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Enhancing Evaluations of Complex Food Security Programs Operating Under Climate Change by Steven Lam A Thesis presented to The University of Guelph In partial fulfilment of requirements for the degree of Doctor of Philosophy in Population Medicine in the field of Public Health Guelph, Ontario, Canada © Steven Lam, April, 2022
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Enhancing Evaluations of Complex Food Security Programs Operating

Under Climate Change

by

Steven Lam

A Thesis

presented to

The University of Guelph

In partial fulfilment of requirements for the degree of

Doctor of Philosophy

in

Population Medicine

in the field of Public Health

Guelph, Ontario, Canada

© Steven Lam, April, 2022

ABSTRACT

ENHANCING EVALUATIONS OF COMPLEX FOOD SECURITY PROGRAMS OPERATING UNDER CLIMATE CHANGE

Steven Lam

University of Guelph, 2022

Advisor(s):

Dr. Warren Dodd

Dr. Sherilee L. Harper

Dr. Kelly Skinner

Dr. Andrew Papadopoulos

Complex, multicomponent programs are increasingly required to address food security

challenges, especially in the context of the climate crisis. While program evaluation has the

potential to improve food security program design, minimal guidance exists on how to evaluate

complex programs. This dissertation research explored strategies for assessing complex food

security programs and opportunities for evaluation to examine climate change, drawing on

several knowledge syntheses and a qualitative study of an ongoing food safety program in

Vietnam called SafePORK. First, a review was conducted to systematically identify and examine

studies reporting on community-based food security monitoring. This review characterized

community-based food security monitoring programs globally and underscored the need to

understand how program evaluation tools can consider climate change. Then, another review

was conducted to systematically explore considerations of climate change within food-related

evaluation reports of United Nations agencies. This review showed that progress toward

mainstreaming climate action in evaluation is slow. Additionally, developing a program theory,

or a pathway showing how changes will occur in a particular context, was identified as a

promising strategy for considering the interactions of program components with climate

change. Next, a third review examined studies reporting on theory-driven food-related

evaluations to characterize how and why evaluations considered climate change. This review

highlighted knowledge gaps of how climate change influenced program outcome pathways or

how programs operated under climate change. Finally, a qualitative study of a food safety

program applying theory-driven evaluation explored the experiences of researchers and

program participants (n=30 interviews). Researchers found the process of developing the

program theory helped them to document and navigate through the adaptive nature of

complex programs. Program participants (slaughterhouse workers and pork retailers) shared

how they were adapting to the impacts of climate change, which was an important factor that

was overlooked within the design of the program. Taken together, this dissertation research

provides insights around how climate change could be better integrated into evaluation

processes.

iii

ACKNOWLEDGEMENTS

To my co-supervisors, Sherilee Harper and Warren Dodd: Sheri, thank you for suggesting I

pursue a PhD and helping to make this journey a reality. Warren, thank you for accepting the

co-supervisory challenge with enthusiasm that remained consistent throughout. I’m grateful for

the time and energy you both provided in pushing my thinking and writing.

To the members of advisory committee, Kelly Skinner and Andrew Papadopoulos: Kelly, I

appreciate the sage evaluation advice you shared at cafes and conferences. Andy, I’m grateful

for our conversations about almost everything. To the both of you, thank you for helping me to

succeed both within and outside of academia by connecting me with paid side projects.

To the Arrell Food Institute, thank you for the opportunity to join the 2017 inaugural cohort of

the Food From Thought research assistantship program. I’m grateful to have met and worked

with a stellar team of students across departments, especially Kathleen Johnson, Michelle

Thompson, and Cameron Fioret. Thank you all for your friendship, in dream life, and in real life!

To the Canadian Association for the Study of International Development, thank you for the

opportunity to participate in the 2017 Doctoral School. Through this experience, I connected

with some amazing peers, including Gloria Novovic, Jeremy John Escobar Torio, and Judyannet

Muchiri. “Thank you SO much” friends for the rants, laughs, and solidarity.

To the Harper labmates, moving to Edmonton in 2018 would not have been as fun without you

Crystal Gong, Jen Jones, Andrea Garcia, Amreen Babujee, Carlee Wright, Jacqui Middleton, and

iv

Kaitlin Patterson. Thank you for the “treat-yo-self Thursdays” and hangouts. Crystal: thanks for

always taking what I said with humour. Jen: your perseverance is contagious, and I might have

caught some of it, so thank you. Andrea: thank you for climbing with me. And thank you to the

wider lab, especially Amy Kipp and Chloe Zivot, for your support on different parts of this work.

To the Dodd labmates, I’m happy to have been in your company when I moved to Waterloo in

2019. Thank you Vinussa Rameshshanker, Chantelle Ramsundar, Emily Kocsis, Josalyn Radcliffe,

Monica Bustos, and Shoshannah Speers for the important conversations around global health.

Thank you especially to Sara Wyngaarden for being such a lovely friend.

To the Ontario Veterinary College, especially everyone at Shared Administrative Services for all

that you do. To my classmate, Aarabhi Rajendiran, thanks for being one of the few people I can

talk to for hours on ends about evaluation and non-evaluation matters. And to Abhinand

Thaivalappil, thanks for consistently having my back, from elementary school to grad school.

To the Canadian Evaluation Society, thank you for your conferences, student awards, and case

competitions, which enriched my PhD experience. Thank you to the evaluators and clients who

worked with me on interesting side projects, providing me with a much-welcomed mental break

from my dissertation alongside professional experience to further my evaluation journey.

To the Indigenous Health and Adaptation to Climate Change team, thank you for your support

during the first couple of years of my PhD. I appreciated the opportunity to work with and learn

from Lea Berrang-Ford, James Ford, and the rest of the team.

v

To the SafePORK team, thank you for your support during the latter half of my PhD. It’s always

wonderful working with you Hung Nguyen-Viet and Fred Unger. Thank you for being so

hospitable and welcoming. To Sinh Dang-Xuan and Trang Le, I’m very grateful for your research

assistance. I’m also happy we stayed connected since the days at the Center for Public Health

and Ecosystem Research. And thank you to the participants of SafePORK for sharing their time,

perspectives, and experiences with us.

Thank you friends for checking-in on me. Special thanks to Chloe Doan for telling me to “dream

bigger, boy.” Troy Stanton, thank you for making me ponder why I want a PhD and other big life

questions. Jennifer Bach, thank you for always being there for me wherever you happen to be in

the world. Huong Nguyen-Mai, thank you chị for always asking me about my Vietnamese and

helping to keep it in shape. Ly Nguyen, thank you for being that kind friend I aspire to be.

To my brothers Kevin and David, thank you for always supporting me with all my life choices. To

my mom, whose sacrifice before and after the war years made possible my life and those of my

brothers. Thank you mẹ for sending me home with food and plants I didn’t realize I needed.

Thank you to the rest of my family in Canada and Vietnam for always welcoming me into your

thoughts and homes. Lastly, thank you Dan, for always managing to make me laugh and keep

me full. Well done, my love.

vi

STATEMENT OF WORK

I wrote research chapters (Chapters 2-5) in collaboration with my advisory committee and other

colleagues. Under the supervision of Drs. Sherilee Harper and Warren Dodd, I wrote Chapter one

(introduction), Chapter six (applied chapter), and Chapter seven (conclusion). The following

scholarships funded my research: the Graduate Student Excellence Entrance Scholarship (2017),

the Ontario Veterinary College PhD Scholarship (2017-2021), the SSHRC General Graduate

Student Funding Travel Scholarship (2018), the CIHR Frederick Banting and Charles Best Canada

Graduate Scholarship (2019-2022), and the Canadian Evaluation Society Educational Fund

Graduate Scholarship (2020).

Chapter two | Community-based monitoring of Indigenous food security in a changing

climate: Global trends and future directions

Published article:

Lam S, Dodd W, Skinner K, Papadopoulos A, Zivot C, Ford J, Garcia P, IHACC Research Team,

Harper SL. (2019). Community-based monitoring of Indigenous food security in a changing

climate: Global trends and future directions. Environmental Research Letters. 14(7): 073002.

I led all stages of the review, including: developing the research question; designing the search

strategy; extracting, analyzing, and interpreting the data; and writing the paper. WD and SLH

supervised and contributed to all stages of the review. KS and AP contributed to

conceptualization and data interpretation. CZ contributed as a secondary reviewer and to the

vii

design of the screening tool. The IHACC team contributed to conceptualization. All co-authors

contributed to manuscript editing. In 2018, I received helpful feedback on this work from the

Ecohealth conference and Ontario Veterinary Colleague Graduate Research Symposium.

Chapter three | How are climate actions evaluated? A review of United Nations food

security evaluations

Published article:

Lam S, Dodd W, Berrang-Ford L, Ford J, Skinner K, Papadopoulos A, Harper SL. (2021). How are

climate actions evaluated? A review of United Nations food security evaluations. Global Food

Security. 28: 100509.

I led all stages of the review including: developing the research question; designing the search

strategy; extracting, analyzing, and interpreting the data; and writing the paper. Amreen Babujee

provided support as a secondary reviewer. WD and SLH supervised and contributed to all stages

of the review. LBF, JF, KS, and AP contributed to conceptualization and data interpretation. All

co-authors contributed to manuscript editing. In 2019, I received helpful feedback on this work

from the Canadian Evaluation Society conference.

Chapter four | How and why are Theory of Change and Realist Evaluation used in food

security contexts? A scoping review

Published article:

viii

Lam S, Dodd W, Wyngaarden S, Skinner K, Papadopoulos A, Harper SL. (2021). How are Theory of

Change and Realist Evaluation used in food security contexts? A scoping review. Evaluation and

Program Planning. 89: 102008.

I led all stages of the review including: developing the research question; designing the search

strategy; extracting, analyzing, and interpreting the data; and writing the paper. WD and SLH

supervised and contributed to all stages of the review. SW contributed as a secondary reviewer

and to the design of the screening tool. KS and AP contributed to conceptualization and data

interpretation. All co-authors contributed to manuscript editing.

Chapter five | Planning and evaluating a complex food safety program operating under a

changing climate: Experiences from Vietnam

Article in preparation for peer-review:

Lam S, Dodd W, Nguyen-Viet H, Unger F, Le TTH, Dang-Xuan S, Skinner K, Papadopoulos A,

Harper SL. “We have a lot of things to do:” On planning and evaluating a complex food safety

program operating under a changing climate.

I co-developed this research project with coordinators of the SafePORK program in Vietnam

(HN-V, FU). I conducted remote interviews with researchers while TL and S-DX conducted

remote interviews with program participants. To ensure data quality, I held de-brief sessions

with TL and S-DX throughout the interview process. Additionally, I conducted data checking (e.g.

ix

explored consistency between transcriptions and recordings). I wrote the manuscript under the

supervision of WD, SLH, HN-V, and FU. All co-authors contributed to manuscript editing.

Chapter six | How the world will measure progress on the Paris climate agreement and

keep countries accountable

Published commentary:

Lam S, Dodd W, Harper SL. (2021). COP26: How the world will measure progress on the Paris

climate agreement and keep countries accountable. The Conversation. Canada.

I wrote this piece to position the importance of evaluation in keeping countries accountable for

their climate action commitments. WD and SLH supported the conceptualization and editing of

the piece. Hannah Hoag, an editor at The Conversation Canada, provided helpful feedback and

edits.

x

TABLE OF CONTENTS

ABSTRACT .......................................................................................................................................................................... ii

ACKNOWLEDGEMENTS ............................................................................................................................................... iii

STATEMENT OF WORK ................................................................................................................................................ vi

TABLE OF CONTENTS .................................................................................................................................................... x

LIST OF TABLES ............................................................................................................................................................. xvi

LIST OF FIGURES .......................................................................................................................................................... xvii

LIST OF ABBREVIATIONS ........................................................................................................................................... xix

LIST OF APPENDICES ................................................................................................................................................... xx

POSITIONALITY STATEMENT .................................................................................................................................. xxii

The research topic ................................................................................................................................................. xxii

The research participants ................................................................................................................................... xxiv

The research context and process ................................................................................................................... xxv

My responsibility ................................................................................................................................................... xxvi

References.............................................................................................................................................................. xxviii

CHAPTER 1: INTRODUCTION .................................................................................................................................... 1

2.1 Introducing the work ................................................................................................................................... 1

2.2 Conceptualizing food security ................................................................................................................. 4

2.3 Measuring food security ............................................................................................................................ 6

2.4 Food security programs .......................................................................................................................... 10

2.5 Program monitoring and evaluation .................................................................................................. 11

xi

2.6 Dissertation objectives ............................................................................................................................. 17

2.7 Why does this dissertation matter today? ....................................................................................... 18

2.8 Methodological framing ......................................................................................................................... 20

2.8.1 Knowledge synthesis ....................................................................................................................... 20

2.8.2 Qualitative research ......................................................................................................................... 22

2.8.3 Combining knowledge synthesis and qualitative research .............................................. 27

2.9 Dissertation structure ............................................................................................................................... 28

2.10 Summary ....................................................................................................................................................... 29

2.11 References .................................................................................................................................................... 31

CHAPTER 2: COMMUNITY-BASED MONITORING OF INDIGENOUS FOOD SECURITY IN A

CHANGING CLIMATE: GLOBAL TRENDS AND FUTURE DIRECTIONS ....................................................... 43

Abstract ............................................................................................................................................................................ 43

2.12 Introduction ................................................................................................................................................. 44

2.13 Methods ........................................................................................................................................................ 48

2.13.1 Search strategy ............................................................................................................................. 48

2.13.2 Citation management ................................................................................................................. 49

2.13.3 Relevance screening and eligibility ....................................................................................... 49

2.13.4 Data extraction and synthesis ................................................................................................. 49

2.14 Results ............................................................................................................................................................ 53

2.14.1 Overview of relevant articles .................................................................................................... 53

2.14.2 Diversity of approaches to community-based monitoring .......................................... 54

2.14.3 Most studies were published in the past decade ............................................................ 55

2.14.4 Wildlife was a prominent type of food monitored.......................................................... 56

xii

2.14.5 More articles focused on men’s participation in monitoring ...................................... 57

2.14.6 Climate change indicators were rarely assessed .............................................................. 57

2.14.7 Varying degrees of Indigenous community engagement in monitoring ............... 59

2.15 Discussion ..................................................................................................................................................... 61

2.16 Conclusion .................................................................................................................................................... 71

2.17 References .................................................................................................................................................... 73

CHAPTER 3: HOW ARE CLIMATE ACTIONS EVALUATED? A REVIEW OF UNITED NATIONS FOOD

SECURITY EVALUATIONS .......................................................................................................................................... 85

Abstract ....................................................................................................................................................................... 85

3.1 Introduction ................................................................................................................................................. 86

3.2 Methods ........................................................................................................................................................ 89

3.2.1 Search strategy .................................................................................................................................. 89

3.2.2 Relevance screening ........................................................................................................................ 90

3.2.3 Data extraction, classification, and analysis ............................................................................ 91

3.2.4 Thematic analysis: examining evaluation challenges and opportunities..................... 96

3.3 Results ............................................................................................................................................................ 97

3.3.1 Climate action mainstreaming into food security evaluation ........................................ 100

3.3.2 Climate considerations in food security evaluation was superficial ............................ 103

3.3.3 High scoring food security evaluations integrated climate considerations into the

evaluation scope, approach, and results ................................................................................................. 104

3.3.4 Low scoring food security evaluations integrated climate considerations into the

evaluation results only ................................................................................................................................... 106

3.3.5 Challenges and opportunities for evaluating climate action ......................................... 107

3.4 Discussion ................................................................................................................................................... 114

xiii

3.4.1 Implications for research and practice ................................................................................... 116

3.4.2 Limitations ......................................................................................................................................... 118

3.5 Conclusion .................................................................................................................................................. 118

3.6 References .................................................................................................................................................. 120

CHAPTER 4: HOW AND WHY ARE THEORY OF CHANGE AND REALIST EVALUATION USED IN

FOOD SECURITY CONTEXTS? A SCOPING REVIEW ...................................................................................... 127

Abstract ..................................................................................................................................................................... 127

4.1 Introduction ............................................................................................................................................... 128

4.2 Methods ...................................................................................................................................................... 130

4.2.1 Search strategy ................................................................................................................................ 130

4.2.2 Relevance screening and eligibility .......................................................................................... 131

4.2.3 Data extraction and synthesis .................................................................................................... 132

4.3 Results .......................................................................................................................................................... 134

4.3.1 Characteristics of studies ............................................................................................................. 134

4.3.2 ToCs and RE were developed primarily using qualitative approaches ...................... 137

4.3.3 ToCs served a variety of purposes whereas RE supported evaluation purposes ... 138

4.3.4 The use of multiple theory-driven evaluation approaches together .......................... 139

4.3.5 Considerations of gender, context, and climate change ................................................. 140

4.3.6 Problem representations offered by studies ........................................................................ 143

4.3.7 Responses to problem framings ............................................................................................... 145

4.4 Discussion ................................................................................................................................................... 149

4.4.1 Strengths and limitations ............................................................................................................ 153

4.5 Conclusion .................................................................................................................................................. 153

xiv

4.5.1 Lessons learned ............................................................................................................................... 154

4.6 References .................................................................................................................................................. 156

CHAPTER 5: “WE HAVE A LOT OF THINGS TO DO:” ON PLANNING AND EVALUATING A

COMPLEX FOOD SAFETY PROGRAM OPERATING UNDER A CHANGING CLIMATE ........................ 163

Abstract ..................................................................................................................................................................... 163

5.1 Introduction ............................................................................................................................................... 164

5.1.1 Complex food safety programs ................................................................................................. 165

5.1.2 Context: Food safety in Vietnam ............................................................................................... 166

5.1.3 The SafePORK program ................................................................................................................ 168

5.1.4 SafePORK locations ........................................................................................................................ 170

5.2 Methods ...................................................................................................................................................... 172

5.2.1 Data collection and analysis ....................................................................................................... 172

5.2.2 Data validity and management ................................................................................................. 173

5.2.3 A note on COVID-19 and ethics ................................................................................................ 173

5.3 Results .......................................................................................................................................................... 174

5.3.1 “We imagine how it can work in practice:” Using program theory to track changes

to the program .................................................................................................................................................. 175

5.3.2 “When it rains, you have to cover the pork:” Attuning to climate change ............... 178

5.3.3 “We always talk about gender in SafePORK:” Attuning to gender equity ................ 182

5.4 Discussion ................................................................................................................................................... 187

5.4.1 Limitations ......................................................................................................................................... 191

5.5 Conclusion .................................................................................................................................................. 192

5.6 References .................................................................................................................................................. 193

xv

CHAPTER 6: HOW THE WORLD WILL MEASURE PROGRESS ON THE PARIS CLIMATE

AGREEMENT AND KEEP COUNTRIES ACCOUNTABLE ................................................................................. 199

6.1 Where are we? .......................................................................................................................................... 200

6.2 How are we doing? ................................................................................................................................. 201

6.3 Collecting and preparing information ............................................................................................. 204

CHAPTER 7: CONCLUSION .................................................................................................................................... 206

7.1 Reflecting on the journey ..................................................................................................................... 206

7.2 Synthesis of findings ............................................................................................................................... 209

7.2.1 Exploring program theory in food security program evaluation.................................. 210

7.2.2 Considering gender and other social identities in evaluation processes .................. 211

7.2.3 Integrating climate change into all stages of an evaluation .......................................... 212

7.3 Strengths and limitations ...................................................................................................................... 214

7.4 Suggestions for future research ......................................................................................................... 216

7.5 Concluding thoughts .............................................................................................................................. 217

7.6 References .................................................................................................................................................. 220

Appendices ................................................................................................................................................................... 224

xvi

LIST OF TABLES

Table 1.1. Food security metrics and their scale, strengths, and weaknesses. ......................................... 8

Table 2.1. Search strategy to identify published articles on Indigenous community-based

monitoring of Indigenous food security. ............................................................................................................ 51

Table 2.2. Inclusion and exclusion criteria to identify published articles on community-based

monitoring of Indigenous food security and climate change..................................................................... 52

Table 2.3. Summary of information extracted from articles on community-based monitoring of

Indigenous food security. ......................................................................................................................................... 53

Table 2.4. Types of community-based monitoring approaches described in articles that reported

the implementation of a monitoring system ..................................................................................................... 61

Table 3.1. Food security and climate change classification system applied to United Nations

evaluation reports. ....................................................................................................................................................... 93

Table 3.2. Assessment rubric for climate action integration into United Nations evaluation

reports. ............................................................................................................................................................................. 96

Table 3.3. Descriptive characteristics of United Nations food security evaluations (n = 136

evaluations) published from 2014 to 2019......................................................................................................... 99

Table 4.1. Criteria to select food-related Theory of Change and Realist Evaluation studies. ........ 132

Table 4.2. Characteristics of food-related Theory of Change and Realist Evaluation studies. ...... 136

xvii

LIST OF FIGURES

Figure 1.1. Visual representation of dissertation research including two chapters on how climate

change is considered in food security monitoring and evaluation. .......................................................... 29

Figure 2.1. Flow chart of the selection of studies that explored community-based monitoring of

Indigenous food security. ......................................................................................................................................... 54

Figure 2.2. Geographic distribution of articles on community-based monitoring of Indigenous

food security. ................................................................................................................................................................. 56

Figure 2.3. Articles on community-based monitoring of Indigenous food security with and

without climate change considerations, over time. ........................................................................................ 58

Figure 3.1. Flow chart illustrating the selection of United Nations food security evaluations (n =

136 unique evaluations within 133 reports) published from 2014 to 2019. .......................................... 98

Figure 3.2. Number of United Nations food security evaluations (n = 136) with a climate focus

published from 2014 to 2019. ............................................................................................................................... 101

Figure 3.3. Proportion of United Nations food security evaluations from 2014 to 2019 focused on

implicit adaptation (a), explicit adaptation (b), mitigation (c), both adaptation and mitigation (d),

and climate change impacts (e). ........................................................................................................................... 102

Figure 3.4. Extent of climate action integration into United Nations food security evaluations

from 2014 to 2019. .................................................................................................................................................... 104

Figure 3.5. Challenges and opportunities for assessing climate action as reported in United

Nations food security evaluations from 2014 to 2019................................................................................. 108

Figure 4.1. Flow chart showing the selection of food-related Theory of Change and Realist

Evaluation studies. ..................................................................................................................................................... 135

Figure 4.2. Food topics of reviewed Theory of Change and Realist Evaluation studies. ................. 137

Figure 4.3. Considerations of context, gender, and climate change in food-related Theory of

Change and Realist Evaluation studies. ............................................................................................................. 142

Figure 4.4. Concept map showing the relationship between problem framings, responses to

problem framings, and conditions under which responses occur in theory-driven evaluations. 146

Figure 5.1. SafePORK program objectives and their interrelationships. ................................................ 170

xviii

Figure 5.2. Map showing locations of study sites (Hung Yen, Nghe An, Hoa Binh provinces) and

the capital city of Vietnam (Hanoi). ..................................................................................................................... 171

Figure 5.3. Timeline of implementation, key milestones, and barriers of SafePORK. ....................... 178

Figure 7.1. Visual representation of key findings from this dissertation. .............................................. 209

xix

LIST OF ABBREVIATIONS

ASF African Swine Fever

CBM Community-Based Monitoring

CFIR Consolidated Framework for Implementation Research

IHACC Indigenous Health Adaptation to Climate Change

FBD Foodborne Disease

LMIC Low- and Middle-Income Country

M&E Monitoring and Evaluation

RE Realist Evaluation

SDG Sustainable Development Goals

ToC Theory of Change

UN United Nations

UNEG United Nations Evaluation Group

xx

LIST OF APPENDICES

Appendix 1: Search strategy to identify published articles on Indigenous community-based

monitoring of Indigenous food security and climate change in AGRICOLA©, PRISMA©,

MEDLINE®, CabDirect©, and the Web of Science™ CORE Collection databases................................. 224

Appendix 2: Complete list of included articles and select article characteristics on Indigenous

community-based monitoring of food security and climate change. ................................................... 228

Appendix 3: Complete list of references. .......................................................................................................... 238

Appendix 4: Questions to guide deductive qualitative analysis conducted on United Nations

food security evaluation reports published from 2014 to 2019. .............................................................. 246

Appendix 5. Codebook of climate-responsive food security evaluation challenges. ...................... 247

Appendix 6. Codebook of climate-responsive food security evaluation solutions........................... 250

Appendix 7: Thematic map of challenges & opportunities for climate-responsive evaluation. .. 253

Appendix 8: List of all included United Nations food security evaluation reports published from

2014 to 2019. ............................................................................................................................................................... 254

Appendix 9: Performance of United Nations food security evaluations published from 2014 to

2019 (n = 136) according to components of the climate assessment rubric. ..................................... 261

Appendix 10: Climate change mandates of United Nations agencies. .................................................. 262

Appendix 11: Comparison between average climate action integration score of United Nations

evaluations and average program duration. ................................................................................................... 263

Appendix 12: Comparison in climate-related reporting between high and low scoring climate

action integration of United Nations evaluations.......................................................................................... 264

Appendix 13: Search strategy used to identify Theory of Change and Realist Evaluation studies

from AGRICOLA©, CabDirect©, Web of Science™ CORE Collection, Medline®, Scopus®, EconLit©,

and Google™. ................................................................................................................................................................ 265

Appendix 14: Summary of the screening tools used in the title and abstract screening stage and

full text screening stage to identify relevant Theory of Change and realist evaluation studies. . 266

xxi

Appendix 15: The data charting form used to extract relevant information from Theory of

Change and Realist Evaluation studies. ............................................................................................................. 268

Appendix 16: List of references of all included studies on food-related Theory of Change and

Realist Evaluation. ...................................................................................................................................................... 272

Appendix 17: Coding process to analyze Theory of Change (ToC) and Realist Evaluation (RE)

studies. ........................................................................................................................................................................... 276

Appendix 18. Number of publications focusing on food-related Theory of Change and Realist

Evaluation studies (note: review cut off 10 March 2020). ........................................................................... 277

Appendix 19: Codebook to identify problems as defined by Theory of Change and Realist

Evaluation studies (2nd level). ................................................................................................................................. 278

Appendix 20: Codebook to identify how Theory of Change and Realist Evaluation studies are

responding to problems (3rd level). ..................................................................................................................... 280

Appendix 21: Interview guide and Consolidated Framework for Implementation Research

constructs used to explore the implementation and evaluation of the SafePORK program. ....... 283

Appendix 22: Audit trail of decisions made and rationales behind them. ........................................... 284

Appendix 23: Impacts of COVID-19 on data collection. .............................................................................. 286

Appendix 24: Presentation material for the SafePORK team. ................................................................... 288

Appendix 25: Characteristics of program participant interviewees. ....................................................... 297

Appendix 26: Codebook to identify overarching themes from SafePORK implementation. ........ 298

xxii

POSITIONALITY STATEMENT

Our social identities affect the way we see and interpret the world around us, and how the world

sees and interprets us, both of which influence the research process (Jacobson & Mustafa, 2019).

As the main research instrument, I have a responsibility to consider how my identities,

experiences, and motivations have shaped this work (Hammarberg et al., 2016; Pitard, 2017).

One way of attuning to positionality is to reflect on three key areas: (1) the research topic, (2) the

research participants, and (3) the research context and process (Holmes, 2020).

The research topic

My interest in program evaluation was shaped by my experiences as an accidental evaluator.

Toward the end of a research internship in Hanoi in 2015, I was asked by colleagues to support

an evaluation of an Ecohealth program. Gaining this experience created possibilities for me to

engage in the evaluation discipline, as I became increasingly involved in evaluations of programs

aiming to improve environmental health, rural development, and food security. To me, one of

the biggest privileges of this discipline is connecting with people who generously share their

thoughts and experiences about how programs can better respond to their needs and priorities.

My dissertation topic came from a place of curiosity developed from working in evaluation and

international development. Working alongside fellow evaluators, I found we would often default

to using traditional approaches to evaluation (e.g. assessing the ability of programs to achieve

their intended outcomes) regardless of the evaluation context. This inclination was influenced by

xxiii

our evaluation training, our comfort in using these tools, and our evaluation client’s suggestions.

I wondered whether these approaches were truly able to support learning, especially in food

security and other development contexts where programs often evolve and intended outcomes

could not be predicted in advance. Moreover, the climate crisis we are experiencing today

increasingly affects programs and measures used to evaluate their impacts. I undertook this PhD

research to better understand and strengthen alternative approaches to evaluation for

supporting complex programs and programs facing external influences such as climate change.

The goal was always pragmatic: to contribute to research on evaluation, and through this,

inform evaluation practice.

When planning an evaluation, I typically look for examples conducted in similar contexts for

inspiration. I especially draw on evaluation reports, which are a useful, timely, and actionable

source of information. Although important for informing decisions, many evaluation reports end

up sitting on shelves gathering dust (Leviton & Melichar, 2016). One way of making evidence

from evaluations more readily available is to consolidate what is learned from evaluations. To

address this research gap, I dedicated time and energy synthesizing data across evaluations to

identify common themes relating to food security program evaluation. The findings provided a

stage for further exploration in subsequent chapters.

Alongside my PhD studies, I work as an independent evaluation consultant. One of the

programs I have been supporting is a food safety program in Vietnam called SafePORK. Before

xxiv

entering my PhD, I had also supported evaluation activities of the previous phase of the

program called PigRISK. Working on these programs contributed to my interest in learning more

about strategies for monitoring and evaluating food security programs in low-resource settings.

Importantly, this connection I had to the SafePORK team provided an opportunity for me to

explore the SafePORK program as a case study in my dissertation.

My social identity as a Canadian-Vietnamese man with historical and cultural connections to

Vietnam also played a role in this research process. My parents were third-wave refugees who

had escaped Vietnam’s oppressive post-war climate in the mid-1980s. I was born and raised in

Canada and nourished by Vietnamese food and stories; if not for these, I might not have

pursued work and studies in Vietnam. The research topic of pork safety also became a personal

interest after I shared what I was working on with my mom. She reflected on the early 1970s

when she and grandma raised pigs on the side of their home as an additional source of income.

Listening to the challenges and opportunities they faced served as a reminder to prioritize

community voices in the findings and recommendations made toward pork safety.

The research participants

Several aspects of my identity gave me access to research participants (i.e. SafePORK researchers

and program participants) likely not afforded to other researchers, including my appearance

(Việt Kiều, Vietnamese overseas), experience living in Vietnam (from 2015 to 2017), and

proficiency with Vietnamese (fluent). I have also built relationships, rapport, and trust with many

xxv

of the same research participants. In these ways, I might be considered an ‘insider’, referring to

an individual who researches with a population they are a member of (Holmes, 2020). This

insider status allowed for more rapid acceptance by research participants. As several SafePORK

researchers told me, I was after all a SafePORK team member, and sharing details with someone

who ‘understands’ was not considered to be an issue. In other ways, I am an outsider, as a

colleague once shared with me “you look Vietnamese”, explaining that because I didn’t grow up

in Vietnam, I am not a real Vietnamese. I viewed this perception of me as beneficial for this

research as it led many participants to elaborate on the context of Vietnam, making often

implicit assumptions explicit. Additionally, the social distance of an outsider may have led some

interviews to be more conversational. At times, SafePORK researchers asked me questions, such

as my plans after the research was finished. Because of my insider-outsider status, and the

power differences between researcher and participant that come with this status, I self-reflected

throughout the dissertation on how to try to produce non-hierarchical research relationships.

Being attentive to these power differences is important for avoiding exploitative research.

The research context and process

My approach to working responsibly on research projects in my dissertation was two-fold. First, I

joined larger community-based research projects to help ensure my research and evaluation

interests aligned with community needs and priorities. For example, the idea of reviewing

community-based monitoring systems for Indigenous food security in Chapter 2 originated by

the IHACC team. I collaborated with my co-supervisors who are part of the Indigenous Health

xxvi

Adaptation to Climate Change (IHACC) team to further develop this idea. For Chapter 5, I

worked closely with the SafePORK coordinators to design a project that meets both dissertation

and SafePORK program learning goals. We decided to explore barriers and facilitators to

multidisciplinary food safety research and practice, drawing on the experiences of SafePORK.

Secondly, I employed strategies to enhance quality and reduce potential bias in the research

process. For example, I co-conducted different aspects of the research process where possible.

For my review-based research chapters, I conducted the search and screening of articles with a

second reviewer. For all research chapters, I conducted analysis and interpretation closely with

my PhD committee. When working within larger research teams, I aimed to deeply listen and

accommodate shifting research priorities. Finally, I strived to continuously reflect on my

positionality with the research topic, participants, and context, which helped me to engage with

the research process in a more meaningful way and undertake ethical research.

My responsibility

Universities have extractive tendencies whereby researchers collect data, analyze findings, and

communicate their results to their fellow academics, without meaningfully engaging with

research participants (Kolinjivadi et al., 2020). Pushing back against these colonial and extractive

models is challenging in academic environments that prioritize efficiency, productivity, and

quantifiable outputs. As a doctoral student, I participated in and benefited from this system by

conducting research and advancing my career. With these positionalities and privileges come

xxvii

responsibilities as a researcher. Firstly, I will continue building mutually beneficial research

collaborations, which could help to ensure the benefits from research are experienced by those

involved (Israel et al., 1998). Secondly, I will continue reflecting on power relations inherent in

the research in order to promote shared control of the research process (Råheim et al., 2016).

Thirdly, I will continue prioritizing community voices in the research process and findings. Doing

so could increase the relevance of the research and improve the usefulness of development

programs and policies for communities (Stein & Mankowski, 2004). Finally, I will use my

privileged position as an evaluator to advocate for evaluation metrics that prioritize research

use, quality, process, and outputs beyond the traditional academic paper (Jessani et al., 2020).

xxviii

References

Darwin Holmes, A. G. (2020). Researcher Positionality - A Consideration of Its Influence and Place

in Qualitative Research - A New Researcher Guide. Shanlax International Journal of

Education. https://doi.org/10.34293/education.v8i4.3232

Hammarberg, K., Kirkman, M., & De Lacey, S. (2016). Qualitative research methods: When to use

them and how to judge them. In Human Reproduction.

https://doi.org/10.1093/humrep/dev334

Israel, B. A., Schulz, A. J., Parker, E. A., & Becker, A. B. (1998). Review of community-based

research: Assessing partnership approaches to improve public health. In Annual Review of

Public Health. https://doi.org/10.1146/annurev.publhealth.19.1.173

Jacobson, D., & Mustafa, N. (2019). Social Identity Map: A Reflexivity Tool for Practicing Explicit

Positionality in Critical Qualitative Research. International Journal of Qualitative Methods.

https://doi.org/10.1177/1609406919870075

Jessani, N. S., Valmeekanathan, A., Babcock, C. M., & Ling, B. (2020). Academic incentives for

enhancing faculty engagement with decision-makers—considerations and

recommendations from one School of Public Health. Humanities and Social Sciences

Communications. https://doi.org/10.1057/s41599-020-00629-1

Kolinjivadi, V., Hecken, G. V., Casolo, J., Abdulla, S., & Blomqvist, R. E. (2020). Towards a Non-

Extractive and Care-Driven Academia. http://www.developmentresearch.eu/?p=801

Leviton, L. C., & Melichar, L. (2016). Balancing stakeholder needs in the evaluation of healthcare

quality improvement. BMJ Quality and Safety. https://doi.org/10.1136/bmjqs-2015-004814

Pitard, J. (2017). A journey to the centre of self: Positioning the researcher in autoethnography.

Forum Qualitative Sozialforschung. https://doi.org/10.17169/fqs-18.3.2764

Råheim, M., Magnussen, L. H., Sekse, R. J. T., Lunde, Å., Jacobsen, T., & Blystad, A. (2016).

Researcher-researched relationship in qualitative research: Shifts in positions and

researcher vulnerability. International Journal of Qualitative Studies on Health and Well-

Being. https://doi.org/10.3402/qhw.v11.30996

Stein, C. H., & Mankowski, E. S. (2004). Asking, witnessing, interpreting, knowing: Conducting

qualitative research in community psychology. In American Journal of Community

Psychology. https://doi.org/10.1023/B:AJCP.0000014316.27091.e8

1

CHAPTER 1: INTRODUCTION

2.1 Introducing the work

As with other social determinants of health, access to food has profound impacts on people’s

health (Tarasuk et al., 2019). Individuals who are food insecure are more likely to experience

nutrient deficiencies and have poorer diets compared to people who are food secure (CFS,

2012). The impacts of food insecurity on health go beyond nutrition and diet; food insecurity is

associated with multiple chronic conditions, a higher risk of depression, and poor self-rated

mental and physical health (Leung et al., 2020). Income, housing, education, and other social

determinants of health may also interact with and exacerbate food insecurity. Climate change

also affects the social determinants of health through its impacts on, among others, access to

adequate food (Ragavan et al., 2020).

While the right to food is a fundamental human right (UN General Assembly, 1948), we live in a

world with worrying food security challenges, particularly in low- and middle-income countries

(Farrell et al., 2018). The most recent estimate showed nearly 10% of the global population were

undernourished (FAO et al., 2021). At the end of 2020, more than 88 million people were

experiencing acute food insecurity, up 20% a year earlier (United Nations, 2021b). Projections

revealed this troublesome trend will continue, with climate change and COVID-19 exacerbating

the situation further and reversing gains made toward food security (Zurayk, 2020; Dodd et al.,

2021; FAO et al., 2021). With nine years left to achieve the 2030 Sustainable Development Goals

2

(SDGs), the world is not on track to “end hunger, achieve food security, and improve nutrition”

(i.e. SDG2) (von Grebmer et al., 2020).

There is no simple explanation for why countries lack food security. Food security can be

disrupted by many factors including environmental degradation, climate change, public policies,

poverty, inequality, conflict, food price volatility, and animal and human diseases (Mbow et al.,

2019; FAO et al., 2021; UN, 2021). The causes of food insecurity are often political, economic,

and social. In the words of the United Nations Secretary-General, “Famine and hunger are no

longer about the lack of food. They are now largely [hu]man-made” (UN, 2021). There is more

than enough food for everyone, but current food systems guarantee inequality in access to

food. If we are to achieve SDG2, we need to understand what works to address food inequality.

Because food security is a result of a wide range of factors, programs tackling food security

challenges are often complex, meaning they have “multiple interacting components” (Moore et

al., 2014, p. 1). The Medical Research Council lists characteristics of complex programs, including,

but not limited to: the number of components involved; the number of groups, settings, or

levels targeted; and, the level of flexibility of the program (Skivington et al., 2021). Programs are

complex not only because of the properties of the program but also the context into which the

program is introduced. Context is the pre-existing conditions, or anything external to the

program, that may affect implementation and outcomes (Thirsk and Clark, 2017). For example,

climate change can be a considered a contextual factor given its influence on all aspects of food

3

security, and by extension, efforts aiming to improve food security (Mbow et al., 2019).

Complexity arises from the interaction of program components with context (Hawe, 2015).

Monitoring and evaluation frameworks play a key role in improving food security programs.

Monitoring refers to the ongoing process of tracking program activities and results whereas

evaluation assesses the extent to which program goals were obtained (UNEG, 2013; Wanzer,

2021). Standard approaches to evaluation – such as the assessment of program outcomes

against pre-determined targets – help assess food security programs that are relatively linear

(e.g. school feeding leads to improved nutrition). However, these approaches become less

effective for supporting complex food security programs, such as those targeting behavioural,

social, and/or policy change. Additionally, the complexity stemming from climate change and

other contextual factors pose further challenges in assessing food security programs.

The “complex” and “complexity” aspects of food security programs have not always been well

acknowledged, described, or considered in program design and evaluation (Hendriks, 2020;

Hendriks, 2015; Jones et al., 2013; Leroy et al., 2015). I argue that if monitoring and evaluation

are to identify and learn from effective food security strategies, we need to account for the

influence of these aspects on implementation and outcomes. In this introduction, I illustrate how

my research sought to expand scholarship on monitoring and evaluation of complex food

security programs. I begin by providing a brief review of how the concept of food security has

evolved. Next, I outline the characteristics of food security programs that make them complex

4

and how such programs can experience complexity. Finally, I provide an overview of the

challenges and opportunities to monitoring and evaluating complex food security programs,

especially under climate change.

2.2 Conceptualizing food security

Originally taken to mean adequate world food supplies of basic foodstuffs, the definition of

food security has been continuously reconceptualized to bring the concept in line with

contemporary issues of human development (Stephenson, 2020; United Nations, 1975). Nearly

two decades ago, Maxwell and Frankenberger (1992) documented 194 different studies on food

security conceptualizations. The definition of food security most widely used today and adopted

by the highest level of global governance on food security (the Committee on World Food

Security) is described as “exist[ing] when all people, at all times, have physical and economic

access to sufficient, safe and nutritious food to meet their dietary needs and food preferences

for an active healthy life” (CFS, 2012, p. 1). From this definition, food security encompasses four

key dimensions: availability (e.g. physical presence of food), access (e.g. economic access to

food), utilization (e.g. nutrition intake), and stability (e.g. assurance of the dimensions over time

in the face of shocks). Increasingly, there is a push toward food and nutrition security,

recognizing both must be addressed for improved health (Mozaffarian et al., 2021).

Critical scholars argued these recent re-articulations of food security draw attention to nothing;

in conceptualizing food security as an outcome, the underlying power relations that have

5

created food security conditions remain out of sight (Shepherd, 2012; Stephenson, 2020; Turner

et al., 2018). Attuning to shifting food security definitions is important because definitions can

influence decisions regarding policy responses. Because food security is a prerequisite for the

right to food, applying rights-based approaches – e.g. focusing on root causes such as matters

of state policy and discrimination – is a promising strategy for addressing often neglected power

relations (Ayala & Meier, 2017). Of note, terms such as ‘deserve’ and ‘fairness’ might be more

effective than ‘rights’ in engaging specific audiences in addressing the root causes of food

insecurity (Godrich et al., 2021).

The shift in the terminology used to talk about food security also reflects a growing

understanding of its multidimensional nature. For example, food security is increasingly linked to

climate change. In its Special Report on Climate Change and Land, the Intergovernmental Panel

on Climate Change indicated climate change has complex interactions with food systems,

leading to food insecurity through impacts on food availability, access, utilization, and stability

(Mbow et al., 2019). The definition of food security has also been expanded to include the fifth

dimension, ‘cultural acceptability’, which acknowledges how food production and consumption

are also strongly influenced by culture (Friedrichsen et al., 2018; Mbow et al., 2019; Power, 2008).

Despite these new understandings, many analyses of ‘food security’ still narrowly focus on

raising the food supply; adaptation to climate change, changing consumption practices, and

cultural acceptability have been treated as challenges that sit alongside the primary goal of

achieving food security as if they were an afterthought (IPES-Food, 2015).

6

2.3 Measuring food security

The changing understandings of food security definitions pose challenges in measuring food

security, which is important for understanding the true scale of food security. Measurements

may focus on food availability, access, utilization, stability, or some combination of these

dimensions (Jones et al., 2013). Data collection may take into account quantitative, qualitative,

psychological, and/or social constructs of the experience of food security (Hendriks, 2015).

Importantly, a single measure that captures all aspects encapsulated in the food security

concept does not exist; each measure both captures and neglects phenomena intrinsic to the

concept of food security (Barrett, 2010). However, there have been efforts to develop a single

measure (e.g. Urke et al., 2014). Furthermore, decisions made around what to measure are not

only technical but also political considering measurement determines the subsequent actions

that flow from findings (Haysom & Tawodzera, 2018).

There is no agreed approach to measuring food security. A 2013 review identified 18 different

food security assessment approaches for the different framings of food security (Jones et al.,

2013). Approaches to measuring food security can be broadly categorized as either direct or

indirect, both of which have their strengths and weaknesses (see Table 1.1). Direct measures are

experience-based and attempt to directly measure families’ lived experiences of food security

(Jones et al., 2013). Indirect measures focus on the specific indicator and use the data generated

as a proxy to determine food security status. Care needs to be taken in the selection of

measurement approaches to avoid measuring an unintended construct of food security,

7

measuring multiple constructs without the ability to differentiate them, and collecting

information irrelevant to those using the data (Haysom & Tawodzera, 2018; Jones et al., 2013).

There is general confusion regarding the scale of food security these measurement approaches

are meant to reflect. Food security can be measured at different levels, including individual,

household, community, national, and global. For example, the Food Insecurity Experience Scale

directly measures individuals’ or households’ experiences through the lens of food access (Leroy

et al., 2015). The Global Food Security Index is country-centered and considers food security

according to the national capacity to promote food affordability, availability, and quality/safety

(Allee et al., 2021). Measurement tools are not static and can adapt over time. For instance, the

2020 edition of the Global Food Security Index incorporated the “Natural Resources and

Resilience” category into the main index, which assesses a country’s exposure to the impacts of

a changing climate (Economist Impact, 2021). Measurements can also be aggregated to

determine food security at a higher level. For instance, household expenditure measures can be

taken at the household level and aggregated to determine food security at the national level

(Russell et al., 2018). Importantly, care needs to be taken when extrapolating food security

estimates to arrive at higher data projections to avoid masking community-level differences.

Maintaining disaggregated data (e.g. demographics) is essential for understanding food security

trends and tailoring food security efforts to local contexts (Morales et al., 2020).

8

Table 2.1. Food security metrics and their scale, strengths, and weaknesses (adapted from Jones

et al., 2013; Leroy et al., 2015; Haysom and Tawodzera, 2018; Hendriks, 2020; Allee et al., 2021).

Approaches Description Scale Strengths Weaknesses

Direct

Food Insecurity

Experience Scales

including HFIAS,

MAHFP, and HFSSM

- Scale contains items

representing the

multidimensional

nature of food

insecurity

- Algorithm to convert

scale scores into food

insecurity categories

- Determines anxiety

levels, food

preferences, economic

access, food quantity

- Individual

- Household

- Measures food

security

according to

individual

experiences

- Captures the

psychosocial

dimensions of

food security

along with

physical

experiences

- Valid across

varied socio-

cultural settings

- Difficult to

establish cut-off

points for

classifying

households into

different levels of

food security

- Does not

capture food

safety dimension

- Different

frequency

response options

needed in

different settings

Indirect

Anthropometry - Focuses on weight,

height, body size, and

skinfold

measurements

- Determines

nutritional status

Individual

- Standardized

measurements

of weight and

height are

reproducible

across

individuals

- Evidence-

based cut-off

points

- Requires time

to collect

measurements

- Measures food

security indirectly

(e.g. uses

anthropometry

as a proxy for

food utilization

Whole Measures for

Community Food

Systems

Measures the

multitude of

interconnected

indicators that define

a healthy, whole

community (e.g.

access to healthy and

affordable food,

strong community

ties, thriving local

economies)

Community - Informs

dialogue about

and

measurements

toward

common values

- Helps to share

the stories of

complex

community

food projects

- Requires time

to learn and

implement the

tool

- Rubric model

may be

cumbersome in

scope

Global Food Security

Index

Index of 34 indicators

within three domains

National (can

inform global)

Provides cross-

national

Measures food

security indirectly

9

of food security: 1)

affordability; 2)

availability; and 3)

quality and safety

comparisons of

food security

status,

determinants,

and outcomes

(e.g. through

measuring the

conditions for

food security

rather than

actual food

security level)

Household

Expenditure Surveys

- Focuses on the

household

expenditure of food

and other necessities

- Determines caloric

intake per capita per

household and

economic access to

food

Household

(can inform

national)

- Dietary quality

and income

data can help

understand

food security

dimensions

- Less costly

and time-

consuming

alternative to

other measures

- Measures

available amount

- Conversion of

available food to

caloric intakes

involves major

assumptions that

can cause

measurement

errors

Coping Strategy Index - Questions how

households are

responding to food

shortages

- Determines how

households are

responding and/or

adapting to the

presence or threat of

food shortages

Household

(can inform

national)

- Uses simple

questions that

are easy to

understand and

implement

- Captures

directly the

notion of

adequacy and

vulnerability

Can be

misleading; both

richer and poorer

households may

report smaller

portions, but it

does not imply

an equal increase

in food insecurity

Dietary Intake

Assessments

including

DDS, FVS, FFS

- Focuses on different

items consumed in a

specific period

- Determines the sum

of the different foods

consumed by

individual/household

over a specific period

and quality of food

- Individual

- Household

- Addresses

both dietary

quality & caloric

intakes at an

individual level

- Possible to

understand

intra-household

food security

levels

- Rely heavily on

respondent’s

memory which

can lead to

measurement

error

- Requires

experienced

researchers to do

interviews

HFIAS, Household Food Insecurity Access Scale Indicator; MAHFP, Months of Adequate Household Food

Provisioning; HFSSM, Household Food Security Survey Module; DDS, Dietary Diversity Scores; FVS, Food

Variety Scores; FFS, Food Frequency Scores.

10

2.4 Food security programs

As with food security measures, programs working toward food security can also vary in scale.

Strategies can begin on an individual level. Using food safety as an example, educational

opportunities could support community members learn more about hygienic practices for safe

food handling. At an institutional level, food safety policy, regulation, and surveillance could

enhance both nutritional quality and the safety of food more widely. Additionally, food security

programs are diverse and vary from being complicated to complex, influenced by the specific

food security phenomenon, program, and/or systems in which the program is placed (Hawe,

2015). Lunch programs providing youth nutritious food could be considered a straightforward

way of encouraging good nutritional intake. More complex is agricultural training programs

promoting behavioural change to encourage expanded agricultural production, especially when

climate-resilient practices are not considered in the program design.

Many food security programs encompass attributes of complex programs (Skivington et al.,

2021). Because food security is a multi-dimensional phenomenon, food security programs often

have an extensive array of activities, from behavioural change to policy change, both of which

are interdependent. Furthermore, many different disciplines, sectors, and actors engage in food

security research and/or practice, resulting in different perspectives on how food security should

be achieved (Hendriks, 2015). These different perspectives often contribute to the design of

food security programs with strategies that change over time, making it difficult to attribute

changes in food security to a specific strategy (Foran et al., 2014). Complex food security

11

programs require flexibility in adapting food security strategies to new learning during

implementation (e.g. feedback from participants) and changes to context (e.g. climate impacts

and the need to adapt) (Hendriks, 2020).

Food security programs often experience complexity because food security is a part of broader

food systems, which encompass all activities and actors in the production, transport, processing,

package, storage, retail, consumption, loss, and waste of food (Mbow et al., 2019). Food systems

(and therefore food security programs) must respond to a host of external factors, especially

climate change. Climate irregularity is a key driving force behind rises in global food insecurity

(von Grebmer et al., 2020). Changes in extreme weather events (Devereux, 2007; Gbegbelegbe et

al., 2014) and temperature and rainfall variability (Myers et al., 2017; Niles & Brown, 2017)

threaten food security by decreasing global food production and increasing the risk of hunger

and undernutrition (Lake et al., 2012; Schmidhuber & Tubiello, 2007). Climate change introduces

unpredictability during food security program implementation, making it challenging to

anticipate food security outcomes in advance. Food security programs increasingly need to

invest in climate adaptation measures to decrease the risks on programming (Conevska et al.,

2018).

2.5 Program monitoring and evaluation

Monitoring and evaluation provide important information about the progress and performance

of food security programs (Uitto et al., 2016; FAO et al., 2018; Lam et al., 2019). Monitoring has

12

several meanings in a food security context. It may refer to the routine collection of information

about program processes to understand the progress being made toward food security targets,

informing program implementation and/or evaluation (UNEG, 2013). Monitoring can also be

part of a food security program itself when used to track and respond to changes in food

security situations (WFP, 2012). Evaluation also has multiple purposes, from rendering a value

judgment to generating learning for program improvement (Wanzer, 2021). The current

understandings of evaluation are not so different from Scriven’s (1991) definition of evaluation

20 years ago when evaluation was described as: “a systematic process to determine merit, worth,

or value of something, or the product of that process” (p. 139). Evaluation, as a way of analyzing

programs, for the most part still reflects its historical underpinnings; it is rooted in a particular

moment in time informed by the values, experience, and needs of a small group of white men

(Dean-Coffey, 2018).

While monitoring to track progress toward program goals is a more-or-less standard across

food security programs, there is no one ‘best’ approach to evaluating food security programs

(Hendriks, 2020; Levinson & Herforth, 2013). The appropriate approach is dependent on the

evaluation questions, intended uses, and attributes of the intervention and evaluation (Befani,

2020). In food security contexts, approaches to evaluation typically draw on positivist

approaches, regardless of the food security topic, study site, and target population. For example,

a systematic review of evaluations of interventions tackling children’s food security in low- and

middle-income countries (LMICs) identified 42 studies, most of which used a quantitative design

13

(88%, n = 37) (Holley & Mason, 2019). Several reviews of food security program evaluations

exclusively selected quantitative studies for review, including those on food safety education in

high-income countries (Young et al., 2015), smallholder livestock interventions in LMICs (Lindahl

et al., 2020), and agriculture for nutrition interventions globally (Bird et al., 2019).

Program evaluations privilege quantitative approaches because food security is often measured

quantitatively, and agricultural experiments tend to draw on experimental designs. While serving

an important role in identifying causal relationships, quantitative approaches that do not

provide an understanding of a program’s context are not very effective in capturing insights into

how and why food security programs work (Hendriks, 2020). Furthermore, the conventional

assessment of program performance against desired outcomes (e.g. results-based management)

is often not effective for complex food security programs where program activities and intended

outcomes can shift due to climate impacts and other contextual factors (Kidoido and Child,

2014; Bilali et al., 2019). Although important, there is a gap in the use of mixed-methods,

qualitative, context-sensitive, and theory-based designs in food security program evaluation

(Bird et al., 2019; Holley & Mason, 2019; Young et al., 2015).

There have been increasing developments of alternative approaches to monitoring complex

food security programs. In the context of agricultural innovation system interventions,

suggested monitoring approaches included outcome mapping, rapid appraisal of agricultural

knowledge systems, most significant change, and participatory impact pathway analysis (Faure

14

et al., 2020; The World Bank, 2012). These monitoring practices recognize the nonlinearity of

agricultural and other development interventions, accepting that outcomes emerge following

ongoing iterations of program implementation. There are also developments in monitoring

programs that track changes to food security status. For example, community-based monitoring

is increasingly considered a promising strategy whereby groups collaborate to track and

respond to local food security issues (Berner et al., 2016; Danielsen et al., 2014; Johnson et al.,

n.d.). If challenges with data ownership, funding, and protection of local monitors are addressed,

community-based monitoring offers an improved understanding of long-term food security

trends, skills development for local monitors, and provision of timely information for local

decision-making.

The need to uncover learnings from complex food security programs has also led to the

development of alternative approaches to evaluation. For example, one promising way of

enhancing the usefulness of program evaluations is to ensure they are based on a clear program

theory, often represented by a Theory of Change (McDermott et al., 2015; Rajala et al., 2021).

Theory of Change aims to move evaluation beyond an input-output notion of evaluation, and

instead, requires program designers to explicitly state how, why, and in what context impact will

be achieved (Douthwaite et al., 2017; Maru et al., 2018). Theories of Change are often visualized

as change pathways with linkages between program activities and outcomes as well as

assumptions underpinning these linkages. For example, in the context of a disaster risk

reduction intervention in Niger, the Theory of Change identified climate action as a key activity

15

influencing outcome pathways (Béné et al., 2020). Tracking the outcomes along the change

pathway – either qualitatively or quantitatively – can help program designers understand the

progress being made toward often elusive food security goals (McDermott et al., 2015).

It is generally assumed – but increasingly debated and largely untested – that qualitative,

contextually responsive, and theory-driven approaches to evaluation can effectively support

complex food security programs in the future (Belcher et al., 2017; Y. Maru et al., 2018).

However, this assumption has been accompanied by comparatively little effort to reflect on their

use in and applicability to food security contexts. Understanding context is important for

understanding how programs work, why they sometimes fail, and how they can be adapted

from one context to another (Craig et al., 2018). Theories of Change are immensely popular, but

also increasingly critiqued for not only neglecting context but also being under-developed

(Armitage et al., 2019; Belcher et al., 2017; Moore & Evans, 2017). If alternative approaches to

evaluation are to contribute to the design, implementation, and evaluation of complex

programs, it is important to clarify the context under which they are helpful. Knowing what

works and when can help evaluators anticipate challenges and select evaluation approaches

likely to generate learnings for food security research and practice.

Evaluators are increasingly recognizing the threat climate change poses to food security and

other development efforts, and in response, communities of practice have been formed to foster

evaluative thinking around climate (e.g. Earth-Eval) and food security (e.g. EvalForward) (Rowe,

16

2019; Ssekamatte, 2018; Uitto 2019). However, there is a gap in conceptualizing the intersection

of climate change and food security in evaluation, particularly around how programs affect (and

are affected by) climate change. Standard food security monitoring and evaluation are typically

not designed to track the response of food programs to climate change (Hendriks, 2020; Tendall

et al., 2015). Importantly, there is a need for insights into how food security monitoring and

evaluation can account for complexity introduced by climate change.

There is also growing calls for food systems transformations that support healthy diets in

sustainable, resilient, just, and equitable ways, with concurrent calls for rigorous monitoring and

evaluation (Fanzo et al., 2021; UN, 2021). A promising approach to help think about the

connections between food systems and climate change within evaluation is Blue Marble

evaluation (Vidueira, 2019). Originally applied in food systems transformation contexts, Blue

Marble evaluation is a principles-based approach to evaluating global systems change initiatives

(Richardson & Patton, 2021). This approach to evaluation encourages evaluators to both “zoom

out” for a big picture perspective and “zoom in” to incorporate context when developing and

evaluating transformation pathways. Additionally, Blue Marble evaluation encourages evaluators

to examine connections across scales, siloes, disciplines, and issues. While influencing systems

change is likely beyond the scope of many programs working toward food security, considering

how programs impact and are impacted by global challenges like climate change is critical for

ensuring climate-responsive programming. Of note, this dissertation does not focus on specific

approaches to evaluation a priori but explores those that emerge during this research process.

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2.6 Dissertation objectives

Conventional approaches to evaluation often rest on the assumption that programs are

delivered as originally intended (Hendriks, 2020; McDermott et al., 2015; Steele Gray & Shaw,

2019). Yet, complex food security programs have strategies and outcomes that continually adapt

in response to learnings during implementation (Ansah et al., 2019; Breeman et al., 2015).

Additionally, food security programs are affected by complexity introduced by climate change

and other contextual factors, which are not well accounted for in conventional monitoring and

evaluation practices (Ebi & Del Barrio, 2017). Frameworks exist to help guide the development of

complex health programs (Moore et al., 2014; O’Cathain et al., 2019; Skivington et al., 2021) and

account for their context (Craig et al., 2018; Paparini et al., 2021). However, experience is still

quite limited and there is minimal information on how such frameworks might support food

security efforts specifically. To address this gap, my research objectives are to:

1) Characterize how food security is monitored under a changing climate;

2) Assess how evaluations of food security programs are considering climate change;

3) Characterize the use of theory-driven evaluation in food security contexts; and,

4) Capture lessons learned from designing and evaluating complex food safety programs.

Ultimately, this research aims to inform the development and evaluation of complex food

security programs. Additionally, this research aims to improve understandings of how

evaluations of food security programs might respond to climate change, which matters

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profoundly within the current context of climate change, rising food security challenges, and

inequitable health outcomes.

2.7 Why does this dissertation matter today?

The Secretary-General of the United Nations convened a Food Systems Summit as a way of

setting the stage for global food systems transformation toward achieving the 2030 Sustainable

Development Goals (UN, 2021). The Summit acknowledged the need to understand how to

effectively monitor and evaluate food systems transformation to ensure transformation efforts

are creating positive change. A key dialogue event focused on convening the private sector,

government agencies, and other food security practitioners to discuss challenges and evidence

gaps in food security monitoring and evaluation (ICRISAT, 2021). For example, a key gap

discussed is the need for monitoring food security outcomes on a real-time basis. As such, this

dissertation is timely in addressing research gaps in food security monitoring and evaluation.

This research also informs strategies for evaluating climate action. To achieve any goal, targets

must be set and progress measured; when it comes to climate goals at the global level, that

assessment is called the “global stocktake.” The stocktake is outlined under Article 14 of the

Paris Agreement and is negotiated through United Nations climate change conferences. The

stocktake, which will occur every five years beginning in 2023, takes a look at the collective

progress the world’s nations have made on climate action (Tompkins et al., 2018). Governments

are still deciding how to collectively evaluate their climate action (Chin & Elliot, 2021). This

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dissertation provides insights into how climate action might be tracked, drawing on lessons

learned from evaluations of food security programs. In doing so, evaluation can better support

efforts to limit warming to 1.5 degrees C.

Additionally, the most recent United Nations climate change conference (COP26) resulted in an

outcome document, known as the Glasgow Climate Pact, which calls on 197 countries to report

their progress toward more ambitious climate commitments; however, this document falls short

in naming specific accountability and reporting mechanisms (United Nations, 2021a). Post-

COP26, dialogue has been held among development evaluators to explore how evaluative

evidence can help deliver the Paris agreement, with a focus on agriculture and food security

contexts (EvalForward, 2021). This dissertation contributes strategies for collecting evaluative

evidence around climate action.

Food systems transformations are needed for more inclusive and sustainable food systems.

Importantly, because food systems impact (and are impacted by) climate change, food systems

transformation and climate action need to go together. As programs increasingly incorporate

climate action measures, programs will turn to evaluation to assess the coupled climate action

and food security outcomes alongside the dynamic interaction between climate change and

complex food security programming. International trends in monitoring and evaluation of food

system efforts showed climate change as high on the agenda (Kusters et al., 2019), highlighting

the urgency of understanding how to account for climate change in monitoring and evaluation.

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2.8 Methodological framing

2.8.1 Knowledge synthesis

The Canadian Institutes of Health Research defines knowledge synthesis as “the

contextualization and integration of research findings of individual research studies within the

larger body of knowledge on the topic” (CIHR, 2010, p. 1). Knowledge syntheses can be used to

summarize what is known about a topic, understand inconsistencies across studies, and define

research agendas (Green et al., 2011; Kastner et al., 2012; Lockwood et al., 2019). In contrast to

traditional literature reviews that do not use structured methods to identify studies, knowledge

syntheses apply clearly defined and reproducible methods. Knowledge synthesis is characterized

by three core attributes: it is systematic, comprehensive, and transparent (Greyson et al., 2019).

These attributes are important for reducing bias and enhancing reproducibility during synthesis

steps. There are many types of knowledge syntheses including realist reviews, narrative reviews,

systematic reviews, and scoping reviews (Tricco et al., 2016).

Unlike systematic reviews, which explore questions from quality-appraised studies, scoping

reviews aim to provide an overview or map of the evidence (Colquhoun et al., 2014). Scoping

reviews are among the most common knowledge synthesis approach used in public health,

particularly for answering questions related to the effectiveness of public health interventions

(Lockwood et al., 2019). Scoping reviews are particularly useful when a topic has not yet been

extensively reviewed by bringing together often large and disparate bodies of knowledge

together into a more concise and manageable format (Munn et al., 2018). Often scoping reviews

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are undertaken to examine the extent, range, and nature of research in a topic area (Arksey &

O’Malley, 2005; Pham et al., 2014).

2.8.1.1 Knowledge synthesis methods

Researchers and evaluators working in food security contexts need access to reliable information

to help inform program decisions (Hendriks, 2020). Because many evaluation reports tend to ‘sit

on the shelf’, scoping reviews can be useful for consolidating what is being learned from

evaluations and making that evidence more readily available (Chandna et al., 2019). Synthesizing

and translating knowledge into food security action (and ways to measure action) matters

greatly, especially in the present context of COVID-19, climate change, and growing rates of

food insecurity (Johnsen et al., 2020). As such, many research chapters in this dissertation (e.g.

Ch. 2-4) draw on scoping reviews to characterize literature in this area. Scoping the literature

identifies ideas where future research may be required but does not evaluate the quality of the

literature (Colquhoun et al., 2014). This distinction is important; these chapters intend to

understand what has been reported in the literature rather than make quality assessments.

Additionally, this dissertation integrates qualitative thematic analysis into scoping reviews to

understand the context behind the reviewed studies as well as strengthen qualitative analysis

skills before working with research participants (Hamel et al., 2021). For example, in Chapter 4, I

used thematic analysis to capture key recurrent messages or ‘themes’ from the reviewed

research and evaluation studies. I selected thematic analysis to move beyond the surface or

obvious content of the data to identify implicit patterns of meaning (Braun et al., 2018). Many of

22

the patterns identified were then explored further in subsequent. Reviewing, assessing, and

synthesizing the literature is a crucial early step before primary data collection, as Clarke argues:

“Those doing qualitative research cannot opt-out of knowing their relevant scholarly

conversations” (Clark, 2016, p. 1).

2.8.2 Qualitative research

Qualitative research is often used in evaluations of complex programs to increase knowledge of

program assumptions, components, and mechanisms (Pawson and Tilley, 1997; Thirsk and Clark,

2017; Rørtveit et al., 2020). Given my research objective of exploring how food security programs

operating under complexity can be supported by evaluation, I chose a qualitative design for the

final research chapter (Ch. 5). This qualitative study focuses on the experiences of researchers

and evaluators involved in food security programs and the broader socio-political contexts that

shape these experiences. Qualitative designs are suitable and often preferred, for research

focused on understanding how people navigate and make decisions in their food environments

(Centre for Food Policy, 2021; Hendriks, 2020). These realities can shed light on the context in

which complex food security programs operate, thus informing the design of evaluations.

Several philosophical assumptions underpinning qualitative research inform the research

process in Chapter 5. For example, ontologically, there are multiple truths and different realities

(Busetto et al., 2020; Guba & Lincoln, 1994; Tomaszewski et al., 2020). Embracing this

assumption, I sought to capture the diverse perspectives of participants, which may conflict but

which, taken together, contribute to a rich understanding of complexities (Creswell, 2014).

23

Qualitative research also assumes the position of the researcher – as the primary research

instrument – impacts all aspects of the research (Jaye, 2002). In my positionality statement, I

discuss how my identities and experiences are entwined in the research (Day, 2012).

Epistemologically, qualitative research takes the stance that knowing is context-dependent, co-

created, and situated (Englander, 2019). I aimed to give a detailed description of the context of

the study and how knowledge reflects a particular point in time (Craig et al., 2018).

To examine complex food security programs operating under complexity for lessons into

program evaluation, I drew on experiences from a food security program called “Market-based

approaches to improving the safety of pork in Vietnam” (SafePORK). SafePORK is a five-year

program (2017-2022) aiming to reduce the burden of foodborne disease in informal, emerging,

and niche markets through designing, piloting, and evaluating food safety interventions.

SafePORK builds on a previous five-year program called PigRISK (2012-2017). Because SafePORK

is a complex, multi-component program conducted by a multidisciplinary team with previous

experience implementing food safety programs (Lam et al., 2016), it provides a realistic example

of how complex food security programs are developed and evaluated. SafePORK

implementation has also been affected by external factors (e.g. African Swine Fever, COVID-19,

climate change), providing opportunities to explore how the program is responding to

complexity.

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2.8.2.1 Qualitative research methods

To achieve the research objective of capturing lessons learned from designing and evaluating

complex food safety programs, I employed three data collection methods: 1) document reviews;

2) semi-structured interviews; and, 3) reflective memos. I also used these multiple lines of inquiry

to triangulate findings and strengthen the internal validity of the study (Carter et al., 2014;

Creswell, 2014).

Understanding the implementation of food safety programs in Vietnam requires an

understanding of Vietnamese food policies. The primary policy document reviewed was the

2010 Food Safety Law (No 55/2010/QH12), which provides for rights and obligations for

organizations and individuals in assuring safe food (The National Assembly, 2010). I also

reviewed key program documents of SafePORK and PigRISK, including meeting notes,

evaluation reports, annual reports, research briefs, policy briefs, and manuscripts. Finally, I

explored the published and grey literature to better understand the food safety context and

other programs contributing to food security outcomes in Vietnam.

The main data sources were semi-structured interviews with researchers and community

members. The interview questions focused on intervention characteristics, outer setting, inner

setting, characteristics of individuals, and implementation process. The interviews were

conducted remotely between August and September 2021. Qualitative health researchers have

long used online methods to conduct qualitative research (Varma et al., 2021). Douedari et al.

(2021) offer several criteria for reflecting on the appropriateness of remote methods, such as

25

research objectives, target participants, and data collection budget and timeframe. The

evaluation-focused research objective addressed in this study could be considered low-risk.

Additionally, I have worked with SafePORK for evaluation-related activities of SafePORK (both

in-person and remotely) and have visited SafePORK study sites. My research topic and

connections made the use of remote methods likely appropriate in this context.

For SafePORK researchers, I conducted interviews in English via Microsoft Teams. For program

participants, interviews were conducted in Vietnamese via phone calls by two SafePORK team

members. These two team members (one man, one woman) were young, early career

researchers working with the International Livestock Research Institute. They divided up the

participant interviewee list among themselves based on familiarity with interviewees to increase

the likelihood of good conversations. Existing trust was viewed by the team as important,

especially during remote data collection where face-to-face interaction was not possible.

Program participants who completed an interview received 50.000 Vietnamese đồng

(approximately US$2.20) as compensation for their time. Program participants were selected by

team members based on participation in SafePORK to ensure a diversity of experiences and

perspectives. Interviews were audio-recorded with verbal informed consent and ranged from 60-

120 mins (with researchers) and 15-20 mins (with participants).

I wrote reflective memos throughout the entire qualitative data collection process as a means of

documenting contextual information and reflecting on the data collection process (Mulhall,

26

2003; Phillippi & Lauderdale, 2018). I wrote down important insights gained from the document

review. I also documented reflections from the interviews, including initial impressions,

surprising revelations, emerging themes, and potential next steps in my study. Additionally, I

recorded similar reflections from de-brief sessions with team members, program coordinators,

and my PhD advisors. Finally, I kept an audit trail of key decisions made (e.g. revisions to the

interview guide) to enhance the trustworthiness of the qualitative inquiry (Carcary, 2009).

I identified patterns in the data using a deductive approach to thematic analysis (Braun et al.,

2018). I paid specific attention to several elements. First, I considered how context was reported

as per guidelines for process evaluations of complex programs (Moore et al., 2014). Secondly, I

explored explicit or implicit mentions of climate change given its growing impact on food

security and other development programs. Finally, I considered how differences and similarities

in the social identities of researchers and program participants (e.g. population, age, gender)

shaped experiences with SafePORK. This approach enabled us to explore how SafePORK is

responding to the needs and priorities of different groups of people. Coding and analyses were

performed using NVivo© software (QSR International, Burlington, MA, USA).

2.8.2.2 Data validity and informed consent

This research was conducted in collaboration with the coordinators of SafePORK who provided

regular guidance and feedback on this work and are co-authors on the manuscript. I shared

preliminary findings with the program coordinators to inform ongoing implementation,

evaluation, and reporting needs. All interviewees verbally provided their informed consent to

27

participate before the interview. This work received research ethics approval from the University

of Guelph (20-02-003) and Hanoi University of Public Health (018-110/DD-YTCC).

2.8.2.3 A note on language

Interviews conducted in Vietnamese were transcribed by the two SafePORK team members. I

translated Vietnamese transcripts into English before coding. For key quotations used in the

findings, I went back to the original transcripts to capture the nuances of Vietnamese (van Nes

et al., 2010).

2.8.3 Combining knowledge synthesis and qualitative research

Scoping reviews have received criticisms for their positivistic leaning and commitment to

procedural objectivity (Dalmer, 2020). Generally speaking, qualitative researchers reject this

notion of objectivity (Guba & Lincoln, 1994). Another criticism of systematic reviewing is that it

can encourage the superficial reading of the material found, with reviewers simply scanning and

extracting the relevant information (Hammersley, 2020). By contrast, qualitative researchers

emphasize the need for careful reading (Day, 2012). Mindful of these criticisms, it is important to

note that my purpose in reviewing studies is to learn from and contribute to evaluation practice

broadly. Because evaluating complex programs requires a wide range of evaluative evidence

(Paparini et al., 2021), I drew on a range of studies rather than a limited set of studies (e.g.

quantitative studies only). Additionally, I engaged in close reading of studies to understand the

context in which evaluations have been used. These close readings shaped the direction of my

qualitative in-depth study exploring food security programs in their real-life settings, enabling a

28

deeper understanding of how and why programming decisions are made. The use of knowledge

syntheses and qualitative research methodologies contributes to the limited research on

evaluation exploring evaluation approaches in food security contexts (Hendriks, 2020).

2.9 Dissertation structure

I wrote my dissertation in a manuscript-based style to help ensure my work reached researchers

and evaluation practitioners much more quickly than what was possible with a book-style

dissertation. Chapters 2 to 5 represent stand-alone research-based chapters that have been

published or are ready to submit for peer review. Chapter 6 represents a practice-based chapter,

common in the public health discipline, which is designed to be more accessible and facilitate

the use of research findings. This chapter was published in The Conversation Canada. For

chapters already published, the reference style of the journal was used.

Underscoring each chapter is an inquiry and/or description of how monitoring and evaluation in

food security contexts might be conducted effectively during a changing climate. And because

climate change impacts on food security will not be equitable, these chapters pay attention

toward for whom food security programs work. In the early chapters, I learn from other

researchers and evaluators who have shared their practical experiences; specifically, I draw on

knowledge synthesis approaches and principles to explore how climate change is addressed in

food security monitoring (Chapter 2) and evaluation (Chapter 3). Engagement with this literature

was the impetus for knowledge synthesis and qualitative analysis of how alternative approaches

29

to evaluation (especially theory-driven evaluation) were used in food security contexts (Chapter

4). Building on emergent themes from previous chapters, the final research chapter (Chapter 5)

explores the experiences of researchers and participants involved in a food security program in

Vietnam (SafePORK) and examines the role of theory-driven evaluation in supporting this

program. For the practice-based chapter, Chapter 6, I reflect on how global progress on climate

action could be measured, drawing on food security as a case study (Figure 1.1).

Figure 2.1. Visual representation of dissertation research including two chapters on how climate

change is considered in food security monitoring and evaluation (Ch. 2 & 3), two chapters on

theory-driven evaluation (Ch. 4 & 5), and one chapter translating research into practice (Ch. 6).

2.10 Summary

This chapter introduces the importance of enhancing monitoring and evaluation tools for these

tools to continue to learn from and improve complex food security programs. In the context of

30

current calls to integrate climate change into all evaluations, this dissertation also explores how

food security program evaluations could account for climate change and other contextual

factors. Ultimately, this dissertation offers insights into how alternative approaches to evaluation

could support complex food security programs under climate change.

31

2.11 References

Allee, A., Lynd, L. R., & Vaze, V. (2021). Cross-national analysis of food security drivers:

comparing results based on the Food Insecurity Experience Scale and Global Food Security

Index. Food Security. https://doi.org/10.1007/s12571-021-01156-w

Ansah, I. G. K., Gardebroek, C., & Ihle, R. (2019). Resilience and household food security: a review

of concepts, methodological approaches and empirical evidence. In Food Security.

https://doi.org/10.1007/s12571-019-00968-1

Arksey, H., & O’Malley, L. (2005). Scoping studies: towards a methodological framework.

International Journal of Social Research Methodology, 8, 19–32.

Armitage, D., Arends, J., Barlow, N. L., Closs, A., Cloutis, G. A., Cowley, M., Davis, C., Dunlop, S. D.,

Ganowski, S., Hings, C., Rotich, L. C., Schang, K., Tsuji, S., & Wiens, C. (2019). Applying a

“theory of change” process to facilitate transdisciplinary sustainability education. Ecology

and Society, 24(3). https://doi.org/10.5751/ES-11121-240320

Ayala, A., & Meier, B. M. (2017). A human rights approach to the health implications of food and

nutrition insecurity. In Public Health Reviews. https://doi.org/10.1186/s40985-017-0056-5

Barrett, C. B. (2010). Measuring food insecurity. In Science.

https://doi.org/10.1126/science.1182768

Befani, B. (2020). Choosing Appropriate Evaluation Methods.

Belcher, B., Suryadarma, D., & Halimanjaya, A. (2017). Evaluating policy-relevant research: lessons

from a series of theory-based outcomes assessments. Palgrave Communications, 3(1).

https://doi.org/10.1057/palcomms.2017.17

Béné, C., Riba, A., & Wilson, D. (2020). Impacts of resilience interventions – Evidence from a

quasi-experimental assessment in Niger. International Journal of Disaster Risk Reduction.

https://doi.org/10.1016/j.ijdrr.2019.101390

Berner, J., Brubaker, M., Revitch, B., Kreummel, E., Tcheripanoff, M., & Bell, J. (2016). Adaptation in

Arctic circumpolar communities: Food and water security in a changing climate.

International Journal of Circumpolar Health, 75. https://doi.org/10.3402/ijch.v75.33820

Bird, F. A., Pradhan, A., Bhavani, R. V., & Dangour, A. D. (2019). Interventions in agriculture for

nutrition outcomes: A systematic review focused on South Asia. Food Policy.

https://doi.org/10.1016/j.foodpol.2018.10.015

32

Braun, V., Clarke, V., Hayfield, N., & Terry, G. (2018). Thematic analysis. In P. Liamputtong (Ed.),

Handbook of Research Methods in Health Social Sciences.

Breeman, G., Dijkman, J., & Termeer, C. (2015). Enhancing food security through a multi-

stakeholder process: the global agenda for sustainable livestock. Food Security, 7(2), 425–

435. https://doi.org/10.1007/s12571-015-0430-4

Busetto, L., Wick, W., & Gumbinger, C. (2020). How to use and assess qualitative research

methods. Neurological Research and Practice. https://doi.org/10.1186/s42466-020-00059-z

Carcary, M. (2009). The research audit trial - enhancing trustworthiness in qualitative inquiry.

Electronic Journal of Business Research Methods.

Carter, N., Bryant-Lukosius, D., Dicenso, A., Blythe, J., & Neville, A. J. (2014). The use of

triangulation in qualitative research. In Oncology Nursing Forum.

https://doi.org/10.1188/14.ONF.545-547

Centre for Food Policy. (2021). Understanding Lived Experience of Food Environments to Inform

Policy: An Overview of Research Methods.

CFS. (2012). Coming to Terms with Terminology: Food Security, Nutrition Security, Food Security

and Nutrition & Food and Nutrition Security. “Committee on World Food Security”

Proceedings of the 39th Session of the Committee on World Food Security.

Chandna, K., Vine, M. M., Snelling, S. J., Harris, R., Smylie, J., & Manson, H. (2019). Principles,

approaches, and methods for evaluation in indigenous contexts: A grey literature scoping

review. Canadian Journal of Program Evaluation. https://doi.org/10.3138/cjpe.43050

Chin, N., & Elliot, C. (2021). Why the First Global Stocktake Should Not Overlook Long-Term

Climate Strategies. World Resources Institute. https://www.wri.org/insights/why-first-

global-stocktake-should-not-overlook-long-term-climate-strategies

CIHR. (2010). A knowledge synthesis chapter.

Clark, A. M. (2016). Why qualitative research needs more and better systematic review. In

International Journal of Qualitative Methods. https://doi.org/10.1177/1609406916672741

Colquhoun, H. L., Levac, D., O’Brien, K. K., Straus, S., Tricco, A. C., Perrier, L., Kastner, M., & Moher,

D. (2014). Scoping reviews: Time for clarity in definition, methods, and reporting. In Journal

of Clinical Epidemiology (Vol. 67, Issue 12, pp. 1291–1294).

https://doi.org/10.1016/j.jclinepi.2014.03.013

33

Conevska, A., Ford, J., Lesnikowski, A., & Harper, S. (2018). Adaptation financing for projects

focused on food systems through the UNFCCC. Climate Policy, 0(0), 1–16.

https://doi.org/10.1080/14693062.2018.1466682

Craig, P., Di Ruggiero, E., Frohlich, K. L., Mykhalovskiy, E., & White, M. (2018). Taking account of

context in population health intervention research: guidance for producers, users and funders

of research.

Creswell, J. W. (2014). Research Design: Qualitative, Creswell, J. W. (2014). . Research design

Qualitative quantitative and mixed methods approaches. Research Design Qualitative

Quantitative and Mixed Methods Approaches.

Dalmer, N. K. (2020). Unsettling Knowledge Synthesis Methods Using Institutional Ethnography:

Reflections on the Scoping Review as a Critical Knowledge Synthesis Tool. Qualitative

Health Research. https://doi.org/10.1177/1049732320949167

Danielsen, F., Topp-Jørgensen, E., Levermann, N., Løvstrøm, P., Schiøtz, M., Enghoff, M., &

Jakobsen, P. (2014). Counting what counts: using local knowledge to improve Arctic

resource management. Polar Geography, 37(1), 69–91.

https://doi.org/10.1080/1088937X.2014.890960

Day, S. (2012). A reflexive lens: Exploring dilemmas of qualitative methodology through the

concept of reflexivity. Qualitative Sociology Review.

Dean-Coffey, J. (2018). What’s Race Got to Do With It? Equity and Philanthropic Evaluation

Practice. American Journal of Evaluation. https://doi.org/10.1177/1098214018778533

Devereux, S. (2007). The impact of droughts and floods on food security and policy options to

alleviate negative effects. Agricultural Economics, 37(S1), 47–58.

https://doi.org/10.1111/j.1574-0862.2007.00234.x

Dodd, W., Kipp, A., Bustos, M., McNeil, A., Little, M., & Lau, L. L. (2021). Humanitarian food

security interventions during the COVID-19 pandemic in low-and middle-income countries:

A review of actions among non-state actors. In Nutrients.

https://doi.org/10.3390/nu13072333

Douedari, Y., Alhaffar, M., Duclos, D., Al-Twaish, M., Jabbour, S., & Howard, N. (2021). ‘We need

someone to deliver our voices’: reflections from conducting remote qualitative research in

Syria. Conflict and Health. https://doi.org/10.1186/s13031-021-00361-w

Douthwaite, B., Mur, R., Audouin, S., Wopereis, M., Hellin, J., Moussa, A.S., Karbo, N., Kasten, W.,

Bouyer, J. (2017). Agricultural Research for Development to Intervene Effectively in Complex

34

Systems and the Implications for Research Organizations.

Ebi, K. L., & Del Barrio, M. O. (2017). Lessons learned on health adaptation to climate variability

and change: Experiences across low- and middle-income countries. In Environmental Health

Perspectives (Vol. 125, Issue 6). https://doi.org/10.1289/EHP405

Economist Impact. (2021). Methodology.

https://impact.economist.com/sustainability/project/food-security-

index/Home/Methodology

El Bilali, H., Callenius, C., Strassner, C., & Probst, L. (2019). Food and nutrition security and

sustainability transitions in food systems. In Food and Energy Security (Vol. 8, Issue 2).

https://doi.org/10.1002/fes3.154

Englander, M. (2019). General knowledge claims in qualitative research. Humanistic Psychologist.

https://doi.org/10.1037/hum0000107

EvalForward. (2021). The role of evaluation for climate action.

https://www.evalforward.org/webinars/evaluation-climate-action

Fanzo, J., Haddad, L., Schneider, K. R., Béné, C., Covic, N. M., Guarin, A., Herforth, A. W., Herrero,

M., Sumaila, U. R., Aburto, N. J., Amuyunzu-Nyamongo, M., Barquera, S., Battersby, J., Beal,

T., Bizzotto Molina, P., Brusset, E., Cafiero, C., Campeau, C., Caron, P., … Rosero Moncayo, J.

(2021). Viewpoint: Rigorous monitoring is necessary to guide food system transformation in

the countdown to the 2030 global goals. In Food Policy.

https://doi.org/10.1016/j.foodpol.2021.102163

FAO, IFAD, UNICEF, W. and W. (2018). The state of food security and nutrition in the world.

FAO, IFAD, UNICEF, W. and W. (2021). The State of Food Security and Nutrition in the World 2021.

Farrell, P., Thow, A. M., Abimbola, S., Faruqui, N., & Negin, J. (2018). How food insecurity could

lead to obesity in LMICs. Health Promotion International.

https://doi.org/10.1093/heapro/dax026

Faure, G., Blundo-Canto, G., Devaux-Spatarakis, A., Le Guerroué, J. L., Mathé, S., Temple, L.,

Toillier, A., Triomphe, B., & Hainzelin, E. (2020). A participatory method to assess the

contribution of agricultural research to societal changes in developing countries. Research

Evaluation. https://doi.org/10.1093/reseval/rvz036

Foran, T., Butler, J. R. A., Williams, L. J., Wanjura, W. J., Hall, A., Carter, L., & Carberry, P. S. (2014).

Taking complexity in food systems seriously: An interdisciplinary analysis. World

35

Development, 61, 85–101. https://doi.org/10.1016/j.worlddev.2014.03.023

Friedrichsen, C. N., Daroub, S. H., Monroe, M. C., Stepp, J. R., & Wani, S. P. (2018). Mental Models

of Soil Management for Food Security in Peri-Urban India. Urban Agriculture & Regional

Food Systems. https://doi.org/10.2134/urbanag2017.08.0002

Gbegbelegbe, S., Chung, U., Shiferaw, B., Msangi, S., & Tesfaye, K. (2014). Quantifying the impact

of weather extremes on global food security: A spatial bio-economic approach. Weather

and Climate Extremes, 4, 96–108. https://doi.org/10.1016/j.wace.2014.05.005

Godrich, S. L., Barbour, L., & Lindberg, R. (2021). Problems, policy and politics – perspectives of

public health leaders on food insecurity and human rights in Australia. BMC Public Health.

https://doi.org/10.1186/s12889-021-11188-8

Green, S., Higgins P., T., J., Alderson, P., Clarke, M., Mulrow D, C., & Oxman D, A. (2011). Cochrane

Handbook: Cochrane Reviews: Ch 8: Assessing risk of bias in included studies. In Cochrane

Handbook for: Systematic Reviews of Interventions (Vol. 6, pp. 3–10).

j:%5CWMCSU%5CWORK PROGRAMME%5CPROJECTS TRAINING%5C2_EXTERNAL

EDUCATION & TRAINING%5CCOURSES - Planned Training%5CUoB_EVIDENCE REVIEW

Training%5CCOURSES RUN

Greyson, D., Rafferty, E., Slater, L., MacDonald, N., Bettinger, J. A., Dubé, È., & MacDonald, S. E.

(2019). Systematic review searches must be systematic, comprehensive, and transparent: A

critique of Perman et al. In BMC Public Health. https://doi.org/10.1186/s12889-018-6275-y

Guba, E. G. E., & Lincoln, Y. S. Y. (1994). Competing Paradigms in Qualitative Research. In

Handbook of qualitative research (pp. 105–117).

https://doi.org/http://www.uncg.edu/hdf/facultystaff/Tudge/Guba%20&%20Lincoln%20199

4.pdf

Hamel, C., Michaud, A., Thuku, M., Skidmore, B., Stevens, A., Nussbaumer-Streit, B., & Garritty, C.

(2021). Defining rapid reviews: a systematic scoping review and thematic analysis of

definitions and defining characteristics of rapid reviews. In Journal of Clinical Epidemiology.

https://doi.org/10.1016/j.jclinepi.2020.09.041

Hammersley, M. (2020). Reflections on the Methodological Approach of Systematic Reviews. In

Systematic Reviews in Educational Research. https://doi.org/10.1007/978-3-658-27602-7_2

Hawe, P. (2015). Lessons from Complex Interventions to Improve Health. Annual Review of Public

Health, 36(1), 307–323. https://doi.org/10.1146/annurev-publhealth-031912-114421

Haysom, G., & Tawodzera, G. (2018). “Measurement drives diagnosis and response”: Gaps in

36

transferring food security assessment to the urban scale. Food Policy.

https://doi.org/10.1016/j.foodpol.2017.12.001

Hendriks, S. (2020). Food security policy, evaluation and impact assessment. Earthscan.

Hendriks, S. L. (2015). The food security continuum: a novel tool for understanding food

insecurity as a range of experiences. Food Security, 7(3), 609–619.

https://doi.org/10.1007/s12571-015-0457-6

Holley, C. E., & Mason, C. (2019). A Systematic Review of the Evaluation of Interventions to

Tackle Children’s Food Insecurity. In Current Nutrition Reports (Vol. 8, Issue 1, pp. 11–27).

https://doi.org/10.1007/s13668-019-0258-1

ICRISAT. (2021). MONITORING AND EVALUATION KEY STEPS FOR FOOD SYSTEM

TRANSFORMATIONS. https://www.icrisat.org/monitoring-and-evaluation-key-steps-for-

food-system-transformations/

IPES-Food. (2015). THE NEW SCIENCE OF SUSTAINABLE FOOD SYSTEMS.

Jaye, C. (2002). Doing qualitative research in general practice: Methodological utility and

engagement. Family Practice. https://doi.org/10.1093/fampra/19.5.557

Johnsen, J. T., Buckner, L., & Ray, S. (2020). Knowledge synthesis and translation in global food

and nutrition security to evaluate and accelerate priority actions. BMJ Nutrition, Prevention

& Health. https://doi.org/10.1136/bmjnph-2020-000104

Johnson, N., Behe, C., Danielsen, F., Nickels, S., & Pulsifer, P. L. (n.d.). Community-Based

Monitoring and Indigenous Knowledge in a Changing Arctic :

http://www.inuitcircumpolar.com/uploads/3/0/5/4/30542564/cbm_final_report.pdf

Jones, A. D., Ngure, F. M., Pelto, G., & Young, S. L. (2013). What Are We Assessing When We

Measure Food Security? A Compendium and Review of Current Metrics. Advances in

Nutrition: An International Review Journal, 4(5), 481–505.

https://doi.org/10.3945/an.113.004119

Kastner, M., Tricco, A. C., Soobiah, C., Lillie, E., Perrier, L., Horsley, T., Welch, V., Cogo, E., Antony,

J., & Straus, S. E. (2012). What is the most appropriate knowledge synthesis method to

conduct a review? Protocol for a scoping review. BMC Medical Research Methodology.

https://doi.org/10.1186/1471-2288-12-114

Kidoido, M., & Child, K. (2014). Evaluating value chain interventions: A review of recent evidence.

37

Kusters, C., ten Hove, H., Bosch, D., Herens, M., Wigboldus, S. (2019). Conference Report:

Monitoring and Evaluation for Inclusive and Sustainable Food Systems.

Lake, I. R., Hooper, L., Abdelhamid, A., Bentham, G., Boxall, A. B. A., Draper, A., Fairweather-Tait,

S., Hulme, M., Hunter, P. R., Nichols, G., & Waldron, K. W. (2012). Climate change and food

security: Health impacts in developed countries. Environmental Health Perspectives, 120(11),

1520–1526. https://doi.org/10.1289/ehp.1104424

Lam, S., Barot, M., Nguyen-Viet, H., & Unger, F. (2016). Changes in researcher capacity in

assessing food safety risks and value chains: Insights from PigRisk team. ILRI. Hanoi.

Lam, S., Dodd, W., Whynot, J., & Skinner, K. (2019). How is gender being addressed in the

international development evaluation literature? A meta-evaluation. Research Evaluation,

28(2), 158–168. https://doi.org/10.1093/reseval/rvy042

Leroy, J. L., Ruel, M., Frongillo, E. A., Harris, J., & Ballard, T. J. (2015). Measuring the food access

dimension of food security: A critical review and mapping of indicators. Food and Nutrition

Bulletin. https://doi.org/10.1177/0379572115587274

Leung, C. W., Kullgren, J. T., Malani, P. N., Singer, D. C., Kirch, M., Solway, E., & Wolfson, J. A.

(2020). Food insecurity is associated with multiple chronic conditions and physical health

status among older US adults. Preventive Medicine Reports.

https://doi.org/10.1016/j.pmedr.2020.101211

Levinson, F. J., & Herforth, A. (2013). Monitoring and Evaluating the Food Security and Nutrition

Effects of Agricultural Projects.

Lindahl, J. F., Mutua, F., & Grace, D. (2020). Evaluating farm-level livestock interventions in low-

income countries: A scoping review of what works, how, and why. In Animal Health

Research Reviews. https://doi.org/10.1017/S1466252320000146

Lockwood, C., dos Santos, K. B., & Pap, R. (2019). Practical Guidance for Knowledge Synthesis:

Scoping Review Methods. In Asian Nursing Research.

https://doi.org/10.1016/j.anr.2019.11.002

Maru, Y., Sparrow, A., Stirzaker, R., & Davies, J. (2018). Integrated agricultural research for

development (IAR4D) from a theory of change perspective. Agricultural Systems, 165, 310–

320. https://doi.org/10.1016/j.agsy.2016.09.012

Maru, Y. T., Sparrow, A., Butler, J. R. A., Banerjee, O., Ison, R., Hall, A., & Carberry, P. (2018).

Towards appropriate mainstreaming of “Theory of Change” approaches into agricultural

research for development: Challenges and opportunities. Agricultural Systems, 165, 344–

38

353. https://doi.org/10.1016/j.agsy.2018.04.010

Maxwell, S., & Frankenberger, T. R. (1992). Household food security: concepts, indicators, and

measurements: A technical review.

Mbow, C., Rosenzweig, C., Barioni, L. G., Benton, T. G., Herrero, M., Krishnapillai, M., Liwenga, E.,

Pradhan, P., Rivera-Ferre, M. G., Sapkota, T., Tubiello, F. N., & Xu, Y. (2019). Food Security. In

P. Z. P.R. Shukla, J. Skea, E. Calvo Buendia, V. Masson-Delmotte, H.-O. Pörtner, D.C. Roberts,

J. P. P. R. Slade, S. Connors, R. van Diemen, M. Ferrat, E. Haughey, S. Luz, S. Neogi, M.

Pathak, J. Petzold, & J. M. P. Vyas, E. Huntley, K. Kissick, M. Belkacemi (Eds.), Climate Change

and Land: an IPCC special report on climate change, desertification, land degradation,

sustainable land management, food security, and greenhouse gas fluxes in terrestrial

ecosystems.

McDermott, J., Johnson, N., Kadiyala, S., Kennedy, G., & Wyatt, A. J. (2015). Agricultural research

for nutrition outcomes - rethinking the agenda. Food Security, 7(3), 593–607.

https://doi.org/10.1007/s12571-015-0462-9

Moore, G., Audrey, S., Barker, M., Bond, L., Bonell, C., Cooper, C., Hardeman, W., Moore, L.,

O’Cathain, A., Tinati, T., Wight, D., & Baird, J. (2014). Process evaluation in complex public

health intervention studies: The need for guidance. In Journal of Epidemiology and

Community Health. https://doi.org/10.1136/jech-2013-202869

Moore, G. F., & Evans, R. E. (2017). What theory, for whom and in which context? Reflections on

the application of theory in the development and evaluation of complex population health

interventions. In SSM - Population Health (Vol. 3, pp. 132–135).

https://doi.org/10.1016/j.ssmph.2016.12.005

Morales, D. X., Morales, S. A., & Beltran, T. F. (2020). Racial/Ethnic Disparities in Household Food

Insecurity During the COVID-19 Pandemic: a Nationally Representative Study. Journal of

Racial and Ethnic Health Disparities. https://doi.org/10.1007/s40615-020-00892-7

Mozaffarian, D., Fleischhacker, S., & Andrés, J. R. (2021). Prioritizing Nutrition Security in the US.

In JAMA - Journal of the American Medical Association.

https://doi.org/10.1001/jama.2021.1915

Mulhall, A. (2003). In the field: Notes on observation in qualitative research. Journal of Advanced

Nursing. https://doi.org/10.1046/j.1365-2648.2003.02514.x

Munn, Z., Peters, M. D. J., Stern, C., Tufanaru, C., McArthur, A., & Aromataris, E. (2018). Systematic

review or scoping review? Guidance for authors when choosing between a systematic or

scoping review approach. BMC Medical Research Methodology.

39

https://doi.org/10.1186/s12874-018-0611-x

Myers, S. S., Smith, M. R., Guth, S., Golden, C. D., Vaitla, B., Mueller, N. D., Dangour, A. D., &

Huybers, P. (2017). Climate Change and Global Food Systems: Potential Impacts on Food

Security and Undernutrition. Annual Review of Public Health, 38(1), 259–277.

https://doi.org/10.1146/annurev-publhealth-031816-044356

Niles, M. T., & Brown, M. E. (2017). A multi-country assessment of factors related to smallholder

food security in varying rainfall conditions. Scientific Reports, 7(1).

https://doi.org/10.1038/s41598-017-16282-9

O’Cathain, A., Croot, L., Duncan, E., Rousseau, N., Sworn, K., Turner, K. M., Yardley, L., &

Hoddinott, P. (2019). Guidance on how to develop complex interventions to improve health

and healthcare. BMJ Open. https://doi.org/10.1136/bmjopen-2019-029954

Paparini, S., Papoutsi, C., Murdoch, J., Green, J., Petticrew, M., Greenhalgh, T., & Shaw, S. E.

(2021). Evaluating complex interventions in context: systematic, meta-narrative review of

case study approaches. BMC Medical Research Methodology.

Pawson, R., Tilley, R. (1997). Realistic evaluation.

Pham, M. T., Rajić, A., Greig, J. D., Sargeant, J. M., Papadopoulos, A., & Mcewen, S. A. (2014). A

scoping review of scoping reviews: Advancing the approach and enhancing the consistency.

Research Synthesis Methods. https://doi.org/10.1002/jrsm.1123

Phillippi, J., & Lauderdale, J. (2018). A Guide to Field Notes for Qualitative Research: Context and

Conversation. Qualitative Health Research. https://doi.org/10.1177/1049732317697102

Power, E. M. (2008). Conceptualizing food security for aboriginal people in Canada. Canadian

Journal of Public Health, 99(2), 95–97. https://doi.org/10.1016/j.gloenvcha.2007.09.002

Ragavan, M. I., Marcil, L. E., & Garg, A. (2020). Climate change as a social determinant of health.

Pediatrics. https://doi.org/10.1542/PEDS.2019-3169

Rajala, E., Vogel, I., Sundin, A., Kongmanila, D., Nassuna-Musoke, M. G., Musundire, R.,

Mulangala, M. N., Chiwona-Karltun, L., Magnusson, U., & Boqvist, S. (2021). How can

agricultural research translation projects targeting smallholder production systems be

strengthened by using Theory of Change? Global Food Security.

https://doi.org/10.1016/j.gfs.2020.100475

Richardson, R. A., & Patton, M. Q. (2021). Leadership-evaluation partnership: Infusing systems

principles and complexity concepts for a transformational alliance. New Directions for

40

Evaluation. https://doi.org/10.1002/ev.20461

Rørtveit, K., Saetre Hansen, B., Joa, I., Lode, K., & Severinsson, E. (2020). Qualitative evaluation in

nursing interventions—A review of the literature. In Nursing Open.

https://doi.org/10.1002/nop2.519

Rowe, A. (2019). Sustainability-Ready Evaluation: A Call to Action. New Directions for Evaluation,

2019(162), 29–48. https://doi.org/10.1002/ev.20365

Russell, J., Lechner, A., Hanich, Q., Delisle, A., Campbell, B., & Charlton, K. (2018). Assessing food

security using household consumption expenditure surveys (HCES): A scoping literature

review. In Public Health Nutrition. https://doi.org/10.1017/S136898001800068X

Schmidhuber, J., & Tubiello, F. N. (2007). Global food security under climate change. Proceedings

of the National Academy of Sciences of the United States of America, 104(50), 19703–19708.

https://doi.org/10.1073/pnas.0701976104

Shepherd, B. (2012). Thinking critically about food security. Security Dialogue.

https://doi.org/10.1177/0967010612443724

Skivington, K., Matthews, L., Simpson, S. A., Craig, P., Baird, J., Blazeby, J. M., Boyd, K. A., Craig, N.,

French, D. P., McIntosh, E., Petticrew, M., Rycroft-Malone, J., White, M., & Moore, L. (2021). A

new framework for developing and evaluating complex interventions: Update of Medical

Research Council guidance. The BMJ. https://doi.org/10.1136/bmj.n2061

Ssekamatte, D. (2018). The role of monitoring and evaluation in climate change mitigation and

adaptation interventions in developing countries. African Evaluation Journal, 6(1).

https://doi.org/10.4102/aej.v6i1.254

Steele Gray, C., & Shaw, J. (2019). From summative to developmental: Incorporating design-

thinking into evaluations of complex interventions. Journal of Integrated Care.

https://doi.org/10.1108/JICA-07-2018-0053

Stephenson, E. S. (2020). Akaqsarnatik: Food, power, and policy in Arctic Canada. McGill

University.

Tarasuk, V., Fafard St-Germain, A. A., & Mitchell, A. (2019). Geographic and socio-demographic

predictors of household food insecurity in Canada, 2011-12. BMC Public Health.

https://doi.org/10.1186/s12889-018-6344-2

Tendall, D. M., Joerin, J., Kopainsky, B., Edwards, P., Shreck, A., Le, Q. B., Kruetli, P., Grant, M., &

Six, J. (2015). Food system resilience: Defining the concept. In Global Food Security (Vol. 6,

41

pp. 17–23). https://doi.org/10.1016/j.gfs.2015.08.001

The National Assembly. (2010). Law No. 55/2010/QH12. https://vanbanphapluat.co/law-no-55-

2010-qh12-of-june-17-2010-on-food-safety

The World Bank. (2012). Monitoring Agricultural Innovation System Interventions.

Thirsk, L. M., & Clark, A. M. (2017). Using Qualitative Research for Complex Interventions: The

Contributions of Hermeneutics. International Journal of Qualitative Methods.

https://doi.org/10.1177/1609406917721068

Tomaszewski, L. E., Zarestky, J., & Gonzalez, E. (2020). Planning Qualitative Research: Design and

Decision Making for New Researchers. International Journal of Qualitative Methods.

https://doi.org/10.1177/1609406920967174

Tompkins, E. L., Vincent, K., Nicholls, R. J., & Suckall, N. (2018). Documenting the state of

adaptation for the global stocktake of the Paris Agreement. Wiley Interdisciplinary Reviews:

Climate Change, 9(5), 1–9. https://doi.org/10.1002/wcc.545

Tricco, A. C., Antony, J., Soobiah, C., Kastner, M., Macdonald, H., Cogo, E., Lillie, E., Tran, J., &

Straus, S. E. (2016). Knowledge synthesis methods for integrating qualitative and

quantitative data: A scoping review reveals poor operationalization of the methodological

steps. Journal of Clinical Epidemiology. https://doi.org/10.1016/j.jclinepi.2015.12.011

Turner, C., Aggarwal, A., Walls, H., Herforth, A., Drewnowski, A., Coates, J., Kalamatianou, S., &

Kadiyala, S. (2018). Concepts and critical perspectives for food environment research: A

global framework with implications for action in low- and middle-income countries. In

Global Food Security. https://doi.org/10.1016/j.gfs.2018.08.003

Uitto, J.I., Puri, J., & van den Berg, R. D. (2016). Evaluating Climate Change Action for Sustainable

Development. Springer.

Uitto, Juha I. (2019). Sustainable Development Evaluation: Understanding the Nexus of Natural

and Human Systems. New Directions for Evaluation, 2019(162), 49–67.

https://doi.org/10.1002/ev.20364

UN. (2021). The food systems summit. https://www.un.org/food-systems-summit

UN General Assembly. (1948). Universal Declaration of Human Rights | United Nations. In

General Assembly resolution.

UNEG. (2013). UNEG Handbook for Conducting Evaluations of Normative Work in the UN System.

42

United Nations. (1975). Report of the World Food Conferance Rome, 5-16 November 1974.

United Nations Publication.

United Nations. (2021a). COP26 closes with ‘compromise’ deal on climate, but it’s not enough,

says UN chief. https://news.un.org/en/story/2021/11/1105792

United Nations. (2021b). With 30 Million Facing Famine, Secretary-General Announces Prevention

Task Force, Warns Security Council against Cutting Aid as Solution to Economic Woes.

https://www.un.org/press/en/2021/sgsm20619.doc.htm

Urke, H. B., Cao, Z. R., & Egeland, G. M. (2014). Validity of a single item food security

questionnaire in Arctic Canada. Pediatrics. https://doi.org/10.1542/peds.2013-3663

van Nes, F., Abma, T., Jonsson, H., & Deeg, D. (2010). Language differences in qualitative

research: Is meaning lost in translation? European Journal of Ageing.

https://doi.org/10.1007/s10433-010-0168-y

Varma, D. S., Young, M. E., Kreider, C. M., Williams, K., Vaddiparti, K., Parisi, C., & Semeah, L. M.

(2021). Practical Considerations in Qualitative Health Research During the COVID-19

Pandemic. International Journal of Qualitative Methods.

https://doi.org/10.1177/16094069211043755

Vidueira, P. (2019). Blue marble evaluation: a personal, professional and organizational

transformation. Global Alliance for the Future of Food.

von Grebmer, K., Bernstein, J., Wiemers, M., Acheampong, K., Hanano, A., Higgins, B.,

Cheilleachair, R.N., Foley, C., Gitter, S., Ekstrom, K., Fritschel, H. (2020). 2020 Global Hunger

Index.

Wanzer, D. L. (2021). What Is Evaluation?: Perspectives of How Evaluation Differs (or Not) From

Research. American Journal of Evaluation. https://doi.org/10.1177/1098214020920710

WFP. (2012). Monitoring Food Security.

Young, I., Waddell, L., Harding, S., Greig, J., Mascarenhas, M., Sivaramalingam, B., Pham, M. T., &

Papadopoulos, A. (2015). A systematic review and meta-analysis of the effectiveness of

food safety education interventions for consumers in developed countries. In BMC Public

Health. https://doi.org/10.1186/s12889-015-2171-x

Zurayk, R. (2020). Pandemic and Food Security: A View from the Global South. Journal of

Agriculture, Food Systems, and Community Development.

https://doi.org/10.5304/jafscd.2020.093.014

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CHAPTER 2: COMMUNITY-BASED MONITORING OF INDIGENOUS FOOD SECURITY IN A CHANGING CLIMATE: GLOBAL TRENDS AND FUTURE DIRECTIONS

Abstract

Climate change is expected to exacerbate existing food security challenges, especially in

Indigenous communities worldwide. Community-based monitoring is considered a promising

strategy to improve monitoring of, and local adaptation to climatic and environmental change.

Yet, it is unclear how this approach can be applied in food security or Indigenous contexts. The

objectives of this paper are to: 1) review and synthesize the published literature on community-

based monitoring of Indigenous food security; and, 2) identify gaps and trends in these

monitoring efforts in the context of climate change. Using a systematic search and screening

process, we identified 86 published articles. Relevant articles were thematically analyzed to

characterize elements of community-based monitoring in the context of climate change. Results

show that the number of articles published over time was steady and increased more than two-

fold within the last five years. The reviewed articles reported on monitoring mainly in North

America (37%) and South America (28%). In general, monitoring was either collaborative (51%)

or externally-driven (37%), and focused primarily on tracking wildlife (29%), followed by natural

resources (16%), environmental change (15%), fisheries (13%), climate change (9%), or some

combination of these topics (18%). This review provides an evidence-base on the uses,

characteristics, and opportunities of community-based monitoring, to guide future food security

monitoring efforts in the context of climate change.

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2.12 Introduction

Enhancing the resilience of different food systems to climate change via monitoring is an

important global health opportunity of the 21st century (1). Through routine monitoring and

assessments of climate-related risks and their interplay with food security, along with linking

early warnings to early responses, food and nutrition crises can be better managed (2,3). Such

efforts are especially crucial now as climate change increasingly challenges food security1 (4,5).

Changes in extreme weather events (6,7), temperature and rainfall variability (8,9), and sea level

(10), threaten food security by decreasing global food production and increasing the risk of

hunger and undernutrition (3,11). Projections indicate these food-related health impacts will far

exceed all other climate-related health risks (12). The effects of climate change on food systems

are expected to be widespread, complex, and variable, both geographically and temporally (13).

Investing in food systems adaptation to climate change across scales, particularly via monitoring,

decreases the risks and uncertainties for food and health systems (14).

The impacts of climate change will not be evenly distributed (15), with Indigenous peoples2

facing complex challenges to their food systems (16,17). Food systems encompass a number of

activities which give rise to a number of food security outcomes (i.e. stability of food access,

1 Food security can be defined as “a situation that exists when all people, at all times, have physical, social and

economic access to sufficient, safe and nutritious food that meets their dietary needs and food preferences for an

active and healthy life” (63). 2 Indigenous peoples can be defined as “the assembly of those who have witnessed, been excluded from, and have

survived modernity and imperialism. They are peoples who have experienced the imperialism and colonialism of the

modern historical period beginning with the Enlightenment. They remain culturally distinct, some with their native

languages and belief systems still alive” (129, p. 114).

45

utilization, and availability); we use the term ‘Indigenous food systems’ to refer to systems of

production, process, distribution, and consumption, which are specific to particular geographic

regions (18,19). Several factors make Indigenous food systems particular sensitive to climate

change impacts. These include: histories and ongoing pressures of colonialism and land

dispossession that have disconnected Indigenous peoples from their land and local knowledge

of food practices (20,21), high burden of existing food security challenges (17), structural

inequities characterized by lack of access to land and other resources (22–24), and habitation in

areas undergoing rapid environmental change, biodiversity loss, and competing demands for

land for food production (25). Indeed, Indigenous communities in many countries tend to be

more food insecure than their non-Indigenous counterparts (26–28); for example, Indigenous

peoples in the United States including American Indians and Alaska Natives were twice as likely

to be food insecure compared to non-Indigenous peoples (29). Around 97% of Indigenous

Batwa households in Uganda were found to be food insecure, which was substantially higher

than the national Ugandan average of 20% (30). Furthermore, Indigenous peoples often have

close relationships with the environment for subsistence; as such, even subtle changes in the

environment can have large impacts on their food security (31,32), including reducing access to,

and availability of, Indigenous foods (33,34).

A food security monitoring system can help reduce climate change impacts on vulnerable food

systems (35). The information captured by the monitoring system can be used for several

purposes: to contribute to monitoring the implementation of international commitments (e.g.,

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Sustainable Development Goals, United Nations Framework Convention on Climate Change,

Paris Agreement); to identify vulnerable areas; to serve as an early warning system for

impending food crises (36–38); and, to inform climate change adaptation3 strategies (39,40).

However, such monitoring systems currently face several major challenges. Due to the diverse

conceptualizations of food security , measurement tools, and intended uses of information, it is

often not clear what exactly is being assessed when we measure food security (41). Secondly,

food security monitoring is typically done through population-based surveys at the national

level (2,38,42). These surveys are generally not designed to provide nuanced understandings of

food security among populations, do not adequately engage with Indigenous communities (42–

44), and are not appropriate for understanding food security of certain population groups

(37,45). For example, a widely used and adapted income-based measure, the Household Food

Security Survey Module does not capture Indigenous food cultures (46,47); instead, it presents a

static snapshot of food security even though Indigenous food systems vary substantially by

household and season (16). Finally, measures of attributing food security challenges to climate

change are not well-developed (48,49); thus, it is not clear whether challenges are due to climate

change or other factors. Yet, overcoming these challenges is key to understanding current and

projected food security and climate-related food shocks (2).

3 Climate change adaptation can be defined as: “In human systems, the process of adjustment to actual or expected

climate and its effects, in order to moderate harm or exploit beneficial opportunities. In natural systems, the process

of adjustment to actual climate and its effects; human intervention may facilitate adjustment to expected climate and

its effects” (131).

47

Community-based monitoring (CBM) is often considered a promising strategy to improve

monitoring of, and local adaptation to, environmental change (50–52). CBM is an approach

whereby groups collaborate to track and respond to issues of common community concern (50).

This approach can take several forms ranging from community-directed monitoring initiatives

originating from communities’ interests and needs to initiatives that simply involve communities

in data collection (53). Similarly, the potential benefits of CBM also vary, including: improved

understanding of long-term trends; reduced cost of research by leveraging existing

infrastructure; skills development and employment opportunities for local monitors; and

provision of timely and relevant information for local decision-making (51,54,55). Moreover, as

many Indigenous communities have been monitoring the environment for centuries (56,57),

there are opportunities to use both Indigenous and Western knowledge systems in CBM to

develop a deeper understanding of pressures on the environment as they arise (58). CBM can be

a key component of community-based adaptation by working with Indigenous communities and

knowledge systems to prepare for the food-related health impacts of climate change (59).

Considering the promise of CBM, the disproportionate food security challenges experienced by

Indigenous communities, and the high sensitivity of Indigenous food systems to climate change,

the goal of our review was to understand and learn from how CBM has been used globally to

track and respond to Indigenous food security and climate-related food challenges. Specifically,

our objectives were to review and synthesize the published literature on CBM of Indigenous

food security in a climate change context. In doing so, we accumulate the knowledge and

48

experiences of developing, implementing, and evaluating CBM systems worldwide. Moreover,

we highlight how Indigenous food security monitoring is different from general food security

monitoring. This is a step toward informing community-based adaptation efforts for addressing

food security challenges of Indigenous communities worldwide.

2.13 Methods

We examined the published literature using a systematic review methodology for climate

change adaptation outlined by Berrang-Ford et al. (2015) involving a stepwise process of

selection, extraction, analysis, and synthesis of the literature (60). To guide our review and

synthesis of trends and gaps, we posed the following question: What does the published

literature tell us about Indigenous community-based monitoring of food security in the context

of climate change?

2.13.1 Search strategy

The initial search for published articles was performed on 5 November 2017 and later updated

on 15 March 2018 using the following databases: AGRICOLA©, PRISMA©, MEDLINE®, CabDirect©,

and the Web of Science™ CORE Collection (Appendix 1). These databases cover agriculture,

health, sociology, and environmental disciplines, therefore providing the opportunity to capture

the broad literature as well as approach the research question from different perspectives. No

search restrictions were placed (e.g. language, date). Each database search used Boolean

operators to pair keywords (Indigenous, monitoring systems, food security / climate change,

community-based) with their synonyms (Table 2.1).

49

2.13.2 Citation management

All citations were imported into the web-based application DistillerSR© (Evidence Partners

Incorporated, Ottawa, ON, Canada). Duplicate citations were removed using the duplicate

removal function.

2.13.3 Relevance screening and eligibility

A two-step relevance screening strategy was employed by two independent reviewers (SL, CZ).

First, the titles and abstracts of articles were screened. Next, all citations deemed potentially

relevant went through a review of the full-text. We included articles that: 1) were published in

journals; 2) described a CBM system; 3) described any aspect of food security or food-related

climate change impacts; and 4) explicitly mentioned an Indigenous community (Table 2.2). The

reference lists of all relevant articles were hand-searched to identify any further relevant studies

not captured in the database search. Reviewers met throughout the screening process to resolve

conflicts and discuss any uncertainties related to study selection. The degree of agreement

between reviewers (i.e., interrater reliability) was assessed using Cohen’s kappa at both stages of

screening (61).

2.13.4 Data extraction and synthesis

A charting form was developed by the authors to capture both count data and information on

the study (62). Information extracted from the paper included the last name of the first author,

year of publication, and whether an author was affiliated with an Indigenous organization or

community (Table 2.3). Descriptions of the CBM system were charted, including the target

50

country, target community, and methods, as well as food security, Indigenous knowledge,

climate change, and gender considerations. We counted whether the CBM system explicitly

mentioned “food security” as well as explicitly mentioned one of the food security pillars (e.g.

access, availability, utilization, stability) (63). We also extracted information on the type of food

source and driver of food security challenges monitored. We counted whether Indigenous

knowledge and climate change were explicitly mentioned. Considering that climate change

impacts will not be gender-neutral (16,64), it is important that responses to climatic stresses not

be limited in the agri-food sector by gender-based constraints. As such, we assessed for gender

considerations in CBM by adapting questions based on a quantitative tool that supports

standardization of sex and gender reporting in publications (65). We also explored the nature of

gender discourse through thematic analysis techniques (66). Specifically, each of these articles

were coded to capture how gender was framed, focusing on gender perspectives and

participation. We also categorized the CBM study broadly as having described: 1) the

development of the monitoring system; or 2) the implementation/evaluation of the monitoring

system. For the latter, we examined each article for evidence to suggest that it could be

classified into one of four general CBM categories: autonomous local monitoring; collaborative

monitoring; consultative monitoring; and externally driven monitoring (67,68). Finally, we

characterized these articles as having an evaluation component if they assessed the

process/implementation, outcome, or impact of the monitoring system.

51

Table 0.1. Search strategy to identify published articles on Indigenous community-based

monitoring of Indigenous food security.

Main terms Expanded terms

Indigenous a Aasax OR Aboriginal OR "Aboriginal-Malay" OR Aborigine OR […]a

Monitoring surveillance OR tracking OR monitoring OR reporting OR "information system"

OR "early warning" OR "early detection" OR "early notification" OR "timely

warning" OR "timely detection" OR "timely notification"

Food security and

climate change

food OR agriculture OR nutrition OR livestock OR fish* OR animal OR plant OR

wildlife OR hunt* OR gather* OR environment* OR ecological OR ecosystem OR

"natural resource" OR "resource management" OR "co-management" OR

"cooperative management" OR "joint management" OR water OR sea OR ocean

OR "climate change" OR "climate variability" OR "climate hazard" OR "extreme

weather" OR "natural hazard" OR disaster OR flood OR drought OR hurricane OR

storm OR cyclone OR "sea level rise" OR "irregular rainfall" OR "intense rainfall"

OR resilience OR poverty OR livelihood OR welfare OR income

Community-based "community-based" OR "community-centred" OR "community-centered" OR

"community-engaged" OR "community-led" OR "locally-based" OR participatory

OR collaborative OR "citizen-led" OR "citizen-engaged" OR "citizen-based" OR

"citizen science" a Search terms used to identify Indigenous peoples globally were derived from Bishop-Williams et al. 2017

(69). A shortened list of expanded search terms was provided here, please see Appendix 2 for the full list

of expanded terms and Appendix 3 for the full list of included articles.

52

Table 0.2. Inclusion and exclusion criteria to identify published articles on community-based

monitoring of Indigenous food security and climate change.

Inclusion Exclusion

Original research published in a

journal

Study described community-based

monitoring or synonyms (e.g.

community-led surveillance)

Study discusses some aspect of

food security, drivers of food

security (e.g. climate change,

poverty), or synonyms (e.g. wildlife,

natural resource)

Study explicitly mentioned an

Indigenous community

Conference abstracts or proceedings, letters to the editor,

reports, news articles, dissertations

Community-based research without a monitoring component,

monitoring study without community-engagement

Study did not discuss food security in any way, study discussed

climate change with no reference to food security

Studies of Indigenous plants, animals, or knowledge without

reference to an Indigenous community, studies of non-

Indigenous communities

53

Table 0.3. Summary of information extracted from articles on community-based monitoring of

Indigenous food security.

Categories Information extracted

Information on the article - Last name of the first author

- Author affiliation with an Indigenous organization or community

(Y/N)

- Year of publication

Community-based

monitoring characteristics

- Study country

- Indigenous community

- Methods used

- Explicit mention of “food security” (Y/N)

- Discussion on food access, availability, or use

- Provided gender-disaggregated data (Y/N)

- Themes surrounding gender (e.g. gender perspectives and

participation)

- Explicit mention of climate change (Y/N)

- Explicit mention of Indigenous knowledge and/or traditional

knowledge (Y/N)

Community-based

monitoring focused on

implementation

- Monitoring approach (autonomous, collaborative, consultative,

externally-driven)

- Evaluation component (Y/N)

2.14 Results

2.14.1 Overview of relevant articles

There were 3986 articles identified through the database search (Figure 2.1). After removal of

duplicates and non-relevant articles, and the addition of articles from reference lists, a total of

86 articles were included. See supplementary file for the full list of included articles and selected

article characteristics. The inter-rater reliability for title/abstract article screening and full-text

article screening was 0.80 and 0.71, respectively, indicating “substantial agreement” (61).

54

Figure 0.1. Flow chart of the selection of studies that explored community-based monitoring of

Indigenous food security.

2.14.2 Diversity of approaches to community-based monitoring

The reviewed studies used several methodological approaches including quantitative (n=8),

qualitative (n=13), mixed methods (n=42), review (n=21), and other (n=42) methodologies4.

Other methodologies included the use of technology, including GIS mapping, GPS tracking, or

use of drones and aerial surveys. Around 42% of articles (n=36) had at least one author with an

affiliation to an Indigenous organization or community with no clear trend on Indigenous co-

4 Numbers do not add up to 86 studies as more than one approach was used in some studies.

55

authorship over time. The majority of articles (n=74) explicitly mentioned “Indigenous

knowledge” or “traditional knowledge” in the context of the study.

2.14.3 Most studies were published in the past decade

Initially, there was a limited the number of articles published following 2001, when articles were

first found. The number of publications increased more than two-fold from 2013 onwards. The

majority of reviewed articles reported on CBM in North America (n=32), followed by South

America (n=24), Australia and Oceania (n=11), Africa (n=6), and Asia (n=4) (Figure 2.2). Several

studies were conducted across multiple continents (n=9). Among the 31 studies published in

North America, most were from Canada (n=28). There was also a varied distribution of

Indigenous group representation, with most studies focused on Indigenous groups in Canada

(n=28), specifically First Nations (n=12), Inuit (n=10), and multiple groups (n=6). Studies also

focused on Indigenous groups of South America (n=25), specifically multiple groups (n=10),

Kaxinawa (n=3), Isoseno-Guarani (n=3), Waiwai (n=1), Xerente (n=1), Makushi (n=1), Matsigenka

(n=1), Kitchwa (n=2), Purepecha (n=1), Andean (n=1), and Amerindian (n=1). There were some

articles on multiple groups from different continents (n=9), Indigenous groups of Oceania

(n=11), Indigenous groups of Africa (n=6), Indigenous groups of Asia (n=4), and Native

Americans (n=3).

56

Figure 0.2. Geographic distribution of articles on community-based monitoring of Indigenous

food security.

2.14.4 Wildlife was a prominent type of food monitored

A wide variety of food sources were monitored, including wildlife (n=25), natural resources

(n=14), and fisheries (n=11). Drivers of food security were also explored, including

environmental change (n=13) and climate change (n=8). Several articles explored a combination

of food sources and food security drivers (n=15). The term “food security” was explicitly

mentioned in 33 articles (38%), while the specific food security pillars reported included food

availability (n=16), food access (n=11), and food utilization (n=6), or some combination of these

pillars (n=17). No articles explored food stability.

57

2.14.5 More articles focused on men’s participation in monitoring

A total of 29 articles (34%) provided gender-disaggregated data. Although 2017 had the highest

proportion of articles that provided gender-disaggregated data, there was no distinguishable

trend suggesting an increase or decrease in active gender considerations over time. For articles

that provided gender-disaggregated data and described the development of the monitoring

system (n=14), all articles considered perspectives of both men and women. The importance of

considering the perspectives of women was emphasized in a study in Nunavik, Canada, aimed to

understand Elders’ and hunters’ observations and knowledge: “Women were included upon the

recommendation of their expert knowledge of ice conditions or their frequency of travel” (64, p.

30). For the articles that provided gender-disaggregated data and described the implementation

of the monitoring system (n=15), all articles mentioned the participation of men, while some of

these articles (n=9) also mentioned the participation of women. One article actively encouraged

the participation of women in monitoring “as a way to acknowledge internally marginalized

groups and alleviate social inequality” (65, p. 22). Although some studies aimed to include equal

participation of men and women, they noted that participants tended to be men (70,72,73).

2.14.6 Climate change indicators were rarely assessed

More than half (56%) of studies (n=48) explicitly mentioned climate change in the context of

food security (Figure 2.3). There was no clear trend over time to suggest a general movement

towards increasing consideration of climate change in articles. While the majority of articles

58

mentioned climate change as justification for pursuing CBM, a limited number of articles (n=8)

described the implementation/evaluation of a community-based food security monitoring

system including climate change indicators. The studies that did consider climate change were

mostly situated in Arctic regions (70,74–77); for example, a study in Alaska employed a

participatory CBM system to explore environmental conditions likely associated with climate

change, health, and food security outcomes (75). In another study, an integrated CBM system in

Nunavik, Canada tracked climatic and ice conditions to support safe access to land and other

resources (70).

Figure 0.3. Articles on community-based monitoring of Indigenous food security with and

without climate change considerations, over time.

0

2

4

6

8

10

12

14

2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017

Nu

mb

er o

f ar

ticl

es

Climate change focus Non-climate change focus

59

2.14.7 Varying degrees of Indigenous community engagement in monitoring

Of the 86 included articles, 37 articles (43%) described work that recommended or informed the

development of CBM approaches. For example, Wesche et al. (2011) stated that their research

project “led to the process of establishing a community-based environmental monitoring

program” (68, p. 403). Most articles (n=49) described the implementation of an existing CBM

system. Among these 49 articles, we documented whether the authors evaluated the monitoring

system. We found that less than half of articles (n=22) reported an evaluation process or

outcome (78–80). These 49 articles were also classified according to the type of CBM approach

adopted (Table 2.4). No clear trend on the type of monitoring approach over time was

discernable.

Only one article reporting on autonomous local monitoring was identified (81). The objective of

this article was to highlight the existence of local monitoring practices based on observations in

three communities in Papua, Indonesia (81). The authors found that communities would monitor

and control their environment and resources, and found evidence of autonomous monitoring

activities in each of the three communities.

More than half of the reviewed articles (51%) were classified as collaborative monitoring. This

approach encouraged project co-creation, transfer of ownership, and knowledge sharing with

community members. An example of this approach was illustrated by Cummings et al. (2017).

The authors described steps taken to introduce drones in two Indigenous villages in Southern

60

Guyana and portrayed the extent of community engagement through the following statement:

“When the participants collect data on their missions, they have the first access to these, and can

decide whether to share the data with the non-indigenous [sic] project team members” (73, p.

13). In another example, the authors described: “A CyberTracker was developed and used by the

Naskapi Nation to verify forest-dwelling caribou presence in collaboration with New Millennium

Capital Corporation” (74, p. 39).

Compared to the other monitoring approaches discussed by articles, a relatively low number of

articles describing consultative monitoring were identified (10%). This CBM approach involved

some degree of decision-making by the community. An example of this approach was described

by Shaffer et al. (2017) where the authors “established a hunter self-monitoring program in

consultation with the Waiwai in July of 2014” (75, p. 1121). In the context of participatory

monitoring in the Amazon, the authors “provided technical support for the development of a

hunting monitoring system aimed at informing adaptive management processes for

sustainability” (76, p. 55). In both cases, community members were involved in identifying

monitoring goals and collecting data, while analysis was performed entirely by the researchers.

The proportion of publications classified as externally driven monitoring schemes was 37%. This

CBM approach involved community members only in data collection with no decision-making

by community members. For example, in one study: “All of the data in the study were collected

by locally recruited and trained indigenous [sic] technicians and most of the data-collection

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process was established a priori, without local input” (77, p. 771). The same authors also

emphasized the importance of knowledge sharing back to the community: “However, we sought

substantial input regarding the format and content of research results to be returned to

collaborating communities” (p. 772). In another study categorized as externally-driven, hunters

were invited to participate on a voluntary basis, and those who accepted were trained to fill

monitoring data sheets (87).

Table 0.4. Types of community-based monitoring approaches described in articles that reported

the implementation of a monitoring system. Adapted primarily from Kouril et al. 2015, Danielsen et al.

2009.

Category Characteristics Number

of

articles

Example

references

Autonomous local

monitoring

Community members are involved in the whole

monitoring process and make all decisions

1 (81)

Collaborative

monitoring

Community members are involved in data collection,

analysis, and interpretation; researchers and

community members make decisions together

25 (70,88–91)

Consultative

monitoring

Community members are involved in data collection

and are consulted; researchers make decisions

5 (84,85,92)

Externally driven

monitoring

Community members are involved only in data

collection or as research assistants, researchers make

all decisions

18 (75,86,87)

2.15 Discussion

This paper systematically examines trends in peer-reviewed publications on CBM. We found the

number of articles on CBM of Indigenous food security were limited but growing. Since 2013,

there has been an increase in the number of publications on this topic by more than two-fold.

62

This trend is consistent with previous studies on broader environmental CBM (50,67) and reflects

the need to include different sources of knowledge and different knowledge users in monitoring

efforts, instead of conventional monitoring approaches which are typically externally driven

(53,93). Furthermore, the increasing interest in CBM is part of a broader trend around the need

to address the disproportionate food security and climate change impacts often experienced by

Indigenous communities globally (17,26–28). The articles captured in this review mainly reported

on CBM in North America, and specifically Canada. This finding could be explained by the

current and projected severity of climate change impacts in the Arctic (such as Arctic Canada)

compared to the rest of world (94), and the need to understand and address such impacts

through CBM. Indeed, there has been a significant growth in research on, and funding for

climate change in Canada’s North (32). This geographic distribution of articles also highlights

gaps in CBM research in many regions where community-level vulnerability is thought to be

significant, particularly in low- and middle-income regions such as Africa and Asia. Gaps could

point to a lack of resources or priority for CBM research in these regions; however, it is possible

that CBM is occurring in these regions, but do not engage with Indigenous communities

specifically, nor include research components to CBM, and thus may not be documented in

published journals. Nevertheless, climate change impacts on Indigenous food systems is a

global phenomenon (16), and this review highlights potential gaps where CBM could be further

developed and implemented.

63

Approximately one third of the reviewed articles provided gender-disaggregated data; this

research gap results in an incomplete understanding of how Indigenous women, men, and

gender-diverse people may differentially participate in, and experience CBM. We encourage

authors and journal editors to integrate assessment of gender into all manuscripts (65). Among

the articles that provided gender-disaggregated data, all articles highlighted the perspectives of

both women and men in the design of the monitoring system. When examining the

implementation of the monitoring system, articles generally emphasized participation of men

only or both men and women. The quality of participation or reasons for participation were

unclear due to lack of reporting in these articles; however, the predominant focus on men in

monitoring efforts could be due to the role of many Indigenous men in hunting, fishing, and

natural resource management in several contexts (84,87,90). Challenges to women’s

participation in, and benefit from, monitoring efforts could be due to failure to recognize and

address gendered power imbalances in project objectives or inadequate considerations of

gender in the program design (95,96). A better understanding of the gendered nature of CBM,

as well as the relationship between climate, food, and gender, are important for planning and

designing a CBM system that reflect gender equity. Critically, an examination of the underlying

social-cultural-political processes that determine differential gender exposure and sensitivity to

climate change and adaptive capacity, as well as gender equity in monitoring is recommended

(97).

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Considering the history of unethical research conducted on and not with Indigenous

communities (98,99), there is increasing demand for the recognition of Indigenous peoples’

contributions and knowledge in the context of research (100), including climate change research

(101,102). Prioritizing collaborative publications is an emerging avenue for acknowledging

Indigenous peoples’ contributions to research (103). While Indigenous peoples’ observations of

climate change are increasingly reported in the published literature (104), we found the inclusion

of Indigenous peoples as co-authors did not appear to follow the same trend. We found less

than half (42%) of reviewed articles on CBM had a co-author with an affiliation to an Indigenous

organization or community. If a monitoring system is community-led and community-based,

there is a need to consider whether co-authorship is appropriate, recognizing that some

community members may request not to be authors for a variety of reasons. Nevertheless, steps

need to be taken to avoid risks including tokenistic inclusion, implied support for findings, and

misappropriation of knowledge (103,105). Multiple evidence-based (MEB) approaches offer a

way forward for Indigenous and non-Indigenous collaborators to work together in developing

CBM systems that respects and reflects different contributions (106). MEB approaches view

Indigenous, local, and scientific knowledge systems as generating different manifestations of

knowledge, that when viewed as complementary, can generate new insights to support

decision-making and action (57). MEB approaches are recognized under the Convention for

Biodiversity as a way of ensuring equitable participation of diverse knowledge systems in

monitoring biodiversity targets (57), as well as the Intergovernmental Science-Policy Platform on

65

Biodiversity and Ecosystem Services to enhance understanding of governance of biodiversity

and ecosystems (107). The Paris Agreement article 7.5 also supports MEB approaches by

acknowledging adaptation action “should be based on and guided by the best available science

and, as appropriate, traditional knowledge, knowledge of indigenous [sic] peoples and local

knowledge systems, with a view to integrating adaptation into relevant socioeconomic and

environmental policies and actions, where appropriate” (97, p. 25).

Variations in the level of Indigenous community engagement in CBM were observed. Articles on

CBM of Indigenous food security were mostly classified as either collaborative monitoring (51%)

or externally driven monitoring (37%). This finding is consistent with a review of environmental

CBM in the Arctic region which found that 47% of systems involved community members in

collaboration while 30% involved community members in data collection only (51). The higher

number of articles describing collaborative monitoring could be explained by the broader trend

of engaging Indigenous communities in research and monitoring practices, whereas externally-

driven monitoring is likely influenced by conventional, government or researcher implemented

monitoring approaches (109), as well as requests by Indigenous communities for external

monitoring support (51,93). However, successful CBM generally occurs when communities

monitor things they personally connect with and care about, rather than for externally-driven

needs (110,111). Moreover, in the context of climate research, studies initiated with and by

Indigenous community members tend to indicate more responsible community engagement

than studies initiative by outside researchers alone (112). Community engagement is also

66

important for generating local ownership and understandings of environmental change, and to

facilitate the development of local climate change adaptation responses (113).

We reviewed the articles that described the implementation of CBM and found less than half of

these articles reported evaluation findings. The limited focus on evaluation could be explained

by challenges of evaluating climate change adaptation programs and policies including

assessing attribution, creating baselines, absence of measurable outcomes, and monitoring over

long time horizons (49,114). Climate change adaptation is also a relatively new field with little

consensus on what constitutes effective adaptation, and how the success of adaptation efforts

should best be measured (115). Nevertheless, in the context of CBM, it is important that

communities and researchers work together towards a consensus to ensure that CBM is

translated into responses to address climate change impacts and enhance food systems

resilience. Evaluations of CBM can also help identify monitoring gaps, inform governance

systems on monitoring progress, and justify continued support for CBM (116,117). Moreover, a

better understanding of CBM processes and outcomes can serve to develop an evidence base

that will inform future climate change adaptation efforts (118).

Only one formal autonomous monitoring scheme was reported in the published literature (81).

This finding is consistent with a recent review of environmental CBM approaches which found

no formal autonomous monitoring schemes (67). It is likely that monitoring is carried out

without documentation in the published literature, as many Indigenous communities often

67

monitor environmental changes and the health of their land (51). Further, communities

participating in monitoring may not be interested in research related to CBM nor publishing in

the literature, but instead interested in mobilizing CBM to support local decision-making (67).

There may also be challenges in understanding autonomous monitoring stemming from

disciplinary obstacles and difficulties describing and characterizing such systems (81,119).

Nevertheless, greater research attention to autonomous climate change monitoring and

adaptation – case studies outlining the process and outcomes of such activities – could provide

important insights to inform climate change adaptation strategies along with a strong

foundation for further documentation of CBM efforts (81).

Four pillars are often referred to when explaining the concept of food security: availability,

access, utilization, and stability (63). For most of articles on CBM of Indigenous food security

reviewed in this paper the specific pillar of food security was not explicitly mentioned, and food

stability was not mentioned at all. The absence of focus on specific food security pillars could be

due to articles focusing on proxies or indicators of food security (e.g., wildlife, climate change).

Moreover, the objectives of CBM may be to address conservation or natural resource

management goals rather than addressing food security challenges directly (50,89,90,120).

This finding highlights the need to clarify what is being assessed when food security is being

monitored (e.g., which food security pillar is being addressed), so that monitoring approaches

can be coordinated and allow comparisons to be made across studies and contexts. Where the

68

food security pillar was specified, we found that CBM typically focuses on food availability and

access, consistent with studies on impacts of climate change on food security (11,121). Less is

known about the role of climate change on food stability and utilization. Considering and

specifying broader determinants of food security in monitoring systems, together with climate

change indicators (e.g. seasonality, rain variability), could support more accurate, transparent,

and consistent monitoring of food system resilience to climate change.

Conventional food security monitoring tends to fail to probe for information that may be

relevant to Indigenous food security, such as the status of Indigenous food systems or

environmental change (2,36,37). This review found articles focused on food security themes that

extended beyond common metrics of food security (e.g. market foods, poverty) including

wildlife, natural resources, environmental change, and fisheries. However, not all aspects of food

security considered important to Indigenous peoples were captured in CBM systems such as

land and knowledge of local food practices (20,21). This review, then, begs the following

questions: who is CBM of Indigenous food security serving? Does a conventional definition of

food security (i.e. four pillars including availability, access, utilization, and stability) adequately

capture the dynamic nature of Indigenous food systems? If a conventional definition of food

security is used to guide the development of a CBM system with Indigenous communities, does

this definition lead to the creation of systems that overlook critical components of Indigenous

food systems? We encourage researchers to grapple with these questions when developing

food security monitoring systems with Indigenous communities. Where food security was

69

defined broadly, we argue that definitions and metrics should consider components highlighted

above that are important for Indigenous communities. Furthermore, given the diverse

Indigenous groups, food systems, and food practices, it is necessary to incorporate race,

ethnicity, and culture when exploring food security (122). Indeed, Indigenous food security can

be better understood by considering the social and economic benefits that Indigenous food

systems provide (123). The importance of monitoring Indigenous food security, and having an

inclusive definition of food security, is only increasing given the current and projected changes

in climate and its disproportionate impact on Indigenous food systems (34). Supporting

Indigenous communities in defining and monitoring food security, and linking monitoring

responses to decision-making and action, will be crucial for community-based adaptation.

Climate change was explicitly mentioned in more than half of the reviewed articles with climatic

indicators explored in only a few articles. The limited consideration of climatic indicators could

be explained by the lack of consensus on how food systems resilience to climate change should

be assessed (124,125). Food system resilience can be defined as the “capacity over time of a

food system and its units at multiple levels, to provide sufficient, appropriate and accessible

food to all, in the face of various and even unforeseen disturbances” (115, p. 19). Measuring

resilience in this context is challenging because the concept of food system resilience has not

been well defined for climate change (127) and the links between resilience of food systems and

climate change are not straight forward (124). Moreover, limited conceptual tools and

frameworks are available to guide such assessments (127,128). However, many Indigenous

70

communities have knowledge of climate and weather, and have developed adaptation strategies

for ensuring food security. For example, Indigenous knowledge systems such as sky and

astronomical observations, animal behaviours, and wind direction played a key role in

determining when farmers prepare the fields and the nature of crops they plant in a particular

season (129). As such, incorporating Indigenous knowledge in the design of food security and

climate change metrics could help improve our understanding of how climate change impacts

on food systems can be assessed over time.

Our review and synthesis highlight examples of how CBM is being used worldwide to address

food-related climate change impacts. The analysis of trends shows a growing interest in CBM

over time, with steady interest in considerations of climate change. The gaps identified in this

study might be useful for communities, researchers, and decision-makers in developing, refining,

or evaluating similar monitoring efforts. While our paper is comprehensive and systematic, we

note several important limitations. First, to examine research that has been conducted on CBM,

we included only published articles. We acknowledge that a substantial body of work may be

found in the grey literature (67). Analyzing the grey literature is recommended for future

research to better understand the full spectrum of CBM practice occurring within Indigenous

communities, especially of autonomous monitoring systems which may be investigated or

evaluated outside of research and the published literature. Secondly, the categorization of the

monitoring approach of articles, along with considerations of gender, were based on the

information presented in each article. We acknowledge the articles themselves may not fully

71

elaborate on the extent to which community engagement was considered. Greater elaboration

on these processes of community engagement in articles will benefit knowledge sharing among

Indigenous and scholarly communities. Finally, reporting and synthesizing evaluative findings

can provide further insights into the effectiveness, impact, and sustainability of CBM systems.

Overall, this study provides important insights into the trends and future directions in CBM of

Indigenous food security based on experiences from around the world and as reported in the

published literature.

2.16 Conclusion

The monitoring of food security with, for, and by Indigenous communities is a growing area of

research and practice. This trend follows the recent global trend of engaging Indigenous

communities, integrating diverse sources of knowledge, and addressing the disproportionate

food security and climate change challenges experienced by Indigenous communities. The

reviewed articles highlight the importance of considering indicators of wildlife and

environmental change in food security monitoring systems, considerations that are typically

excluded in conventional food security monitoring efforts. While many articles acknowledged

the impact of climate change on food security, few articles explicitly explored climatic indicators.

This finding is reflective of the limited understanding of how food systems resilience to climate

change should be assessed. We also found many examples of collaborative CBM but limited

examples of autonomous CBM. Exploring these trends highlight key research opportunities for

supporting monitoring and adaptation of food systems. First, we encourage articles to reflect

72

and report on the processes and outcomes of CBM. Furthermore, the development and

inclusion of food security and climate change metrics in CBM are also recommended. Finally, a

greater attention to autonomous monitoring and adaptation could help inform more effective

responses to climate change. When viewed as a whole, our findings provide an evidence-base of

research on CBM worldwide to address Indigenous food security challenges, serving as a

resource to inform future community-based adaptation efforts.

73

2.17 References

1. Watts N, Adger WN, Ayeb-Karlsson S, Bai Y, Byass P, Campbell-Lendrum D, et al. The

Lancet Countdown: tracking progress on health and climate change. Vol. 389, The Lancet.

2017. p. 1151–64.

2. World Food Programme. Food Security Monitoring System (FSMS) [Internet]. 2018.

Available from: https://www.wfp.org/food-security/assessments/food-security-

monitoring-system

3. Lake IR, Hooper L, Abdelhamid A, Bentham G, Boxall ABA, Draper A, et al. Climate change

and food security: Health impacts in developed countries. Environ Health Perspect.

2012;120(11):1520–6.

4. Wheeler T, von Braun J. Climate change impacts on global food security. Science.

2013;341(6145):508–13.

5. Tai APK, Martin MV, Heald CL. Threat to future global food security from climate change

and ozone air pollution. Nat Clim Chang. 2014;4(9):817–21.

6. Gbegbelegbe S, Chung U, Shiferaw B, Msangi S, Tesfaye K. Quantifying the impact of

weather extremes on global food security: A spatial bio-economic approach. Weather

Clim Extrem. 2014;4:96–108.

7. Devereux S. The impact of droughts and floods on food security and policy options to

alleviate negative effects. In: Agricultural Economics. 2007. p. 47–58.

8. Niles MT, Brown ME. A multi-country assessment of factors related to smallholder food

security in varying rainfall conditions. Sci Rep. 2017;7(1).

9. Myers SS, Smith MR, Guth S, Golden CD, Vaitla B, Mueller ND, et al. Climate Change and

Global Food Systems: Potential Impacts on Food Security and Undernutrition. Annu Rev

Public Health [Internet]. 2017;38(1):259–77. Available from:

http://www.annualreviews.org/doi/10.1146/annurev-publhealth-031816-044356

10. Chen CC, McCarl B, Chang CC. Climate change, sea level rise and rice: Global market

implications. Clim Change. 2012;110(3–4):543–60.

11. Schmidhuber J, Tubiello FN. Global food security under climate change. Proc Natl Acad

Sci U S A [Internet]. 2007;104(50):19703–8. Available from:

http://www.pnas.org/content/104/50/19703.short

74

12. Hales S, Kovats S, Lloyd S, Campbell-Lendrum D. Quantitative risk assessment of the

effects of climate change on selected causes of death , 2030s and 2050s [Internet]. Risk

Assessment. I.World Health Organization. 2014. Available from:

www.who.int/about/licensing/copyright_form/en/index.html%5Cnhttp://who.int/globalch

ange/publications/quantitative-risk-assessment/en/

13. Vermeulen SJ, Campbell BM, Ingram JSI. Climate Change and Food Systems. Annu Rev

Environ Resour [Internet]. 2012;37(1):195–222. Available from:

http://www.annualreviews.org/doi/10.1146/annurev-environ-020411-130608

14. Conevska A, Ford J, Lesnikowski A, Harper S. Adaptation financing for projects focused on

food systems through the UNFCCC. Clim Policy [Internet]. 2018;0(0):1–16. Available from:

https://doi.org/10.1080/14693062.2018.1466682

15. Dennig F, Budolfson MB, Fleurbaey M, Siebert A, Socolow RH. Inequality, climate impacts

on the future poor, and carbon prices. Proc Natl Acad Sci [Internet]. 2015;112(52):15827–

32. Available from: http://www.pnas.org/lookup/doi/10.1073/pnas.1513967112

16. FAO. Indigenous Peoples’ food systems & well-being: Interventions & polices for healthy

communities [Internet]. 2013. Available from:

http://www.fao.org/docrep/018/i3144e/i3144e.pdf

17. Ford JD. Indigenous health and climate change. Am J Public Health. 2012;102(7):1260–6.

18. Keleman Saxena A, Cadima Fuentes X, Gonzales Herbas R, Humphries DL. Indigenous

Food Systems and Climate Change: Impacts of Climatic Shifts on the Production and

Processing of Native and Traditional Crops in the Bolivian Andes. Front Public Heal

[Internet]. 2016;4. Available from:

http://journal.frontiersin.org/Article/10.3389/fpubh.2016.00020/abstract

19. FAO. INDIGENOUS PEOPLES’ FOOD SYSTEMS: the many dimensions of culture, diversity

and environment for nutrition and health. 2009; Available from:

ftp://ftp.fao.org/docrep/fao/012/i0370e/i0370e.pdf

20. Reading CL, Wein F. Health Inequalities and Social Determinants of Aboriginal Peoples’

Health. Natl Collab Cent Aborig Heal [Internet]. 2009;1–47. Available from:

http://www.nccah-ccnsa.ca/docs/social determinates/nccah-loppie-wien_report.pdf

21. Coté C. “Indigenizing” Food Sovereignty. Revitalizing Indigenous Food Practices and

Ecological Knowledges in Canada and the United States. Humanities [Internet].

2016;5(3):57. Available from: http://www.mdpi.com/2076-0787/5/3/57

75

22. Skinner K, Hanning RM, Desjardins E, Tsuji LJS. Giving voice to food insecurity in a remote

indigenous community in subarctic Ontario, Canada: Traditional ways, ways to cope, ways

forward. BMC Public Health. 2013;13(1).

23. Elliott B, Jayatilaka D, Brown C, Varley L, Corbett KK. “We are not being heard”: Aboriginal

perspectives on traditional foods access and food security. Vol. 2012, Journal of

Environmental and Public Health. 2012.

24. Richmond CAM, Ross NA. The determinants of First Nation and Inuit health: A critical

population health approach. Heal Place. 2009;15(2):403–11.

25. Lemke S, Delormier T. Indigenous Peoples’ food systems, nutrition, and gender:

Conceptual and methodological considerations. Matern Child Nutr. 2017;13.

26. Hoover E, Cook K, Plain R, Sanchez K, Waghiyi V, Miller P, et al. Indigenous Peoples of

North America : Environmental Exposures and Reproductive Justice. Environ Health

Perspect. 2015;120(12):1645–9.

27. Ford JD, Macdonald JP, Huet C, Statham S, MacRury A. Food policy in the Canadian North:

Is there a role for country food markets? Soc Sci Med. 2016;152:35–40.

28. Council of Canadian Academies. Aboriginal Food Security in Northern Canada: An

Assessment of the State of Knowledge. 2014. 296 p.

29. Jernigan VBB, Huyser KR, Valdes J, Simonds VW. Food Insecurity Among American Indians

and Alaska Natives: A National Profile Using the Current Population Survey–Food Security

Supplement. J Hunger Environ Nutr [Internet]. 2017;12(1):1–10. Available from:

https://www.tandfonline.com/doi/full/10.1080/19320248.2016.1227750

30. Patterson K, Berrang-Ford L, Lwasa S, Namanya DB, Ford J, Twebaze F, et al. Seasonal

variation of food security among the Batwa of Kanungu, Uganda. Public Health Nutr.

2017;20(1):1–11.

31. Barber M, Jackson S, Dambacher J, Finn M. The persistence of subsistence: Qualitative

social-ecological modeling of indigenous aquatic hunting and gathering in tropical

Australia. Ecol Soc. 2015;20(1).

32. Furgal C, Seguin J. Climate change, health, and vulnerability in Canadian northern

Aboriginal communities. Environ Health Perspect. 2006;114(12):1964–70.

33. Lynn K, Daigle J, Hoffman J, Lake F, Michelle N, Ranco D, et al. The impacts of climate

change on tribal traditional foods. Clim Change. 2013;120(3):545–56.

76

34. Furgal C, Seguin J. Climate change, health, and vulnerability in Canadian northern

Aboriginal communities. Environ Health Perspect. 2006;114(12):1964–70.

35. Beddington JR, Asaduzzaman M, Clark ME, Bremauntz AF, Guillou MD, Jahn MM, et al.

The role for scientists in tackling food insecurity and climate change. Agric Food Secur.

2012;1(1).

36. FAO, IFAD, WFP. Monitoring Food Security and Nutrition in Support of the 2030 Agenda

for Sustainable Development: Taking stock and looking ahead. Rome; 2016.

37. Babu SC. Evidence-Informed Policymaking: Lessons from Food Security and Nutrition

Monitoring Systems during Food Crises. In: Sahn DE, editor. The Fight Against Hunger

and Malnutrition: The Role of Food, Agriculture, and Targeted Policies. OUP Oxford; 2015.

38. World Health Organization. Food and nutrition surveillance systems: Technical guide for

the development of a food and nutrition surveillance system. WHO Geneva; 2013.

39. Canadian Polar Comission. State of Environmental Monitoring in Northern Canada

[Internet]. 2015. Available from: https://www.canada.ca/en/polar-

knowledge/publications/cpc-stateofenv.html

40. High Level Task Force on the Global Food Security Crisis. Updated Comprehensive

Framework for Action. 2010; Available from:

http://www.fao.org/fileadmin/user_upload/ISFP/UCFA_Final.pdf

41. Jones AD, Ngure FM, Pelto G, Young SL. What Are We Assessing When We Measure Food

Security? A Compendium and Review of Current Metrics. Adv Nutr An Int Rev J [Internet].

2013;4(5):481–505. Available from:

http://advances.nutrition.org/cgi/doi/10.3945/an.113.004119

42. Ford JD, Berrang-Ford L, King M, Furgal C. Vulnerability of Aboriginal health systems in

Canada to climate change. Glob Environ Chang [Internet]. 2010;20(4):668–80. Available

from: http://dx.doi.org/10.1016/j.gloenvcha.2010.05.003

43. Smylie J, Anderson I, Ratima M, Crengle S, Anderson M. Indigenous health performance

measurement systems in Canada, Australia, and New Zealand. Lancet.

2006;367(9527):2029–31.

44. Anderson MJ, Smylie JK. Health Systems Performance Measurement Systems in Canada:

How Well do They Perform in First Nations, Inuit, and Métis Contexts? Pimatisiwin

[Internet]. 2009;7(1):99–115. Available from:

http://www.ncbi.nlm.nih.gov/pubmed/23450984%5Cnhttp://www.pubmedcentral.nih.gov/

77

articlerender.fcgi?artid=PMC3582648

45. Bilukha O, Prudhon C, Moloney G, Hailey P, Doledec D. Measuring anthropometric

indicators through nutrition surveillance in humanitarian settings: Options, issues, and

ways forward. Food Nutr Bull. 2012;33(2):169–76.

46. Statistics NC for H. US Household Food Security Survey Module: Six-Item Short Form.

Security. 2008.

47. Bickel G, Nord M, Price C, Hamilton W, J. C. Guide to measuring household food security,

revised 2000. Alexandria, VA; 2000.

48. Ebi KL, Del Barrio MO. Lessons learned on health adaptation to climate variability and

change: Experiences across low- and middle-income countries. Vol. 125, Environmental

Health Perspectives. 2017.

49. Ford JD, Berrang-Ford L, Lesnikowski A, Barrera M, Jody Heymann S. How to track

adaptation to climate change: A typology of approaches for national-level application.

Ecol Soc. 2013;18(3).

50. Pollock RM, Whitelaw GS. Community-based monitoring in support of local sustainability.

Local Environ. 2005;10(3):211–28.

51. Johnson N, Behe C, Danielsen F, Nickels S, Pulsifer PL. Community-Based Monitoring and

Indigenous Knowledge in a Changing Arctic : [Internet]. Available from:

http://www.inuitcircumpolar.com/uploads/3/0/5/4/30542564/cbm_final_report.pdf

52. Kipp A, Cunsolo A, Gillis D, Sawatzky A, Harper S. The Need for Community-led,

Integrated, and Innovative Monitoring Programs when Responding to the Health Impacts

of Climate Change. Int J Circumpolar Health. 2018;

53. Danielsen F, Jensen AE, Alviola PA, Balete DS, Mendoza M, Tagtag A, et al. Does

monitoring matter? A quantitative assessment of management decisions from locally-

based monitoring of protected areas. Biodivers Conserv. 2005;14(11):2633–52.

54. Berner J, Brubaker M, Revitch B, Kreummel E, Tcheripanoff M, Bell J. Adaptation in Arctic

circumpolar communities: Food and water security in a changing climate. Int J

Circumpolar Health. 2016;75.

55. Danielsen F, Topp-Jørgensen E, Levermann N, Løvstrøm P, Schiøtz M, Enghoff M, et al.

Counting what counts: using local knowledge to improve Arctic resource management.

Polar Geogr. 2014;37(1):69–91.

78

56. Farhan Ferrari M, de Jong C, Belohrad VS. Community-based monitoring and information

systems (CBMIS) in the context of the Convention on Biological Diversity (CBD).

Biodiversity. 2015;16(2–3):57–67.

57. Tengö M, Hill R, Malmer P, Raymond CM, Spierenburg M, Danielsen F, et al. Weaving

knowledge systems in IPBES, CBD and beyond—lessons learned for sustainability. Vols.

26–27, Current Opinion in Environmental Sustainability. 2017. p. 17–25.

58. Johnson N, Alessa L, Behe C, Danielsen F, Gearheard S, Gofman-Wallingford V, et al. The

contributions of Community-Based monitoring and traditional knowledge to Arctic

observing networks: Reflections on the state of the field. Arctic. 2015;68(5):1–13.

59. Ebi K., Semenza JC. Community-based adaptation to the health impacts of climate

change. Vol. 35, Community-based adaptation to the health impacts of climate change.

2008. p. SP-501-7.

60. Berrang-Ford L, Pearce T, Ford JD. Systematic review approaches for climate change

adaptation research. Vol. 15, Regional Environmental Change. 2015. p. 755–69.

61. Landis JR, Koch GG. The measurement of observer agreement for categorical data.

Biometrics. 1977;33(1):159–74.

62. Levac D, Colquhoun H, O’Brien KK. Scoping studies: advancing the methodology.

Implement Sci. 2010;5:69.

63. FAO. The State of Food Insecurity in the World 2001. Rome; 2001.

64. Habtezion S. Gender, climate change and food security. New York, NY; 2012.

65. Heidari S, Babor TF, De Castro P, Tort S, Curno M. Sex and gender equity in research:

rationale for the SAGER guidelines and recommended use. Gaceta Sanitaria. 2018;

66. Braun V, Clarke V. Using thematic analysis in psychology Using thematic analysis in

psychology. Qual Res Psychol. 2006;3(2):77–101.

67. Kouril D, Furgal C, Whillans T. Trends and key elements in community-based monitoring:

a systematic review of the literature with an emphasis on Arctic and Subarctic regions.

Environ Rev [Internet]. 2016;24(2):151–63. Available from:

http://www.nrcresearchpress.com/doi/10.1139/er-2015-0041

68. Danielsen F, Burgess ND, Balmford A, Donald PF, Funder M, Jones JPG, et al. Local

participation in natural resource monitoring: A characterization of approaches. Conserv

79

Biol. 2009;23(1):31–42.

69. Bishop-Williams K, Sargeant JM, Berrang-Ford L, Edge V, IHACC Research Team, Harper

SL. A protocol for a systematic narrative synthesis review: The global impact of

environment on acute respiratory infections in Indigenous populations. BMC Syst Rev

[Internet]. 2017;In preparation. Available from: http://dx.doi.org/10.1186/s13643-016-

0399-x

70. Tremblay M, Furgal C, Larrivee C, Annanack T, Tookalook P, Qiisik M, et al. Climate

Change in Northern Quebec: Adaptation Strategies from Community-Based Research.

Arctic. 2008;61:27–34.

71. Constantino P de AICarlos HSA, Ramalho EE, Rostant L, Marinelli CE, Teles D, et al.

Empowering local people through community-based resource monitoring: A comparison

of Brazil and Namibia. Vol. 17, Ecology and Society. 2012.

72. Parlee BL, Goddard E, First Nation ŁKD, Smith M. Tracking Change: Traditional Knowledge

and Monitoring of Wildlife Health in Northern Canada. Hum Dimens Wildl. 2014;19(1):47–

61.

73. Setty RS, Bawa K, Ticktin T, Gowda CM. Evaluation of a participatory resource monitoring

system for nontimber forest products: The case of Amla (Phyllanthus spp.) fruit harvest by

Soligas in South India. Ecol Soc. 2008;13(2).

74. Wesche S, Schuster RC, Tobin P, Dickson C, Matthiessen D, Graupe S, et al. Community-

based health research led by the Vuntut Gwitchin First Nation. Int J Circumpolar Health

[Internet]. 2011;70(4):396–406. Available from:

https://www.tandfonline.com/doi/full/10.3402/ijch.v70i4.17846

75. Driscoll DL, Mitchell E, Barker R, Johnston JM, Renes S. Assessing the health effects of

climate change in Alaska with community-based surveillance. Clim Change. 2016;137(3–

4):455–66.

76. Driscoll DL, Sunbury T, Johnston J, Renes S. Initial findings from the implementation of a

community-based sentinel surveillance system to assess the health effects of climate

change in Alaska. Circumpolar Heal Suppl [Internet]. 2013;72:946–54. Available from:

http://10.0.13.74/ijch.v72i0.21405%5Cnhttp://search.ebscohost.com/login.aspx?direct=tru

e&AuthType=ip,url,cookie,uid&db=aph&AN=109175649&site=ehost-live&scope=site

77. McClymont Peace D, Myers E. Community-based participatory process--climate change

and health adaptation program for Northern First Nations and Inuit in Canada. Int J

Circumpolar Health. 2012;71(0):1–8.

80

78. Ens EJ, Towler GM, Daniels C. Looking back to move forward: Collaborative ecological

monitoring in remote Arnhem Land. Ecol Manag Restor. 2012;13(1):26–35.

79. Kofinas G, Lyver POB, Russell D, White R, Nelson A, Flanders N. Towards a protocol for

community monitoring of caribou body condition. Rangifer. 2003;Special Is:29–38.

80. Oviedo AFP, Bursztyn M. Community-based monitoring of small-scale fisheries with

digital devices in Brazilian Amazon. Fish Manag Ecol. 2017;24(4):320–9.

81. Sheil D, Boissière M, Beaudoin G. Unseen sentinels: local monitoring and control in

conservation’s blind spots. Ecol Soc [Internet]. 2015;20(2). Available from:

http://www.ecologyandsociety.org/vol20/iss2/art39/

82. Cummings A, Cummings G, Hamer E, Moses P, Norman Z, Captain V, et al. Developing a

UAV-Based Monitoring Program with Indigenous Peoples. J Unmanned Veh Syst.

2017;5(4):115–25.

83. Herrmann TM, Sandström P, Granqvist K, D’Astous N, Vannar J, Asselin H, et al. Effects of

mining on reindeer/caribou populations and indigenous livelihoods: Community-based

monitoring by Sami reindeer herders in Sweden and First Nations in Canada. Polar J.

2014;4(1):28–51.

84. Shaffer CA, Milstein MS, Yukuma C, Marawanaru E, Suse P. Sustainability and

comanagement of subsistence hunting in an indigenous reserve in Guyana. Conserv Biol.

2017;31(5):1119–31.

85. Van Vliet N, Sandrin F, Vanegas L, L’haridon L, Fa JE, Nasi R. High-tech participatory

monitoring in aid of adaptive hunting management in the Amazon. Unasylva.

2017;68(249):53–62.

86. Luzar JB, Silvius KM, Overman H, Giery ST, Read JM, Fragoso JM V. Large-scale

Environmental Monitoring by Indigenous Peoples. Bioscience [Internet]. 2011;61(10):771–

81. Available from: https://academic.oup.com/bioscience/article-

lookup/doi/10.1525/bio.2011.61.10.7

87. de Paula M, Xerente V, Pezzuti J. Hunting and monitoring: Community-based research in

xerente indigenous land, Brazilian Cerrado. Hum Ecol Rev [Internet]. 2017;23(1):23–44.

Available from: https://www.scopus.com/inward/record.uri?eid=2-s2.0-

85038815827&doi=10.22459%2FHER.23.01.2017.02&partnerID=40&md5=f35ffbb57e5cf9

6acc97f18422006b8f

88. Mateo-Vega J, Potvin C, Monteza J, Bacorizo J, Barrigón J, Barrigón R, et al. Full and

81

effective participation of indigenous peoples in forest monitoring for reducing emissions

from deforestation and forest degradation (REDD+): Trial in Panama’s Darién. Ecosphere.

2017;8(2).

89. Gill H, Lantz T. A Community-Based Approach to Mapping Gwich’in Observations of

Environmental Changes in the Lower Peel River Watershed, NT. J Ethnobiol [Internet].

2014;34(3):294–314. Available from: http://www.bioone.org/doi/abs/10.2993/0278-0771-

34.3.294

90. Constantino P de AL, Fortini LB, Kaxinawa FRS, Kaxinawa AM, Kaxinawa ES, Kaxinawa AP,

et al. Indigenous collaborative research for wildlife management in Amazonia: The case of

the Kaxinawá, Acre, Brazil. Biol Conserv. 2008;141(11):2718–29.

91. Brook RK, Kutz SJ, Veitch AM, Popko RA, Elkin BT, Guthrie G. Fostering community-based

wildlife health monitoring and research in the Canadian North. Ecohealth. 2009;6(2):266–

78.

92. Van Rijsoort J, Jinfeng Z. Participatory resource monitoring as a means for promoting

social change in Yunnan, China. Biodivers Conserv. 2005;14(11):2543–73.

93. Danielsen F, Pirhofer-Walzl K, Adrian TP, Kapijimpanga DR, Burgess ND, Jensen PM, et al.

Linking public participation in scientific research to the indicators and needs of

international environmental agreements. Conserv Lett. 2014;7(1):12–24.

94. Anisimov OA, Vaughan DG, Callaghan TV, Furgal C, Marchant H, Prowse TD, et al. Polar

regions (Arctic and Antarctic). In: Intergovernmental Panel on Climate Change Working

Group. 2007. p. 653–85.

95. Nordic Development Fund. Gender equality study: A study on addressing gender aspects

in projects co-financed by NDF in developing countries. Helsinki; 2004.

96. Fisher S. Tracking Adaptation and Measuring Development through a gender lens.

London, UK; 2014.

97. Bunce A, Ford J. How is adaptation, resilience, and vulnerability research engaging with

gender? Vol. 10, Environmental Research Letters. 2015.

98. Brant Castellano M. Ethics of Aboriginal Research.Pdf. J Aborig Heal. 2004;1(January):98–

114.

99. Smith LT. Decolonizing Methodologies. New York. 1999. 28-74 p.

82

100. Inuit Tapiriit Kanatami. National Inuit Strategy on Research [Internet]. 2018. Available

from: www.itk.ca

101. Ford JD, Cameron L, Rubis J, Maillet M, Nakashima D, Willox AC, et al. Including

indigenous knowledge and experience in IPCC assessment reports. Vol. 6, Nature Climate

Change. 2016. p. 349–53.

102. Ford JD, Vanderbilt W, Berrang-Ford L. Authorship in IPCC AR5 and its implications for

content: Climate change and Indigenous populations in WGII. Clim Change.

2012;113(2):201–13.

103. Castleden H, Morgan VS, Neimanis A. Researchers’ Perspectives on Collective/Community

Co-Authorship in Community-Based Participatory Indigenous Research. J Empir Res Hum

Res Ethics [Internet]. 2010;5(4):23–32. Available from:

http://journals.sagepub.com/doi/10.1525/jer.2010.5.4.23

104. Green D, Raygorodetsky G. Indigenous knowledge of a changing climate. Clim Change.

2010;100(2):239–42.

105. Castleden HE, Martin D, Cunsolo A, Harper S, Hart C, Sylvestre P, et al. Implementing

Indigenous and Western Knowledge Systems (Part 2): “You Have to Take a Backseat” and

Abandon the Arrogance of Expertise. Int Indig Policy J [Internet]. 2017;8`(4). Available

from: https://ir.lib.uwo.ca/iipj/vol8/iss4/8/

106. Gratani M, Royee F, Butler JRA. A research process and criteria indicators framework for

developing indigenous freshwater ecosystem health monitoring. Cogent Environ Sci

[Internet]. 2016;2(1):1–14. Available from:

https://www.cogentoa.com/article/10.1080/23311843.2016.1214228

107. Tengö M, Brondizio ES, Elmqvist T, Malmer P, Spierenburg M. Connecting diverse

knowledge systems for enhanced ecosystem governance: The multiple evidence base

approach. Vol. 43, Ambio. 2014. p. 579–91.

108. UNFCCC. Adoption of the Paris Agreement [Internet]. Paris; 2015. Available from:

http://www.un.org/ga/search/view_doc.asp?symbol=FCCC/CP/2015/L.9/Rev.1&Lang=E

109. Chandler M, See L, Copas K, Bonde AMZ, López BC, Danielsen F, et al. Contribution of

citizen science towards international biodiversity monitoring. Biol Conserv. 2017;213:280–

94.

110. Wiseman ND, Bardsley DK. Monitoring to Learn, Learning to Monitor: A Critical Analysis of

Opportunities for Indigenous Community-Based Monitoring of Environmental Change in

83

Australian Rangelands. Geogr Res. 2016;54(1):52–71.

111. Staddon SC, Nightingale A, Shrestha SK. The Social Nature of Participatory Ecological

Monitoring. Soc Nat Resour. 2014;27(9):899–914.

112. David-Chavez DM, Gavin MC. A global assessment of Indigenous community engagement

in climate research. Environ Res Lett. 2018;13:123005.

113. Bardsley D, Rogers G. Prioritizing Engagement for Sustainable Adaptation to Climate

Change: An Example from Natural Resource Management in South Australia. Soc Nat

Resour. 2011;24(1):1–17.

114. Fisher S, Dinshaw A, Mcgray H, Rai N, Schaar J. Evaluating Climate Change Adaptation:

Learning From Methods in International Development. New Dir Eval. 2015;2015(147):13–

35.

115. Hedger M, Greeley M, Leavy J. Evaluating Climate Change : Pro-Poor Perspectives. Inst

Dev Stud. 2012;39(4):75–80.

116. Brooks N, Anderson S, Ayers J, Burton I, Tellam I. Tracking adaptation and measuring

development [Internet]. Climate Change. 2011. Available from:

http://pubs.iied.org/pdfs/10031IIED.pdf

117. Ford JD, Berrang-Ford L. The 4Cs of adaptation tracking: consistency, comparability,

comprehensiveness, coherency. Vol. 21, Mitigation and Adaptation Strategies for Global

Change. 2016. p. 839–59.

118. Ford JD, Sherman M, Berrang-Ford L, Llanos A, Carcamo C, Harper S, et al. Preparing for

the health impacts of climate change in Indigenous communities: The role of community-

based adaptation. Glob Environ Chang. 2018;49.

119. Sheil D, Lawrence A. Tropical biologists, local people and conservation: New opportunities

for collaboration. Vol. 19, Trends in Ecology and Evolution. 2004. p. 634–8.

120. Constantino PAL. Dynamics of hunting territories and prey distribution in Amazonian

Indigenous Lands. Appl Geogr. 2015;56:222–31.

121. Campbell BM, Vermeulen SJ, Aggarwal PK, Corner-Dolloff C, Girvetz E, Loboguerrero AM,

et al. Reducing risks to food security from climate change. Glob Food Sec. 2016;11:0–1.

122. Skinner K, Pratley E, Burnett K. Eating in the City: A Review of the Literature on Food

Insecurity and Indigenous People Living in Urban Spaces. Societies [Internet]. 2016;6(2):7.

84

Available from: http://www.mdpi.com/2075-4698/6/2/7

123. Neufeld HT, Richmond CAM, Health Access Centre SOA. Impacts of place and social

spaces on traditional food systems in southwestern Ontario. Int J Indig Heal [Internet].

2017;12(1):93. Available from: https://journals.uvic.ca/index.php/ijih/article/view/16903

124. Douxchamps S, Debevec L, Giordano M, Barron J. Monitoring and evaluation of climate

resilience for agricultural development – A review of currently available tools. World Dev

Perspect. 2017;5:10–23.

125. Schipper ELF, Langston L. A comparative overview of resilience measurement frameworks

analysing indicators and approaches. Overseas Dev Inst - Work Pap 422 [Internet].

2015;(July):30. Available from:

www.odi.org%5Cnwww.odi.org/facebook%5Cnwww.odi.org/twitter

126. Tendall DM, Joerin J, Kopainsky B, Edwards P, Shreck A, Le QB, et al. Food system

resilience: Defining the concept. Vol. 6, Global Food Security. 2015. p. 17–23.

127. IISD. Climate Resilience and Food Security A framework for planning and monitoring.

2013;(June):29.

128. Sturgess P. Measuring Resilience. UK; 2016.

129. Ebhuoma EE, Simatele DM. “We know our Terrain”: indigenous knowledge preferred to

scientific systems of weather forecasting in the Delta State of Nigeria. Climate and

Development. 2005;1–12.

130. Smith LT. On tricky ground: Researching the native in the age of uncertainty. In: The SAGE

handbook of qualitative research. 3rd ed. Thousand Oaks, CA: Sage; 2005. p. 85–107.

131. IPCC. Summary for Policymakers. In: V. Masson-Delmotte, P. Zhai, H. O. Pörtner, D.

Roberts, J. Skea PRS, A. Pirani, W. Moufouma-Okia, C. Péan, R. Pidcock, S. Connors, J. B. R.

Matthews, Y. Chen, X. Zhou MIG, E. Lonnoy, T. Maycock, M. Tignor TW, editors. Global

warming of 15°C An IPCC Special Report on the impacts of global warming of 15°C above

pre-industrial levels and related global greenhouse gas emission pathways, in the context

of strengthening the global response to the threat of climate change,. Geneva,

Switzerland: World Meteorological Organization; 2018. p. 32.

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CHAPTER 3: HOW ARE CLIMATE ACTIONS EVALUATED? A REVIEW OF UNITED NATIONS FOOD SECURITY EVALUATIONS

Abstract

Established in Article 14 of the Paris Agreement, countries must evaluate progress toward

climate adaptation, mitigation, and financial goals via the 2023 global stocktake. Yet, the extent

of climate integration into evaluation in response to the rapidly approaching stocktake mandate

remains unclear. Many United Nations agencies recognize the importance of mainstreaming

climate action into food security and broader development programming. Our goal is to

examine how United Nations food security programs are evaluating climate action. Using a

systematic search and screening process, we included evaluations that described any aspect of

food security, evaluated completed programs, and were published between 2014 and 2019. We

examined the extent of climate change mainstreaming into food security evaluation by

developing and applying an assessment rubric. We also identified, compared, and characterized

evaluation challenges and opportunities using thematic analysis. Of the 136 relevant evaluations,

69% (n = 94) assessed food security programs that integrated climate action. While many

evaluations reported adaptation outcomes, considerations of climate action in the evaluation

approach were often insufficient. Based on our analysis, challenges to climate evaluation

included inadequate resource allocation, weak monitoring and evaluation systems, dependency

on food security evaluation, and limited climate focus in programs and evaluations. The

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assessment rubric provides a tool for understanding and encouraging climate change

integration into evaluation, and through this, helps countries prepare for the global stocktake.

3.1 Introduction

The Paris Agreement’s global goal on climate change adaptation (UNFCCC, 2015) raises a

fundamental question: How do we monitor and report on adaptation globally? The Agreement

has established that a global stocktake will be conducted in 2023, and every five years thereafter

to assess the collective progress in achieving the purpose of the Agreement (Article 14). To do

so, the global stocktake will consider “mitigation, adaptation, and the means of implementation

and support, and in the light of equity and the best available science” (UNFCCC, 2015, p. 18).

Although countries are asked to provide information on progress toward adaptation targets,

how countries track, monitor, and evaluate such progress is not prescribed by the Agreement.

The Agreement also does not provide a definition of adaptation, and continued debates about

the definition of adaptation create difficulties in monitoring and evaluating climate actions (i.e.

climate change mitigation and/or adaptation) (Tompkins et al., 2018). Furthermore, while

accepted methods to monitor migration progress exist (e.g. through national greenhouse gas

inventories), a comparable accepted method to document adaptation baselines does not yet

exist.

Assessing how people and countries are adapting is particularly important for programs aiming

to enhance food security (Conevska et al., 2019). Changes in temperature, increased extreme

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weather events, and increased rainfall variability are already threatening food production, food

access, food safety, food stability, nutrition, and environmental sustainability (Fujimori et al.,

2018; Mbow et al., 2019; Ray et al., 2019). Yet, evaluating the success of climate-resilient food

security programs is challenging due to trade-offs between mitigation, adaptation, and food

security (Denton et al., 2015; Sherman & Ford, 2014). For example, some forms of agricultural

intensification (e.g. monoculture systems) aiming to maintain supply under climate change may

also increase vulnerabilities to climate extremes (Mbow et al., 2019). Furthermore, standard food

security monitoring and evaluation (M&E) is typically not designed to track the resilience of

food systems, defined as “the capacity over time of a food system and its units at multiple levels,

to provide sufficient, appropriate and accessible food to all, in the face of various and even

unforeseen disturbances” (Tendall et al., 2015, p. 19). Similar challenges have been noted more

broadly for tracking climate change adaptation progress (Berrang-Ford et al., 2019; Ford et al.,

2013; Tompkins et al., 2018).

Navigating trade-offs between climate change mitigation, climate change adaptation, and food

security measures in programming require processes for learning from integrated climate and

food security efforts (Fisher et al., 2015; Mbow et al., 2019). Investing in climate change M&E is

important for learning from climate change adaptation efforts in support of food security and

help countries meet the reporting requirements of the Paris Agreement (FAO et al., 2018; Lam et

al., 2019; Uitto et al., 2016). Evaluators are increasingly recognizing the threat climate change

poses to sustainable development efforts and thus the need to consider climate change in

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evaluation (Rowe, 2019; Ssekamatte, 2018; Uitto 2019). Communities of practice have been

formed to foster evaluative thinking around climate (e.g. Earth-Eval) and food security (e.g.

EvalForward). However, there is a gap in conceptualizing the intersection of climate change and

food security in evaluation.

Because the climate crisis transcends national boundaries, intergovernmental organizations play

a key role in coordinating climate actions across countries. The United Nations (UN), for

example, promotes system-wide platforms for climate action (e.g. United Nations Framework

Convention on Climate Change; UNFCCC), food security (e.g. Committee on World Food

Security), and evaluation (e.g. United Nations Evaluation Group; UNEG). Many UN agencies have

recognized the importance of climate action mainstreaming, broadly referring to processes for

integrating climate change considerations into development policies, programs, and/or

individual actions (Somanathan et al., 2014; UNDP, 2011; USAID, 2015). The operationalization of

climate action mainstreaming, particularly adaptation, tends to be diverse, taking place across

levels (e.g. national, local) and sectors (e.g. environmental, risk reduction planning) (Runhaar et

al., 2018). Decisions surrounding the extent to which mainstreaming should be conducted is also

complex, and influenced by factors including the development policy objective, scale, and

duration. For example, a “development-first” approach that focuses on integrating climate

considerations into existing planning processes might be more appropriate for projects with a

short planning cycle (Kim et al., 2017); conversely, a “climate-first” approach focused on

comprehensive risk management of vulnerabilities to climate variability and change might be

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more appropriate for programs implemented across a longer time horizon. Learning from

practices and experiences documented in UN program evaluation reports may provide insights

into assessing and improving the climate-resilience of food security programs and evaluations.

Given the pressing global stocktake mandate, the impacts of climate change on food security

programming, and the climate responsibilities of UN agencies, this study asks: how are climate

actions evaluated in UN food security contexts? The objectives are: 1) to assess the extent to

which climate action is mainstreamed into UN food security evaluation reports including

variations across the food security topic (e.g. access, availability), climate change focus (e.g.

adaptation, mitigation), geographic region, and time; and, 2) to identify, compare, and

characterize the challenges and opportunities for evaluating climate action embedded within

food security programs.

3.2 Methods

3.2.1 Search strategy

We adopted a systematic evaluation approach to examine publicly available information on UN

food security evaluations. Specifically, we searched the UN Evaluation Group (UNEG) database

for evaluations using a systematic search and screening process (Colquhoun et al., 2014). The

UNEG database contains publicly available evaluation reports of its 47 UNEG members, totaling

over 10,000 reports (UNEG, 2016). UNEG members are encouraged to submit UN evaluations

into the database, and in doing so, support the use of evaluation reports beyond their primary

audience in the UN agencies that commissioned them. As UNEG members are encouraged to

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meet UNEG Norms and Standards5 for evaluation; this helps to ensure that a reasonable level of

quality and consistency among evaluation reports is achieved.

We searched the UNEG database using the term ‘food’. Evaluation reports that were completed

between 2014 and 2019 were selected. We selected reports published in the past six years to

allow for an in-depth analysis of present-day evaluations completed following the 2014

Intergovernmental Panel on Climate Change (IPCC) Fifth Assessment Report which called for

M&E strategies for managing climate impacts and reducing risks (Denton et al., 2015). To

capture UN evaluation reports that may not be indexed in the database, we used the same

database search protocol and searched the online evaluation repositories of UN entities selected

based on their membership in the High-Level Task Force on Global Food and Nutrition Security6.

Initial searches were conducted on 10 January 2019 and updated on 17 February 2020.

3.2.2 Relevance screening

A two-step screening strategy was employed. First, the titles and summaries of evaluation

reports were screened for relevance. Next, all reports deemed potentially relevant went through

a review of the full-text to confirm relevance. In each step, reports were screened according to a

5 UNEG has 14 norms (e.g. utility, credibility, independence) and five standards (e.g. institutional framework

management of the evaluation function, evaluation competencies) for evaluation. 6 UN entities searched included World Food Programme (WFP), Food and Agriculture Organization (FAO),

International Fund for Agricultural Development (IFAD), World Meteorological Organization (WMO), United Nations

Children’s Fund (UNICEF), United Nations Industrial Development Organization (UNIDO), International Labour

Organization (ILO), United Nations Environment Programme (UNEP), United Nations High Comissioner for Refugees

(UNHCR), and United Nations Development Programme (UNDP) (United Nations, 2015).

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priori inclusion criteria. Reports were included if they generally referred to a food security pillar7,

pillar synonym, or aspect of food security8. Moreover, only final evaluations were included to

ensure sufficient information was available for synthesis purposes; midterm evaluations, country

portfolio evaluations, evaluation summaries, monitoring exercises, and reviews were excluded.

All citations were imported into a spreadsheet (Excel 2013, Microsoft Corporation, Redmond,

WA). To ensure rigour and reduce bias in the screening process, all screening steps were

conducted by two independent reviewers; any conflicts were discussed and reconciled regularly

throughout the review process. The level of reviewer agreement was measured using a kappa

score (McHugh, 2012).

3.2.3 Data extraction, classification, and analysis

A charting form was developed to collect key characteristics of each evaluation report including

the year of evaluation completion, UN entity, budget, evaluation methodology, and program

budget, scale, duration, and geographic region.

We classified evaluation reports into different categories of pathways toward food security

based on program descriptions and outcomes (Table 3.1). We developed these categories of

pathways by an inductive thematic analysis of evaluation reports captured in this review (Table

7 Four pillars are commonly referred to when explaining the concept of food security: availability, access, utilization,

and stability (FAO, 2001). 8 Food security is defined as “a situation that exists when all people, at all times, have physical, social and economic

access to sufficient, safe and nutritious food that meets their dietary needs and food preferences for an active and

healthy life” (FAO, 2001, p. 49).

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1). We also classified evaluation reports into one of six climate change categories based on

program descriptions and outcomes. Climate change categories were adapted from the five

climate change categories developed by Donner et al. (2016) by replacing “interdeterminate

based on the information available in the database” with “climate-change impacts,” as well as

adding “both adaptation and mitigation”. Because climate change has multi-faceted and

temporal impacts on all dimensions of food security, articles discussing food security pathways

such as food production, food access, and infrastructure could be categorized as having used

climate action measures. The urgency of climate change might place a focus of climate change

in food security programs. For example, against the backdrop of Myanmar’s vulnerability to

climate-related hazards (e.g. flash floods, drought, and erratic rainfall), a food assistance

program aimed to improve the preparedness for and mitigation of disasters and climate change

(WFP, 2016). The program prioritized emergency relief (e.g. cash, food) and asset creation (e.g.

soil conservation, watershed management) in disaster-prone areas.

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Table 3.1. Food security and climate change classification system applied to United Nations

evaluation reports.

Categories Description of pathways or actions

Food security*

Food production Pathway that directly supports food production and productivity, such as the

provision of seeds, fertilizer, and land.

Food access Pathway that meets immediate food needs, such as school feeding, food

assistance, and food relief programs.

Infrastructure Pathway to improve infrastructure including roads, flood management,

irrigation, and/or storage facilities.

Market-based Pathway that enhances markets for farmers, link consumers to markets, provide

access to financial services, and/or support business development.

Capacity building Pathway that trains extension workers, farmers, researchers, and policymakers in

food production and/or managing risks to food security.

Food security

monitoring system

Pathway to track the food security situation on an ongoing basis over time.

Nutrition Pathway addressing malnutrition, including overnutrition, undernutrition, and

associated conditions such as stunting.

Climate change

Explicit adaptation Actions to reduce vulnerability to the effects of climate change. To be

considered under this category, the report had to explicitly mention

“adaptation.”

Implicit adaptation A wide range of actions that can reduce societal vulnerability to external

stresses like climate events (e.g. disaster preparedness), or adapt to a particular

range of projected climate outcomes (e.g. coastal protective measures).

Evaluations categorized as ‘implicit’ adaptation generally described, but did not

explicitly mention, adaptation.

Mitigation Actions taken to reduce greenhouse gas emissions or greenhouse gas

concentrations.

Both adaptation and

mitigation

Actions taken to adapt to (explicitly or implicitly) and mitigate climate change.

Climate change

impacts

Actions to capture how climate change is affecting food security and/or the

programming context without referencing adaptation or mitigation.

Climate absent The climate change relevance of the program was not articulated.

* Categories are not mutually exclusive and do overlap; for example, programs aiming to improve food

access can relate to nutrition by focusing on access to nutritious foods.

We examined the extent to which climate change was integrated into evaluations using an

assessment rubric (Table 3.2). The rubric was intended to provide a high-level assessment of

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climate action considerations. The rubric could be modified to capture greater detail, depending

on the needs and goals of the assessment. For example, the rating scale in evaluation scope

(question b) could have a maximum score of three to account for studies mentioning all three

climate change considerations (e.g. adaptation, mitigation, impact). We developed the rubric

based on a series of questions organized around three general components of evaluation:

• Evaluation scope: using a two-point (0-2) rating scale, we assessed climate change

considerations in the evaluation report introduction and questions. We assessed how the

evaluation report described the context of climate risks, vulnerabilities, and impacts.

Furthermore, we assessed whether the report described how climate change might

impact (or be impacted by) the program.

• Evaluation approach: using a one-point (0-1) rating scale, we assessed whether climate

change was mentioned in the evaluation theory, methodology, methods, and data

analysis, as well as whether the report described how it intended to assess the context-

specific climate change challenges. We used lower weighting for the evaluation

approach considering frameworks for evaluating outcomes of climate action only

recently emerged (Uitto et al., 2016).

• Evaluation results: using a three-point (0-3) rating scale, we assessed climate change

considerations in the evaluation findings, conclusions, and recommendations. We

assessed whether the reports demonstrated a link between the identified climate change

risks, vulnerabilities, and impacts and the program activities, outcomes, and impacts.

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A climate action integration index was then developed and calculated by summing scores for

component indices using equal weighting to reflect the equal importance of each component in

the evaluation framework (Lamhauge et al. 2012). This index was calculated on a six-point scale,

building on similar evaluation methodologies in the climate change field (Bunce & Ford, 2015;

Sherman & Ford, 2014). Based on this six-point scale, we categorized the 94 reports (69% of all

evaluations) integrating climate action as having high, moderate, or low levels of climate change

considerations in evaluation. To be classified as high level, reports had to score between five to

six points; moderate levels scored between three to four points; and low levels scored between

one and two points. We used descriptive statistics to present the characteristics of evaluations

and examine the extent to which climate action was integrated into evaluation.

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Table 3.2. Assessment rubric for climate action integration into United Nations evaluation

reports.

Criteria and guiding questions Scoring system

Evaluation scope Total possible score: 2

a. Does the introduction of the evaluation acknowledge a climate change

issue(s)?

Yes: score of 1

No: score of 0

b. Does the evaluation include an objective/question/criterion specific to

the assessment of climate change adaptation, mitigation, and/or impacts?

Yes: score of 1

No: score of 0

Evaluation approach Total possible score: 1

a. Is climate change adaptation, mitigation, and/or impacts mentioned in

the evaluation theory, methodology, methods, and/or analysis?

Yes: score of 1

No: score of 0

Evaluation results Total possible score: 3

a. Does the findings section provide information on climate change

adaptation, mitigation, and/or impacts?

Yes: score of 1

No: score of 0

b. Does the conclusion provide information on climate change adaptation,

mitigation, and/or impacts?

Yes: score of 1

No: score of 0

c. Are there specific recommendations to address climate change

adaptation, mitigation, and/or impacts?

Yes: score of 1

No: score of 0

3.2.4 Thematic analysis: examining evaluation challenges and opportunities

We used a hybrid deductive-inductive approach (Fereday & Muir-Cochrane, 2006) to conduct

thematic analysis (Braun et al., 2018). Thematic analysis involved identifying patterns or themes

in evaluation reports that captured challenges and opportunities for evaluating climate action in

food security programs. We deductively coded segments of text using an analytical tool that we

developed (Appendix 4). In this tool, we defined the following three themes: context, approach,

and opportunities/challenges. These themes were derived from literature on M&E of climate

action and food security (Bours et al., 2014; Fisher et al., 2015; Ford et al., 2013). During this

initial stage, further themes were inductively developed to accommodate data that could not be

coded into one of the predetermined themes. To ensure validity, weekly discussions among

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team members (SL, WD, SLH) were held to co-develop, define, expand, collapse, and finalize the

themes. The final codebook, comprising all codes along with their descriptions and examples,

was applied to all the evaluation reports (Appendix 5 and 6). To better understand the

relationship between themes of climate-responsive evaluation challenges and opportunities, we

developed a thematic map (Appendix 7). NVivo© qualitative analysis software was used to

facilitate the coding of text segments, development of themes, and organization of quotations

(QSR International, Version 12).

3.3 Results

After the removal of duplicates and non-relevant reports, and the addition of reports from the

targeted search of UN websites, a total of 133 relevant reports were identified (Appendix 8).

Several reports documented more than one evaluation study, resulting in 136 unique

evaluations that were reviewed in this paper (Figure 3.1). The kappa inter-rater reliability score

for the title/summary screening was 0.70, indicating “good agreement” (McHugh, 2012). A

summary of the descriptive characteristics of these evaluations is shown in Table 3.3.

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Figure 3.1. Flow chart illustrating the selection of United Nations food security evaluations (n =

136 unique evaluations within 133 reports) published from 2014 to 2019.

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Table 3.3. Descriptive characteristics of United Nations food security evaluations (n = 136

evaluations) published from 2014 to 2019.

Characteristics No. %

Year of publication:

2014 23 16.9

2015 13 9.6

2016 27 19.9

2017 27 19.9

2018 29 21.3

2019 17 12.5

Geographic region: a

Africa 71 52.2

Asia 61 44.9

North America 8 5.9

South America 7 5.1

Europe 3 2.2

Australia and Oceania 3 2.2

Programming scale:

National 79 58.1

Provincial/regional 33 24.3

Local 24 17.6

United Nations agency:

Food and Agriculture Organization 44 32.4

International Fund for Agricultural Development 41 30.1

World Food Programme 27 19.8

United Nations Children’s Fund 11 8.1

United Nations Development Programme 9 6.6

United Nations Environment Programme 4 2.9

Evaluation methodology:

Qualitative 90 66.2

Mixed qualitative and quantitative 45 33.1

Quantitative 1 0.7

Food security pathway:

Capacity building 136 100

Food production 86 63.2

Nutrition 42 30.9

Market access 41 30.1

Infrastructure 32 16.9

Food access 23 16.9

Information systems 17 12.5

Climate change focus:

Implicit adaptation 46 33.8

Climate absent 42 30.9

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Explicit adaptation 24 17.6

Climate change impacts 16 11.8

Both adaptation and mitigation 7 5.1

Mitigation 1 0.7 a Numbers may not sum to 136 as some evaluations were conducted across multiple geographic regions.

3.3.1 Climate action mainstreaming into food security evaluation

From 2014 to 2019, six UN agencies published evaluations of completed food security

programs. In general, evaluations were conducted for accountability (i.e. assessing performance

and results of the operation) and learning (i.e. identifying the reasons why certain results

occurred) purposes. The average budget of programs was 36.8 million USD (range: 0.7 – 435

million USD) and the median duration was four years (range: 1 – 24 years). Programs were

conducted in 83 countries, primarily in African and Asian regions. Most UN food security

evaluations (69%; n = 94) integrated climate action with no clear trend over time (Figure 3.2).

Among the evaluations that integrated climate action, most focused primarily on adaptation

either implicitly (34%; n = 46) or explicitly (18%, n = 24). The proportion of evaluations focused

on implicit adaptation and climate change impacts increased over time while explicit adaptation

and mitigation decreased (Figure 3.3). The proportion of evaluations focused on both

adaptation and mitigation increased until 2019, when the proportion dropped back down to

2014 levels.

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Figure 3.2. Number of United Nations food security evaluations (n = 136) with a climate focus

published from 2014 to 2019.

0

10

20

30

40

50

60

70

80

90

2014 2015 2016 2017 2018 2019

Num

ber

of

eval

uat

ions

Year

Climate present Climate absent

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Figure 3.3. Proportion of United Nations food security evaluations from 2014 to 2019 focused

on implicit adaptation (a), explicit adaptation (b), mitigation (c), both adaptation and mitigation

(d), and climate change impacts (e).

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3.3.2 Climate considerations in food security evaluation was superficial

Within food security pathways, programs most likely to score medium or high climate action

integration were those focused on improving food access, followed by market access,

infrastructure, food productivity, capacity building, information systems, and nutrition. In terms

of climate change foci, programs focused on mitigation were more likely to score medium or

high climate action integration followed by both adaptation and mitigation, explicit adaptation,

implicit adaptation, climate change impacts, and climate absent. The median duration of

programs with a mitigation component was five years which is slightly higher than the median

program duration of four years, suggesting mitigation might be more relevant in programs with

longer time horizons. Geographically, programs most often scoring medium or high climate

action integration were those conducted in North America, followed by South America,

Australia/Oceania, Africa, Asia, and Europe.

Of the evaluations that considered climate action, the integration of climate differed within

components of an evaluation (Appendix 9). For example, one-quarter of evaluations (25%, n =

34) scored highest for the results component of the assessment tool by reporting climate-

related findings, conclusions, and recommendations. However, most evaluation studies did not

account for climate action in the evaluation scope or approach. For instance, 126 evaluations

(93%) did not elaborate on how climate action was evaluated. Over 66% (n = 90) of evaluations

were classified as low level of climate action integration, followed by 24% (n=32) as medium

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integration, and 10% (n=14) as high integration. There was a slight decrease in low and high

climate integration with a slight increase in medium climate integration over the six years (2014-

2019) (Figure 3.4).

Figure 3.4. Extent of climate action integration into United Nations food security evaluations

from 2014 to 2019.

3.3.3 High scoring food security evaluations integrated climate considerations into the evaluation scope, approach, and results

The extent of climate action integration in UN evaluations differed by UN agency, with UNDP

scoring highest on average (3.3/6), followed by WFP (2.4), FAO (2.3/6), IFAD (1.9/6), UNEP

(1.25/6), and UNICEF (0.7/6). The different climate action mandates of UN agencies (Appendix

10) could help explain the varying extents of climate action integration in UN evaluations. For

0

10

20

30

40

50

60

70

80

90

100

2014 2015 2016 2017 2018 2019

Pro

po

rtio

n o

f ev

aluat

ions

(%)

Year

Low climate action integration Medium climate action integration High climate action integration

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example, UNICEF aims to integrate environmental sustainability as a cross-cutting issue without

specifying climate action. In contrast, UNDP ensures all its programming considers climate and

disaster risk. As such, explicit commitments to mainstream climate action into all programs

could contribute to higher average climate action integration scores.

There does not appear to be a clear relationship between median program duration and

average climate change integration score of individual UN agencies (Appendix 11). The median

program duration across all levels of climate action integration was four years, suggesting no

relationship between the different levels of integration and program durations. Articles

published between 2017 and 2019 tended to have slightly higher average climate change

integration scores (2.7) compared to those published between 2014 and 2016 (2.5), suggesting

an increase in climate change integration over time.

Except for UNICEF, all UN agencies had at least one report scoring high in climate action

integration. For example, one UNDP evaluation report covering a resilience capacity building

program in the Democratic Republic of the Congo described the risks of climate change to food

security, conducted a literature review focused on climate change, and reported changes to

climate resilience of food production systems (UNDP, 2015). In a WFP evaluation report covering

a relief and recovery program in Zimbabwe, the context introduced the impacts of climate

change on agricultural production and evaluation questions examined evidence that

interventions were designed to address unpredictable drought (WFP, 2014g). Promising climate

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evaluations included a climate risk assessment, an explicit strategy for measuring climate action

outcomes, and a dedicated overview of climate action outcomes, while climate-absent

evaluations did not mention climate in the context or methods (Appendix 12). A key finding of

our study was a weakness in climate assessment methodologies, casting doubt on the

robustness of the climate-related outcomes presented.

3.3.4 Low scoring food security evaluations integrated climate considerations into the evaluation results only

All UN agencies had at least one evaluation scoring in both the medium and low categories in

climate action integration. Evaluations scoring medium often reported risks posed by climate

change to the program and presented results related to climate change; however, they tended

not to elaborate on the climate assessment methodology. For example, one evaluation report

described Guatemala’s climate vulnerability and context and assessed changes in resilience to

climate hazards from a food-for-assets program; however, the report did not describe the

methodological approach for linking adaptation results with adaptation efforts (WFP, 2014a).

Low scoring evaluations generally either: 1) reported risks climate change posed to the program

without presenting climate-related findings, or 2) presented climate-related findings without

providing an overview of how climate change influenced the program context. Like medium

scoring evaluations, low scoring evaluations did not elaborate on how climate action was

assessed.

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3.3.5 Challenges and opportunities for evaluating climate action

Evaluations across all UN agencies reported challenges of existing M&E systems and

implications of these challenges on evaluation resources, food security assessment, and climate

action assessment (Figure 3.5 and Supplementary file Figure 1). M&E systems were often

reported as “weak,” “underperforming,” or “unsatisfactory” (FAO, 2016; IFAD, 2014b, 2015b),

resulting in the “absence of a well-articulated theory of change,” “lack of outcome and even

output level data,” or “poor selection of indicators” (IFAD, 2016b, 2017c, 2018a). Without a clear

theory of change, for example, it was difficult to accurately assess the impact pathways leading

to adaptation and food security results (UNEP, 2016). When data were available, in many cases

they were “inconsistent” or “poor” to meaningfully inform evaluative judgments on the success

of food security programs (FAO, 2017b; WFP, 2016).

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Figure 3.5. Challenges and opportunities for assessing climate action as reported in United

Nations food security evaluations from 2014 to 2019.

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Challenge 1: Weak M&E systems with implications for climate evaluation

According to evaluations, a weak M&E system often did not allow changes to climate resilience

to be measured or attributed to the food security program (WFP, 2014c, p. 43). Typically, food

security indicators such as food consumption, dietary diversity, and coping strategies were

collected without taking into account “the occasional contextual events that may have affected

the regularity of the interventions or the households’ food security (i.e. floods)” (WFP, 2018, p.

26). Furthermore, the absence of “well-defined,” “quantifiable,” and “operational” indicators

(IFAD, 2016c, 2018a, 2018d) often prevented climate-related assessments. For example, one

evaluation assessing an agricultural greenhouse gas mitigation program across six countries

(South Africa, Indonesia, Columbia, Ecuador, Costa Rica, and the Democratic Republic of the

Congo) reported, “Through the information that the Evaluation Team gathered, it is not known if

the training was delivered effectively and that it strengthened the capacity of national compilers

to gather and analyze climate change data” (FAO, 2014b, p. 16). This quotation underscores the

importance of designing climate adaptation and mitigation indicators to capture climate-related

outcomes of food security programs.

Challenge 2: Inadequate resources for climate evaluation

Because evaluation often draws on existing data from M&E systems, the quality of an evaluation

can depend on the quality of M&E systems. As one evaluation report covering a livestock

development program in Laos explained, “The joint evaluation faced a number of challenges in

the assessment of both effectiveness and rural poverty impact which were mainly due to the

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weaknesses of project-level M&E system” (IFAD, 2018a, p. 6), highlighting the role of M&E

systems in facilitating evaluation. Including climate action in the evaluation scope was also

constrained by limited resources such as human, capacity, time, funding, and logistics (FAO,

2017c; WFP, 2018). In low resource contexts, extreme weather events posed further challenges

to the evaluation process. For example, one evaluation report describing a relief and recovery

program highlighted:

It needs to be mentioned that Madagascar is not only a large country but also that it is

highly complex, with difficult political conditions, security constraints, an enormous agro-

ecological variety, and both quick-onset (cyclones) and slow-onset (droughts, harvest

failure due to locusts) disasters (WFP, 2014d, p. 2, emphasis added).

Challenge 3: Limited food security programming focused on climate action

When climate action was not an objective of the food security program, climate action was often

overlooked in the M&E stage. The lack of climate action in food security programming

contributed to limited climate-related activities, outputs, and outcomes to support evaluative

judgement. As one evaluation report covering a program in Vietnam explained, “There was also

no indication of contribution to climate change adaptation over the life of the Pro-Poor

Partnerships for Agroforestry Development (3PAD) project, even if the awareness and reporting

on severe weather events and the negative effects on crops and livestock increased over the

3PAD project lifetime” (IFAD, 2018b, p. 32). As such, an evaluation will not uncover meaningful

climate-related outcomes without climate action being integrated into the program. Several

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evaluations reported avoiding assessing climate action entirely, demonstrating a broader

implication of a lack of climate action integration in programming. For example, one evaluation

reporting on a livestock development program in Laos stated,

This [adaptation] evaluation criterion concerns the contribution of the project to increase

climate resilience and beneficiaries’ capacity to manage short- and long-term climate

risks. The project did not specifically contribute to this objective. As a consequence, this

criterion is not rated (IFAD, 2018a, p. 36).

Challenge 4: Dependency on food security evaluation

In several evaluations, extreme weather events linked to climate change impacted food security

evaluation. In Algeria, endline surveys were delayed “to avoid biased outcomes” due to the

impact of unexpected, flash floods “on key determinants of malnutrition” (WFP, 2018b, p. 29),

highlighting the influence of severe floods on food security measurement tools. Some climate

evaluations were also influenced by the multi-faceted nature of food security programs. For

example, in a multi-sectoral project with multiple interventions that aimed to promote the use of

sustainable land management across 17 countries, attributing progress in sustainable

agriculture, biodiversity conservation, and climate change adaptation to any one particular

intervention was reported to be challenging (UNEP, 2015). Furthermore, food security evaluation

was often constrained by the “absence of monitoring data”, “the issue of attribution”, and “food

security and agricultural production not [being] the explicit focuses of the program” (IFAD,

2016a, 2017b; WFP, 2014b), posing challenges to climate evaluation. Climate action was difficult

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to assess when data surrounding indicators (e.g. changes to food security status) were not

adequately captured.

Opportunity 1: Build a foundation for climate evaluation by investing in M&E systems

Many evaluations emphasized the importance of building a strong M&E foundation by

strengthening capacity, specifically analytical, project management, and M&E skills (IFAD, 2015a,

2017a; UNICEF, 2018); these foundational skills lay the groundwork for evaluations to integrate

climate change considerations. Some evaluations also suggested M&E systems focus on

adaptation outcomes (e.g. reducing food insecurity) over outputs and activities (e.g. number of

trainings held) to capture observed changes to adaptive capacity (FAO, 2014a). To invest in M&E

systems, reports recommended to budget for an explicit climate change evaluation criterion in

the evaluation design (FAO, 2018c) and to allocate funds to evaluations generally (IFAD, 2019).

Opportunity 2: Prioritize climate action in food security evaluation

Although a program may not have explicitly included climate change adaptation in the program

design, some activities may have contributed to climate change adaptation (IFAD, 2018c, p. 24).

An evaluation of a rural development program in Morocco reported, “Nothing was specifically

done to improve resilience to climate change” (IFAD, 2014c, p. 19). The authors added, “it is

likely that the activities to protect natural resources, especially water, soil and vegetation cover,

directly or indirectly contributed to resilience” (IFAD, 2014c, p. 19), highlighting the promise of

climate evaluation in capturing climate co-benefits. In an evaluation of an agroforestry

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development project, the report identified climate action trade-offs, stating, “Climate change

adaptation is rated less positively: attention was focused on climate change mitigation through

the forestry sector, not climate change adaptation to improve the resilience of poor farmers and

communities” (IFAD, 2018d, p. 33). While some UN agencies have developed approaches for

measuring resilience (e.g. WFP 2014d), evaluation reports generally considered climate action as

a cross-cutting theme or stand-alone evaluation question. Furthermore, they often assessed the

ways the program was aligned with climate-related frameworks, policies, or strategies including

the Sustainable Development Goal 13 (climate action) (FAO, 2018b), national climate change

strategies (FAO, 2018c; IFAD, 2018c; WFP, 2014c), UN Development Assistance Frameworks

(UNDP, 2016; WFP, 2014d), UN country strategies (FAO, 2018a; IFAD, 2018c; UNEP, 2015; WFP,

2014f), and the UNFCCC (FAO, 2017a).

Opportunity 3: Prioritize climate action in food security programming

All UN agencies explored in this study had at least one evaluation emphasizing the importance

of integrating climate action into food security programming. In the context of a relief and

recovery program in Zimbabwe, increasing focus on resilience programming has been

recommended despite “a perception… that this kind of programming is somewhat outside

WFP’s core mandate” (WFP, 2014c, p. 48). Several evaluations also highlighted the need to

integrate climate into program theory. For example, one report covering a program in Kenya

recommended “a more robust design process that sets out an appropriate long-term theory of

change for target communities” (WFP, 2014c, p. 47), emphasizing the importance of showing the

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theory behind how the program will contribute to the overall goal of food security resilience to

climate change.

3.4 Discussion

The rapidly approaching 2023 global climate change stocktake makes it important to clarify the

ways of assessing progress toward collective climate change goals. Considering the support of

many UN agencies in climate action mainstreaming into food security and development

planning, this paper systematically examines UN food security program evaluation reports.

While many evaluations focused on climate change adaptation programs, few assessed

programs focused on mitigation, which is a missed opportunity considering agriculture, forestry,

and other types of land use account for 23% of human greenhouse gas emissions (Mbow et al.,

2019). Importantly, evaluations with a mitigation focus were more likely to score medium to

high climate action integration. Both mitigation and adaptation – as well as the mitigation-

adaptation nexus – are critical for achieving food security (Babiker et al., 2018; Richardson et al.,

2018).

Although changing, the extent of climate action integration into food security evaluation

remained low over the six years. Progress toward climate action mainstreaming into evaluation

is slow despite global calls (e.g. the Paris Agreement, the Sendai Framework for Disaster Risk

Reduction, the 2030 Agenda for Sustainable Development) for international cooperation on

adaptation and mainstreaming of climate action into development planning. While many

evaluations integrated climate action into the evaluation findings, conclusions, and

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recommendations, the methodological dimensions were often neglected, thus preventing

thorough considerations of climate action in evaluation data collection and analysis. Our

assessment rubric offers a tool to illuminate the extent of climate action mainstreaming into

food security evaluation and the possibilities in applying climate action mainstreaming to help

countries prepare for the global adaptation stocktake.

Mandating the assessment of program contributions to climate resilience was encouraged by

many evaluations, highlighting opportunities to integrate climate action into the evaluation

scope. For example, IFAD defined a new adaptation criterion in an updated evaluation manual

as: “The contribution of the project to reducing the negative impacts of climate change through

dedicated adaptation or risk reduction measures” (IFAD, 2016d, p. 38). IFAD also offered core

questions to guide the evaluation such as: “To what extent did the program demonstrate

awareness and analysis of current risks?” (pg. 42). Commonly used criteria for evaluating climate

policy included goal achievement, efficiency, and cost-effectiveness (Huitema et al., 2011). IFAD

was the first to mandate an explicit criterion, paving a way forward for encouraging climate

evaluation of all programs. As investments in preparing for climate change increase, developing

and applying quality assurance systems can help support climate-responsiveness of evaluation

(Carbon, 2017).

While our 6-question assessment tool did not specify the collection of qualitative data, we found

the qualitative analysis of evaluation challenges and opportunities to be useful for

contextualizing assessment findings. We recommend having a comments section beside the

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scoring section to accommodate the extraction of relevant qualitative information, helping to

explain why a particular rating was given. Furthermore, the tool did not specify the collection of

quantitative data. Additional information related to the program, such as duration, is important

to support the analysis of the scoring. Our assessment also covered UN evaluation reports

conducted over the past six years, which was a time-intensive undertaking. However, this

approach does not require primary data collection and makes effective use of evaluation data

already systematically collected by UN agencies. Practitioners might consider applying this tool

on a more periodic basis to understand the current status of climate action integration; then,

compare findings every five years to understand trends in climate action integration over time.

3.4.1 Implications for research and practice

There was a slight decrease in low and high climate integration in evaluations, with a slight

increase in medium climate integration from 2014 to 2019. In response to a growing and

pressing climate change stocktake mandate, further integration of climate change into

evaluation is needed. As evidenced by the reviewed evaluation reports, the integration of

climate change can involve adding climate action as an explicit evaluation objective, question, or

criterion. Such framing showed value by highlighting the implications of climate change,

revealing trade-offs and co-benefits, and encouraging climate action in future programming.

Several assessment frameworks, guidebooks, and reporting formats have also been developed

over the last decade to support this integration. For example, adaptation tracking, a

subcomponent of M&E, seeks to systematically identify, characterize, and compare adaptation

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across nations over time (Ford & Berrang-Ford, 2016). The Tracking Adaptation and Measuring

Development is a conceptual framework to monitor and evaluate climate change adaptation

within and across sectors and levels of programming (Brooks, et al., 2011). The German

Cooperation for International Cooperation and partners have developed an impact evaluation

guidebook for climate change adaptation projects (GIZ, 2015). To guide the tracking of policies

that address mitigation, the World Resources Institute developed a framework (Barua et al.,

2014). Several scholars have synthesized tools, frameworks, and approaches for evaluating

adaptation (Bours et al., 2014; Fisher et al., 2015; Ford et al., 2013). More engagement from

evaluators with these theoretical developments is important for informing climate evaluation;

reviewing the peer-reviewed literature and grey literature on research on evaluation related to

climate evaluation might support this process. Most evaluations mentioned challenges of M&E

more generally rather than specific challenges of climate evaluation; yet, climate evaluation

challenges were extensively discussed in the published literature. We expanded the existing

literature by identifying practical challenges of adaptation assessment including limited

prioritization of climate action in programming and dependency on food security evaluation.

Based on our review, a gap in evaluation practice is the reporting on mitigation measures and

outcomes. Additionally, future research is needed to further develop adaptation indicators,

criteria, and frameworks, particularly those that are grounded in the realities and experiences of

organizations that commissioned the evaluation. Evaluations attuned to the needs, priorities,

and constraints of organizations are important for developing food security programs and

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evaluations responsive to the impacts of climate change (Bours et al., 2014).

3.4.2 Limitations

We acknowledge several limitations of our approach. Firstly, the extent of climate action

integration into evaluation was assessed based on the information presented in the evaluation

report. As with any report, many topics might have been considered during the evaluation

process but not reported on; as such, climate change might have been considered in the

evaluation but not documented. Reflecting on and sharing the decision-making process is

important for providing insights into evaluating climate action. Secondly, the different

terminology for climate action used in evaluation reports made it challenging to classify the

climate considerations of evaluations; clarity in the definition of climate action would support

future climate assessments. Nevertheless, the review is comprehensive and provides in-depth

insights into how UN food security programs are responding to climate change from 2014 to

2019.

3.5 Conclusion

Climate evaluation is a growing area of research and practice in food security and broader

development contexts. This interest is in response to the growing impacts of climate change on

food security globally, public investments made in climate action, and the need to demonstrate

progress toward collective climate change goals. We show through our assessment of UN food

security evaluation reports published over the past six years (2014-2019) that progress toward

mainstreaming climate action in evaluation is slow, particularly for climate change mitigation.

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The limited quality and quantity of data from existing M&E systems create barriers to producing

evaluative judgments around climate action. The integration of climate into the evaluation scope

and approach is an important opportunity for contextualizing, prioritizing, and guiding the

assessment of climate action. Our assessment rubric offers a tool to understand and encourage

climate action mainstreaming into food security evaluation. In doing so, the rubric can help

strengthen the evidence-base of climate-related food security programming, informing

processes such as the upcoming 2023 global climate change stocktake.

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3.6 References

Babiker, M., Bertoldi, P., Buckeridge, M., Cartwright, A., Araos Maldives, M., Bakker, S., Bazaz, A.,

Belfer, E., Benton, T., de Coninck, H., Revi, A., Babiker, M., Bertoldi, P., Buckeridge, M.,

Cartwright, A., Dong, W., Ford, J., Fuss, S., Hourcade, J., … Waterfield, T. (2018). Chapter 4 -

Strengthening and Implementing the Global Response. Global Warming of 1.5°C. An IPCC

Special Report on the Impacts of Global Warming of 1.5°C above Pre-Industrial Levels and

Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the

Global Response to the Threat of Climate Change. Cambridge University Press. Cambridge.

Barua, P., Fransen, T., Wood, D. (2014). CLIMATE POLICY IMPLEMENTATION TRACKING

FRAMEWORK. World Resources Institute. Washington, DC.

Berrang-Ford, L., Biesbroek, R., Ford, J. D., Lesnikowski, A., Tanabe, A., Wang, F. M., Chen, C., Hsu,

A., Hellmann, J. J., Pringle, P., Grecequet, M., Amado, J. C., Huq, S., Lwasa, S., & Heymann, S.

J. (2019). Tracking global climate change adaptation among governments. In Nature

Climate Change. (Vol. 9, pp. 440-449).

Bours, D., McGinn, C., & Pringle, P. (2014). Monitoring & evaluation for climate change

adaptation and resilience : A synthesis of tools , frameworks and approaches. SEA Change

CoP, Phnom Penh and UKCIP, May, 1–67. Oxford. Phnom Penh.

Braun, V., Clarke, V., Hayfield, N., & Terry, G. (2018). Thematic analysis. In P. Liamputtong (Ed.),

Handbook of Research Methods in Health Social Sciences. Springer. Singapore.

Brooks, N., Anderson, S., Ayers, J., Burton, I., & Tellam, I. (2011). Tracking adaptation and

measuring development. IIED. London.

Bunce, A., & Ford, J. (2015). How is adaptation, resilience, and vulnerability research engaging

with gender? In Environmental Research Letters (Vol. 10, Issue 12:123003).

Carbon, M. (2017). An Analytical Framework for Evaluating a Diverse Climate Change Portfolio. In

Evaluating Climate Change Action for Sustainable Development. Springer Nature. Cham.

Colquhoun, H. L., Levac, D., O’Brien, K. K., Straus, S., Tricco, A. C., Perrier, L., Kastner, M., & Moher,

D. (2014). Scoping reviews: Time for clarity in definition, methods, and reporting. In Journal

of Clinical Epidemiology (Vol. 67, Issue 12, pp. 1291–1294).

Conevska, A., Ford, J., Lesnikowski, A., & Harper, S. (2019). Adaptation financing for projects

focused on food systems through the UNFCCC. Climate Policy. (Vol. 19, Issue 1, pp. 43-58).

121

Denton, F., Wilbanks, T. J., Abeysinghe, A. C., Burton, I., Gao, Q., Lemos, M. C., Masui, T., O’Brien,

K. L., Warner, K., Bhadwal, S., Leal, W., Van Ypersele, J. P., & Wright, S. B. (2015). Climate-

resilient pathways: Adaptation, mitigation, and sustainable development. In Climate Change

2014 Impacts, Adaptation and Vulnerability: Part A: Global and Sectoral Aspects. Cambridge

University Press. Cambridge.

Donner, S. D., Kandlikar, M., & Webber, S. (2016). Measuring and tracking the flow of climate

change adaptation aid to the developing world. Environmental Research Letters, 11(5), 1–9.

https://doi.org/10.1088/1748-9326/11/5/054006

FAO, IFAD, UNICEF, W. and W. (2018). The state of food security and nutrition in the world.

FAO. (2001). The State of Food Insecurity in the World 2001. FAO. Rome.

FAO. (2014a). End of project evaluation report of the Programme for Improvement of Irrigation

Systems and Construction of Micro-hydro Power Facilities in Kabul and Bamyan Provinces.

FAO. Rome.

FAO. (2014b). Final Evaluation of “Monitoring and Assessment of GHG Emissions and Mitigation

Potentials in Agriculture Project” - GCP /GLO/286/GER. FAO. Rome.

FAO. (2016). Final evaluation of the Improved Global Governance for Hunger Reduction

Programme. FAO. Rome.

FAO. (2017a). Evaluation of the Benefit-sharing Fund second project cycle. FAO. Rome.

FAO. (2017b). Final evaluation of Sudan Food Security Policy and Strategy Capacity Building

programme. FAO. Rome.

FAO. (2017c). Final Evaluation of the project “Forestry and Protected Area Management in Fiji,

Samoa, Vanuatu and Niue (GEFPAS-FPAM).” FAO. Rome.

FAO. (2018a). Final Evaluation of the Project “Increased Household Food, Income and Nutrition

Security through Commercialization of an Integrated and Sustainable Smallholder Livestock

Sector in Zimbabwe.” FAO. Rome.

FAO. (2018b). Final evaluation of the project “Mainstreaming the use and conservation of

agrobiodiversity in public policy through integrated strategies and in situ implementation in

four Andean Highlands provinces.” FAO. Rome.

FAO. (2018c). Final Evaluation of the Project “Strengthening Climate Change Resilience and

Disaster Risk Reduction in Agriculture to Improve Food Security in Haiti After the

122

Earthquake.” FAO. Rome.

Fereday, J., & Muir-Cochrane, E. (2006). Demonstrating Rigor Using Thematic Analysis : A Hybrid

Approach of Inductive and Deductive Coding and Theme Development. International

Journal of Qualitative Methods, 5, 80–92. https://doi.org/10.1063/1.2011295

Fisher, S., Dinshaw, A., Mcgray, H., Rai, N., & Schaar, J. (2015). Evaluating Climate Change

Adaptation: Learning From Methods in International Development. New Directions for

Evaluation, 2015(147), 13–35. https://doi.org/10.1002/ev.20128

Ford, J. D., & Berrang-Ford, L. (2016). The 4Cs of adaptation tracking: consistency, comparability,

comprehensiveness, coherency. In Mitigation and Adaptation Strategies for Global Change

(Vol. 21, Issue 6, pp. 839–859). https://doi.org/10.1007/s11027-014-9627-7

Ford, J. D., Berrang-Ford, L., Lesnikowski, A., Barrera, M., & Jody Heymann, S. (2013). How to

track adaptation to climate change: A typology of approaches for national-level application.

Ecology and Society, 18(3):40. https://doi.org/10.5751/ES-05732-180340

Fujimori, S., Hasegawa, T., Rogelj, J., Su, X., Havlik, P., Krey, V., Takahashi, K., & Riahi, K. (2018).

Inclusive climate change mitigation and food security policy under 1.5 ◦ C climate goal.

Environmental Research Letters, 13(7): e074033. https://doi.org/10.1088/1748-9326/aad0f7

GIZ. (2015). Impact Evaluation Guidebook for Climate Change Adaptation Projects. GIZ. Bonn.

Huitema, D., Jordan, A., Massey, E., Rayner, T., van Asselt, H., Haug, C., Hildingsson, R., Monni, S.,

& Stripple, J. (2011). The evaluation of climate policy: Theory and emerging practice in

Europe. Policy Sciences, 44:179-198. https://doi.org/10.1007/s11077-011-9125-7

IFAD. (2014a). Kingdom of Morocco Rural Development Project in the Mountain Zones of Al-Haouz

Province. IFAD. Rome.

IFAD. (2014b). Republic of the Sudan Gash Sustainable Livelihoods Regeneration Project. IFAD.

Rome.

IFAD. (2015a). Lao People’s Democratic Republic Rural Livelihoods Improvement Programme in

Attapeu and Sayabouri. IFAD. Rome.

IFAD. (2015b). Republic of Turkey Sivas-Erzincan Development Project. IFAD. Rome.

IFAD. (2016a). Federal Republic of Nigeria Community-Based Agricultural and Rural Development

Programme. IFAD. Rome.

123

IFAD. (2016b). Kyrgyz Republic Agricultural Investments and Services Project. IFAD. Rome.

IFAD. (2016c). Republic of the Philippines Rural Microenterprise Promotion Programme. IFAD.

Rome.

IFAD. (2016d). Evaluation manual. IFAD. Rome.

IFAD. (2017a). Arab Republic of Egypt West Noubaria Rural Development Project. IFAD. Rome.

IFAD. (2017b). Kingdom of Lesotho Rural Financial Intermediation Programme Project

Performance Evaluation. IFAD. Rome.

IFAD. (2017c). Republic of Malawi Rural Livelihoods Support Programme. IFAD. Rome.

IFAD. (2018a). Lao People’s Democratic Republic Northern Region Sustainable Livelihoods through

Livestock Development Project. IFAD. Rome.

IFAD. (2018b). Republic of Guyana Rural Enterprise and Agricultural Development Project. IFAD.

Rome.

IFAD. (2018c). Republic of Kenya Smallholder Horticulture Marketing Programme. IFAD. Rome.

IFAD. (2018d). Socialist Republic of Viet Nam Pro-Poor Partnerships for Agroforestry Development

Project. IFAD. Rome.

IFAD. (2019). Democratic Socialist Republic of Sri Lanka Smallholder Plantations Entrepreneurship

Development Programme. IFAD. Rome.

Kim, Y., Smith, J. B., Mack, C., Cook, J., Furlow, J., Njinga, J. L., & Cote, M. (2017). A perspective on

climate-resilient development and national adaptation planning based on USAID’s

experience. Climate and Development, 9(2):141-151.

https://doi.org/10.1080/17565529.2015.1124037

Lam, S., Dodd, W., Skinner, K., Papadopoulos, A., Zivot, C., Ford, J., Garcia, P. J., & Harper, S. L.

(2019). Community-based monitoring of Indigenous food security in a changing climate:

Global trends and future directions. Environmental Research Letters, 14(7): 073002.

https://doi.org/10.1088/1748-9326/ab13e4

Lamhauge, N., Lanzi, E., & Agrawala, S. (2012). Monitoring and evaluation for adaptation: Lessons

from development cooperation agencies. OECD. Paris.

Mbow, C., Rosenzweig, C., Barioni, L. G., Benton, T. G., Herrero, M., Krishnapillai, M., Liwenga, E.,

Pradhan, P., Rivera-Ferre, M. G., Sapkota, T., Tubiello, F. N., & Xu, Y. (2019). Food Security. In

124

P. Z. P.R. Shukla, J. Skea, E. Calvo Buendia, V. Masson-Delmotte, H.-O. Pörtner, D.C. Roberts,

J. P. P. R. Slade, S. Connors, R. van Diemen, M. Ferrat, E. Haughey, S. Luz, S. Neogi, M.

Pathak, J. Petzold, & J. M. P. Vyas, E. Huntley, K. Kissick, M. Belkacemi (Eds.), Climate Change

and Land: an IPCC special report on climate change, desertification, land degradation,

sustainable land management, food security, and greenhouse gas fluxes in terrestrial

ecosystems. Cambridge University Press. Cambridge.

McHugh, M. L. (2012). Interrater reliability: the kappa statistic. Biochemia Medica, 22(3):276–282.

https://doi.org/10.11613/BM.2012.031

Ray, D. K., West, P. C., Clark, M., Gerber, J. S., Prishchepov, A. V., & Chatterjee, S. (2019). Climate

change has likely already affected global food production. PLoS ONE, 14(5): e0217148.

https://doi.org/10.1371/journal.pone.0217148

Richardson, K. J., Lewis, K. H., Krishnamurthy, P. K., Kent, C., Wiltshire, A. J., & Hanlon, H. M.

(2018). Food security outcomes under a changing climate: impacts of mitigation and

adaptation on vulnerability to food insecurity. Climatic Change, 147(1–2), 327–341.

https://doi.org/10.1007/s10584-018-2137-y

Rowe, A. (2019). Sustainability-Ready Evaluation: A Call to Action. New Directions for Evaluation,

162: 29–48. https://doi.org/10.1002/ev.20365

Runhaar, H., Wilk, B., Persson, Å., Uittenbroek, C., & Wamsler, C. (2018). Mainstreaming climate

adaptation: taking stock about “what works” from empirical research worldwide. Regional

Environmental Change. 18:1201-1210. https://doi.org/10.1007/s10113-017-1259-5

Sherman, M. H., & Ford, J. (2014). Stakeholder engagement in adaptation interventions: an

evaluation of projects in developing nations. Climate Policy, 14(3):417–441.

https://doi.org/10.1080/14693062.2014.859501

Somanathan, E., Sterner, T., Sugiyama, D., Chimanikire, N., Dubash, J., Essandoh-Yeddu, S., Fifita,

L., Goulder, A., Labanndeira, S., Managi, C., Mitchell, J., Montero, P., Teng, F., & Zylicz, T.

(2014). National and Sub-national Policies and Institutions. Cambridge University Press.

Cambridge.

Ssekamatte, D. (2018). The role of monitoring and evaluation in climate change mitigation and

adaptation interventions in developing countries. African Evaluation Journal, 6(1): a254.

https://doi.org/10.4102/aej.v6i1.254

Tendall, D. M., Joerin, J., Kopainsky, B., Edwards, P., Shreck, A., Le, Q. B., Kruetli, P., Grant, M., &

Six, J. (2015). Food system resilience: Defining the concept. In Global Food Security (Vol. 6,

pp. 17–23). https://doi.org/10.1016/j.gfs.2015.08.001

125

Tompkins, E. L., Vincent, K., Nicholls, R. J., & Suckall, N. (2018). Documenting the state of

adaptation for the global stocktake of the Paris Agreement. Wiley Interdisciplinary Reviews:

Climate Change, 9(5), 1–9. https://doi.org/10.1002/wcc.545

Uitto, J.I., Puri, J., & van den Berg, R. D. (2016). Evaluating Climate Change Action for Sustainable

Development. Springer. Cham.

Uitto, Juha I. (2019). Sustainable Development Evaluation: Understanding the Nexus of Natural

and Human Systems. New Directions for Evaluation, 2019(162), 49–67.

https://doi.org/10.1002/ev.20364

UNDP. (2011). Mainstreaming Climate Change in National Development Processes and UN

Country Programming: A guide to assist UN Country Teams in integrating climate change

risks and opportunities. UNDP. New York.

UNDP. (2015). FINAL EVALUATION OF THE PROJECT “BUILDING THE CAPACITY OF THE

AGRICULTURE SECTOR IN DR CONGO TO PLAN FOR AND RESPOND TO THE ADDITIONAL

THREATS POSED BY CLIMATE CHANGE ON FOOD PRODUCTION AND SECURITY” OR

PANA-ASA PROJECT DR CONGO. UNDP. New York.

UNDP. (2016). TERMINAL EVALUATION REPORT: ENHANCING ADOPTION OF CLIMATE SMART

AGRICULTURE PRACTICES IN UGANDA‘S FARMING SYSTEMS. UNDP. New York.

UNEP. (2015). Terminal Evaluation of the UNEP/GEF Project “A Global Initiative on Landscapes for

People, Food and Nature.”UNEP. Kenya.

UNEP. (2016). Terminal Evaluation of the UNDA 7th Tranche funded UNEP project “Capacity

Building in National Planning for Food Security.” UNEP. Kenya.

UNFCCC. (2015). Paris Agreement. Accessed 6 June 2020. Available from

https://unfccc.int/sites/default/files/english_paris_agreement.pdf

UNICEF. (2018). Evaluation of Community-based Management of Acute Malnutrition Programme

supported by UNICEF in DPR Korea. UNICEF. New York.

United Nations. (2015). High level task force on global food and nutrition security (HLTF).

Accessed 15 June 2020. Available from http://www.un.org/en/issues/food/taskforce/

United Nations Evaluation Group. (2016). Norms and standards for evaluation. UNEG. New York.

USAID. (2015). INTEGRATING CLIMATE CHANGE INTO USAID ACTIVITIES. USAID. Arlington.

126

WFP. (2014a). Evaluation of the Impact of Food for Assets on Livelihood Resilience in Guatemala.

WFP. Rome.

WFP. (2014b). Evaluation of the Impact of Food for Assets on Livelihood Resilience in Uganda.

WFP. Rome.

WFP. (2014c). Evaluation of the Impact of Food for Assets on Livelihood Resilience in Senegal

(2005 – 2010). WFP. Rome.

WFP. (2014d). Kenya, PRRO 200174, Food Assistance to Refugees: An Evaluation of WFP’s

Operation (2011-2013). WFP. Rome.

WFP. (2014e). MADAGASCAR, PROTRACTED RELIEF AND RECOVERY (PRRO) 200065 “RESPONSE

TO RECURRENT NATURAL DISASTERS AND SEASONAL FOOD INSECURITY IN

MADAGASCAR.” WFP. Rome.

WFP. (2014f). Philippines, Protracted Relief and Recovery Operation PRRO 200296. WFP. Rome.

WFP. (2014g). Zimbabwe, Protracted Relief and Recovery Operation 200453 “Responding to

Humanitarian Needs and Strengthening Resilience to Food Insecurity” (September 2012–

March 2014). WFP. Rome.

WFP. (2016). Myanmar Protracted Relief and Recovery Operation 200299: “Supporting Transition

by Reducing Food Insecurity and Undernutrition Among the Most Vulnerable.” WFP. Rome.

WFP. (2018). Evaluation of the Nutrition Components of the Algeria PRRO 200301. WFP. Rome.

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CHAPTER 4: HOW AND WHY ARE THEORY OF CHANGE AND REALIST EVALUATION USED IN FOOD SECURITY CONTEXTS? A SCOPING REVIEW

Abstract

The complex ways in which food security actions lead to nutrition and other health outcomes

make it important to clarify what programs work and how, with theory-driven evaluation

emerging as a promising approach to evaluate complex programs. However, it is unclear how

and why theory-driven evaluation is applied in food security contexts. Our objective is to

examine the development and use of Theory of Change and Realist Evaluation to support food

security programs globally. Using a systematic search and screening process, we included

studies that described a food security program, used a Theory of Change or Realist Evaluation,

and presented original research or evaluations. We found a total of 59 relevant Theory of

Change studies and eight Realist Evaluation studies. Based on our analysis, Theories of Change

arose in response to three main problems: 1) the need to evaluate under complexity; 2)

challenges with evaluation; and, 3) information gaps surrounding a program. In contrast, Realist

Evaluation was reported to be developed primarily to understand a program’s outcomes.

Reflecting on the problem to be addressed in the evaluation might help improve

understandings of the evaluation context, which might then inform the choice and design of an

evaluation approach.

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4.1 Introduction

Food security programs play a crucial role in improving nutrition, reducing poverty, and

strengthening resilience to climate change, particularly for rural communities in low resource

settings (Mbow et al., 2019). Such programs often combine a variety of components, including

food assistance, nutritional education, and agricultural technology and training (Grace et al.,

2019). While progress is being made in understanding the impact of food security programs

(Bird et al., 2019; Fiorella et al., 2016), the causal pathways leading to impact are often unclear

(Thornton et al., 2017; Lam et al., 2021). This limitation reflects not only the lack of evaluation

studies that go beyond assessing a program’s results, but also the challenges in attributing

observed outcomes to the food security program. Yet, unraveling the complexities of how food

security actions transform into nutrition and other health outcomes is important for describing,

replicating, and scaling-up effective strategies (Jones et al., 2013).

An important tool in international development and agricultural research programs is theory-

driven evaluation (Johnson et al., 2015), which aims to develop a “program theory” of how a

program works and how the various components interact to produce outcomes (Salter &

Kothari, 2014). Two approaches to theory-driven evaluation gaining popularity in evaluating

complex programs are Theory of Change (ToC) and Realist Evaluation (RE) (Blamey & Mackenzie,

2007; Rolfe, 2019). ToC encourages stakeholders to describe the causal pathways and the

underlying assumptions of programs implemented in the context of social change (Mayne &

Johnson, 2015). RE explores the mechanisms that are likely to operate in social programs, the

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contexts in which they might operate, and the outcomes that will be observed if they operate as

expected (Westhorp 2014). ToCs are increasingly mainstreamed into evaluations of food security

programs (Maru et al., 2018), whereas the use of RE is relatively nascent (Marchal et al., 2012).

Theory-driven evaluation has proven in many cases to be useful (Breuer et al., 2016). However,

the uncritical adoption of theory-driven evaluations opens for unanticipated consequences that

might undermine their value. The main concerns over the use of ToCs are under-contributing

theoretical knowledge and overlooking complexity (Lam, 2020). For REs, there are risks of

suboptimal analyses due to the lack of clarity on what exactly must be done to conduct an RE

(Jagosh, 2019). Despite these challenges and given the value of ToCs and REs, many agricultural

research and development agencies and their funders are continuing to apply theory-driven

evaluation to examine the pathways linking food security actions to nutrition and health

outcomes (Johnson et al., 2015). Learning from the practices and experiences documented in

evaluation studies may provide important insights into strategies for the effective use of theory-

driven evaluation, particularly ToCs and REs, in assessing food security programs.

Given the multiple pathways toward food security, the need to understand how food security

programs lead to nutrition and other health outcomes, and the rising popularity of theory-

driven evaluation, this study asks: how and why are ToCs and RE used? Our objectives are to: 1)

examine the nature, extent, and range of published and grey literature on ToCs and REs used in

the context of food security; and 2) examine the assumptions, conditions, and problem framings

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that allow ToCs and REs to emerge as appropriate tools to guide the evaluation of food security

programs. In doing so, we become better equipped to make methodological choices that align

with the evaluation setting and the attributes of the food security program.

4.2 Methods

We examined the published and grey literature using a scoping review methodology involving a

multi-stage process of search, selection, extraction, and synthesis of the literature (Colquhoun et

al., 2014). We explored the published literature to provide insights into the theoretical

understanding of ToCs and REs whereas the grey literature offered practical knowledge.

4.2.1 Search strategy

In consultation with a university librarian, we developed search terms and strings (Appendix

13). We searched for studies using the following databases: AGRICOLA©, CabDirect©, Web of

Science™ CORE Collection, Medline®, Scopus®, and EconLit©. These databases were selected to

ensure coverage of food security topics from a wide variety of disciplines. The following search

string was used: (food OR agriculture OR nutrition OR livestock OR fish* OR animal OR plant OR

wildlife) AND ((“theor* of change”) OR (realist AND evaluation) OR (realism AND evaluation)).

We also searched Google™ and websites of relevant organizations (Theory of Change

community, the Consultative Group on International Agricultural Research) to capture studies

from the grey literature. No search restrictions were placed. Searches were performed on 10

March 2020. The reference lists of all included studies were hand-searched to identify relevant

studies not captured in the searches.

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4.2.2 Relevance screening and eligibility

All citations were imported into the web-based application DistillerSR© (Evidence Partners

Incorporated, Ottawa, ON, Canada, v2) for duplicates removal and relevance screening. A two-

step relevance screening strategy was employed by two independent reviewers. First, the titles

and abstracts of articles and reports were screened; next, all citations deemed potentially

relevant went through a review of the full-text (Appendix 14). Studies were considered to be

relevant if: they described the development, implementation, and/or evaluation of a food

security9 or nutrition security10 program; they described a ToC and/or RE approach; and, they

were original research or evaluations published in a journal or report (Table 4.1). Reviewers met

regularly throughout the screening process to resolve conflicts and discuss any uncertainties

related to study selection. The degree of agreement between reviewers was assessed using

Cohen’s Kappa (Landis & Koch, 1977).

9 Food security is “a situation that exists when all people, at all times, have physical, social and economic access to

sufficient, safe and nutritious food that meets their dietary needs and food preferences for an active and healthy life”

(FAO 2001, p. 49). 10 Nutrition security is “a situation that exists when secure access to an appropriately nutritious diet is coupled with a

sanitary environment, adequate health services and care, in order to ensure a healthy and active life for all household

members” ((FAO, 2013, p. 50). Nutrition is an integral part of all four dimensions of food security (availability,

accessibility, utilization, and stability) (Hwalla et al., 2016).

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Table 4.1. Criteria to select food-related Theory of Change and Realist Evaluation studies.

Inclusion Exclusion

Study describes the development,

implementation, or evaluation of a

food security program.

Study focused on a topic not related to food security.

Study explicitly mentions using a

Theory of Change and/or Realist

Evaluation approach.

Theory of Change and/or Realist Evaluation approach were

mentioned but were not the primary methodological approach

used in the study.

Individual research study published

in a journal or report.

Conference abstracts, letters to the editor, news articles,

dissertations, and reviews.

4.2.3 Data extraction and synthesis

To address objective one (to examine the nature, extent, and range of published and grey

literature on ToCs and REs used in the context of food security), a data charting form was

created to extract data from the studies (Appendix 15). We captured general characteristics of

the article/report, including authorship details, year of publication, type of publication, study

country, study scale, and food topic. Furthermore, we extracted data relevant to the scoping

review objective including: the evaluation purpose; the evaluation methodology; how climate

change was considered11; how studies described context12; and, how population characteristics

11 Climate change is increasingly impacting how programs are developed, implemented, and evaluated, particularly

those aiming to improve food security. Integrating climate considerations into program theory is essential for

understanding how food security programs will respond to climate change. 12 Making explicit the circumstances in which a program is developed, implemented, and evaluated is important for

understanding why programs work and why their impacts might vary in different settings.

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were reported13. Results were exported into Excel® 2016 (Microsoft, Redmond, WA, USA, v16)

for descriptive analysis.

To address objective two (to examine the assumptions, conditions, and problem framings that

allow ToCs and REs to emerge as appropriate tools to guide the evaluation of food security

programs), all studies were thematically analyzed to identify patterns in the studies using an

inductive approach (Braun et al., 2018). Several sequential phases of inductive coding were

conducted, with results from one level informing the focus of coding in the subsequent phase.

In phase 1, we examined the differences in process, outcomes, and use of theory-driven

evaluation. Building from these findings, phase 2 involved understanding why differences

emerged by examining problem framings. Problem framing is a crucial element of program

theory that defines the challenge which a program will address (Archibald, 2020; Bacchi, 2009).

The multiple experiences, causes, and consequences of food security challenges make it

especially important to define the problem in this context. In phase 3, we examined the

responses to and implications of problem framings. Finally, in phase 4 we examined whether the

responses to problem framings were appropriate to the program needs (see Appendix 17 for

an overview of the coding process). Regular discussions among the authors were held to co-

develop the themes. NVivo© qualitative analysis software (QSR International, Burlington, MA,

13 Differentiating food security outcomes by social identity (e.g. population, age, gender) is helpful for ensuring that

program theories are responding to the needs and priorities of different groups of people.

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USA, v12) was used to facilitate the coding of text segments, develop themes, and organize

quotations.

4.3 Results

4.3.1 Characteristics of studies

After the removal of duplicates and non-relevant studies, and the addition of studies from the

hand-search, a total of 63 studies were identified (Figure 4.1; see Table S4 for a list of all

included studies). Five pairs of studies reported on evaluations of the same food security

program; these pairs were counted once and analyzed together. The kappa scores for the

title/abstract screening and full-text screening were 0.71 and 0.61 respectively, indicating “good

agreement” for both screening levels (McHugh, 2012). Studies were published between 2011

and 2020 (see Appendix 18 for the number of publications over time). The number of studies

utilizing ToCs and RE in food security contexts has increased, with the majority of studies

published within the past five years (2015-2019) (71%, n = 45). Studies were predominately from

countries in Africa or Asia (90%; n = 57) (Table 4.2). A diversity of topics was covered in the

reviewed studies, with a strong focus on nutrition security and agricultural productivity (Figure

4.2). Food security programs operated primarily at the national (59%; n = 37) or international

scale (29%; n = 18). ToCs were used in nearly all studies (94%; n = 59) whereas RE was used in

eight studies (13%). Both ToCs and RE were used in four studies, which were included in the

counts above.

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Figure 4.1. Flow chart showing the selection of food-related Theory of Change and Realist

Evaluation studies.

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Table 4.2. Characteristics of food-related Theory of Change and Realist Evaluation studies.

Theory of Change

studies

Realist Evaluation

studies

All reviewed studies a

Characteristics No. % No. % No. %

Type of publication:

Grey literature 36 61.0 3 37.5 38 60.3

Published literature 23 39.0 5 62.5 25 39.7

Geographic region: b

Africa 41 69.5 4 50.0 42 66.7

Asia 14 23.7 3 37.5 15 23.8

North America 4 6.8 1 12.5 4 6.3

South America 2 3.4 0 0 2 6.3

Europe 2 3.4 2 25.0 2 3.2

Australia and Oceania 2 3.4 0 0 2 3.2

Not applicable c 7 11.9 0 0 7 11.1

Programming scale: b

International 18 30.5 0 0 18 28.6

National 35 59.3 4 50 37 58.7

Provincial 10 16.9 2 25 11 17.5

Local 16 27.1 3 37.5 17 27.0

Not applicable c 7 11.9 0 0 7 11.1

Evaluation purpose b

Evaluation 49 83.0 8 100 53 84.1

Planning 26 44.1 0 0 26 41.3

Learning 12 20.4 0 0 12 19.0

Implementation 8 13.6 0 0 8 12.7

Evaluation approach:

Qualitative 29 49.2 8 100 33 52.4

Quantitative 0 0 0 0 0 0

Mixed qualitative-

quantitative

0 0 0 0 0 0

Not applicable c 7 11.9 0 0 7 11.1

Not specified d 23 39.0 0 0 23 36.5

a Numbers do not add up to the total as studies may apply both Theories of Change and Realist

Evaluation.

b Categories are not mutually exclusive. c Study did not specify characteristics of case studies (e.g. conceptual/theoretical papers). d Study did not provide sufficient detail to categorize the evaluation approach.

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Figure 4.2. Food topics of reviewed Theory of Change and Realist Evaluation studies.

4.3.2 ToCs and RE were developed primarily using qualitative approaches

The development process varied across ToC studies (94%; n = 59), with methods ranging from

participatory workshops (n = 20) which encouraged stakeholder participation, to evaluator-led

approaches such as interviews (n = 2). For example, a participatory workshop in Tanzania

engaged program implementers, dairy value chain scientists, government representatives, and

private sector actors in the creation of a ToC for a dairy value chain development program

(Kidoido & Korir 2013). Another common approach was to draft an initial ToC by the evaluation

team and then circulate the draft to program implementers and/or wider stakeholders for

revisions (Johnson et al. 2015). Of note, 23 studies (36%) did not provide enough detail to

categorize the methodology. REs (13%; n = 8) were also conducted using qualitative approaches

using either interviews (n = 6) or workshops (n = 2). For example, RE was reported to be used

for identifying the relationships between context, mechanisms, and outcomes of a farm

0 2 4 6 8 10 12 14

Food loss

Food security risk management

Community food security

Food safety

Natural resource management

Agricultural innovation systems

Climate change adaptation of food systems

Market-based approaches to food security

Agricultural productivity

Nutrition security

Number of studies

Fo

od

to

pic

Theory of Change Realist Evaluation

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biosecurity project in the United Kingdom (Maye et al., 2019). The authors conducted interviews

with policymakers in addition to literature reviews to develop initial context, mechanism, and

outcome relationships, followed by validation of the relationships through surveys and

interviews with farmers.

4.3.3 ToCs served a variety of purposes whereas RE supported evaluation purposes only

While ToCs had multiple reported uses in a food security program, ToCs primarily served as a

basis for program monitoring and evaluation (83%; n = 49). For example, in Nimpagaritse et al.

(2020) a proposed ToC was developed for a nutrition program in Burundi to identify starting

points for monitoring and evaluation. Once ToCs were developed, many studies collected data

on indicators by complementing the ToC with other evaluation tools, including contribution

analysis (Obodai et al., 2018), outcome harvesting (Douthwaite & Getnet 2019), or qualitative

and/or quantitative monitoring of change pathways identified by the ToC (Cole et al., 2016). Of

note, few studies provided a citation for the specific ToC process or approach used (Arriola et al.,

2020; Michelini et al., 2020; Omore et al., 2019), contributing to uncertainty surrounding the

assumptions underpinning the design of these ToCs. The reviewed studies typically used ToCs to

set the stage for evaluation, suggesting ToCs were considered an evaluation planning tool rather

than an evaluation approach.

Many studies also described developing ToCs for program planning purposes (44%, n = 26) (e.g.

Arriola et al., 2020) or learning, deriving good practices, and generating new research questions

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(20%; n = 12) (e.g. Sally & Merrey 2019). ToCs were rarely reported to be used for

implementation purposes (e.g. Catholic Relief Services 2017) (14%, n = 8). In the few cases

where guiding implementation was a stated purpose, studies supported the practice of

reflection on outcomes to “become part of the culture of implementation” (Apgar et al. 2017, p.

29). In many instances (36%; n = 23), particularly in the grey literature, we were unable to

categorize the evaluation approach because details were missing on how the ToC was

developed.

In contrast to ToC studies, no RE studies reported using the evaluation approach to support

program planning, implementation, or learning. Rather, RE played an important role in

evaluating food security programs to assess and report on results. For example, a study in

Vietnam aimed to identify what contribution the project made to reducing poverty and food

insecurity (McDonald, 2011). The study drew on RE as an evaluation framework to identify what

changed, what mechanisms brought about these changes, and how the context informed the

change. While REs generally provided rich insights into the context and mechanisms that

created desired outcomes of programs, the volume of data generated through REs can be

difficult to manage (Maye et al., 2019).

4.3.4 The use of multiple theory-driven evaluation approaches together

Four studies reported on the use of ToC together with RE. For example, interviews with health

sector staff and reviews of nutritional guidelines helped to develop a retrospective ToC for a

food and beverage sales environment intervention in Canada (Levay et al., 2018). The ToC was

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then reported to be used as a basis for an RE aiming to provide an in-depth explanation as to

why the intervention worked. Another study described using a logical framework, ToC, and RE to

construct a program theory in the context of a child feeding program in Tanzania (Floate et al.,

2019). According to the authors, the logical framework and ToC helped provide theories of how

the program would achieve change through a series of outcomes and planned activities;

however, “critical untested assumptions” were made in using these two approaches (p. 12). Thus,

the authors explained how RE enabled them to tease out how participants may interact with

program resources in a given context to produce outcomes, providing a more nuanced

understanding of key mechanisms and contextual factors that were not provided by the logical

framework or ToC.

4.3.5 Considerations of gender, context, and climate change

The variety of food security topics, methods, and purposes of ToCs made it difficult to draw

broad conclusions on patterns in gender, climate change, and contextual considerations. Also,

there did not appear to be a clear pattern in gender, climate change, and contextual

considerations among RE studies, though this lack of a pattern was likely due to the small

sample of included RE studies. While this review explored how different social groups (e.g.

population, age, gender) were reported on, only gender implications were explicitly mentioned

in studies. Both ToC and RE studies considered gender in nearly half of studies (Figure 4.3),

primarily by outlining outcome pathways for women as the main program beneficiaries. In

several studies, gender concerns were described vaguely. For example, in a ToC of an aquatic

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agricultural systems program, the assumption “issues of gender explicitly addressed” was

presented without an elaboration of the nature of these gendered issues (Johnson et al. 2019,

pg. 423). All RE studies accounted for contextual influences on program implementation and

outcomes, primarily social and/or political influences. Fewer ToC studies integrated context

compared to RE studies, as context was historically not considered in the conceptualization of

ToCs. In a ToC study focused on strengthening smallholder dairy value chains, contextual issues

around the program were “internalized into the change pathway” (Omore et al., 2019, p. 902),

suggesting context might sometimes be implicit. Very few ToC and RE studies noted climate

change considerations.

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Figure 4.3. Considerations of context, gender, and climate change in food-related Theory of

Change and Realist Evaluation studies.

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4.3.6 Problem representations offered by studies

There was considerably more heterogeneity in methods and purposes for ToC studies compared

to RE. To identify factors that might explain these differences, we explored the issues authors

defined for their evaluations. In examining the problem representations offered in studies, three

themes emerged: complex food security programs, systems, and issues; evaluation challenges;

and information gaps in food security strategies, process, and outcomes (see Appendix 19 for

the codebook). Of note, some studies used multiple framings; for example, a study may have

focused primarily on complexity but also discussed limitations of evaluation approaches.

Complex food security programs, systems, and issues. Many ToC studies framed evaluation

problems around the complexity of food security programs, which were characterized by

multidimensions and an integrated and multisectoral approach (Maye et al., 2019; Omore et al.,

2019). Such programs often required long timeframes, multiple causal strands, and multiple

feedback loops (Omore et al., 2019; Wesley et al., 2019), leading to emergence, unpredictability,

non-linearity, and uncertainty of outcomes (Douthwaite et al., 2017; Pradel, et al., 2013).

Furthermore, food security programs were reported to be complex due to the social systems

within which food security actions occur and the interactions of diverse groups whose behaviour

food security programs aimed to influence (Apgar et al., 2017). And in complex social systems,

multiple factors contributed to food security outcomes, making it difficult to identify cause-and-

effect linkages (Child et al., 2015). Food security concepts (e.g. nutrition, food system resilience)

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were also complex themselves due to their lack of clear solutions, a plurality of perspectives, and

evolving nature (Béné et al., 2020; Epp and Garside, 2019).

Evaluation challenges. Another common problem representation reported in ToC studies was

the limitations of existing approaches to evaluation. Traditional approaches to evaluation (e.g.

those comparing a baseline and endline) were described as neither able to capture how and why

programs work (Ton 2014), nor to assess a complex program’s contribution to food security due

to multiple factors that influence change (Bene et al. 2020). Tools conceptually similar to ToC

that aimed to map change pathways (e.g. logic model, logical framework, results chain) were

critiqued for oversimplifying food security programs (Levay et al. 2019). ToCs for agricultural

research have also been critiqued for assuming impact will be created through a predictable

linear adoption pathway, thus ignoring complex systems dynamics and missing alternative

pathways (Douthwaite & Hoffecker, 2017). Furthermore, ToCs were reported to have decreased

effectiveness when program theories were not adequately spelled out or did not account for

assumptions, context, or unexpected outcomes (Cole et al., 2016; Douthwaite et al., 2017). The

limited research on how to evaluate certain food security concepts also posed challenges for

evaluation. For instance, Bene et al. (2019) argued the resilience of food systems to climate

change is a latent variable and thus cannot be measured directly.

Information gaps in food security processes, outcomes, and strategies. Most ToC studies

and all RE studies centered problems around the need for explaining how and why programs

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work. Focusing on program process was considered particularly important in ToC studies. Maru

et al. (2018) explained that many food security programs, especially agricultural research for

development interventions, tended to have “lofty food security and/or agricultural development

goals” without articulating “the theories and pathways for how and why the particular

intervention would contribute to or achieve impact” (p. 345). The need for a framework to

navigate towards impact was also reported in ToC studies, particularly in settings characterized

by a “multiplicity of views from different actors on issues of joint concern” (Vellema et al., 2017,

p. 2). Donors have sometimes influenced the use of ToCs in program planning since many

donors require projects to present a clear plan showing how activities lead to outcomes

(Catholic Relief Services 2017). RE studies appeared motivated simply by the fact that a food

security program’s outcomes were understudied, underexplored, or unknown (Michelini et al.,

2020; Ohly et al., 2019). Among these RE studies, few also discussed how programs were

complex due to contextual factors (e.g. social, cultural, economic) that influenced a program’s

outcomes (Owusu-Addo et al., 2019).

4.3.7 Responses to problem framings

To deepen insights into problem framings articulated by authors, we examined the response of

authors to these problem framings and conditions under which responses occurred (see

Appendix 20 for the codebook). Then, we assessed whether responses were appropriate for the

problem framing. We found ToCs to be the main solution for all problem framings, suggesting

ToCs might be appropriate in addressing multi-dimensional needs. All reviewed ToC studies

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included a narrative describing change pathways toward food security, with most narratives also

accompanied by a figure depicting such pathways. The figure typically included arrows

representing presumed causal linkages and boxes representing activities and outcomes. This

boxes-and-arrows model was popular among each problem framing, but the level of specificity

varied, with complexity-framed studies reaching an impressive level of detail. All RE studies

presented context, mechanism, and outcome configurations. The relationship between problem

framings and responses to problem framings is shown in Figure 4.4.

Figure 4.4. Concept map showing the relationship between problem framings, responses to

problem framings, and conditions under which responses occur in theory-driven evaluations.

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There were two main pathways through which “complexity-aware” ToCs were developed: (1) the

study emphasized complex issues or systems (Douthwaite and Hoffecker 2017; Epp et al. 2019;

Maru et al. 2018), and (2) the study focused on evaluation challenges or information gaps while

also emphasizing complexity (Douthwaite et al., 2017). Studies reported accounting for

complexity through feedback loops (i.e. two-way arrows linking outcomes) and backward

mapping (i.e. asking what are the necessary preconditions for outcomes to occur). The concept

of emergence was considered in some studies through revisions made to the ToC as new

information was gained during program planning or implementation. For example, in Apgar et

al. (2017), the initial broad ToC for an aquatic agricultural systems program was revised after a

planning workshop to further detail the ToC, leading to the integration of gender equity,

nutrition, and climate change resilience needs. According to some authors, ToCs of complex

programs were purposively simplified by presenting a variety of ToCs for actors, projects, or

sites (i.e. nested ToCs). For instance, Douthwaite et al. (2013) developed a broad ToC at the

program-level and several ToCs at the project-level.

Studies describing a program’s complexity, an evaluation challenge, or an information gap

typically developed ToCs that appeared simple. Simple ToCs were often characterized by

linearity, expressed through the use of uni-directional arrows between activities and outcomes

(Pound 2015). In many studies, ToCs were described as following an “if/then” logic (i.e. if these

activities are conducted, then these outcomes will be achieved) (Álvarez-Mingote et al., 2020;

Baker et al., 2013; Levay et al., 2018), suggesting a stepwise pathway toward food security

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outcomes. Some studies included assumptions in the linear pathway, which resembled an

adapted logic model (e.g. Levay et al., 2019; Obodai et al., 2018). While program theories in RE

studies were static, ToCs might likely be revised following implementation. For example, in

Nimpagaritse et al. (2020), the ToC initially resembled a logic model but upon revision, it

included assumptions such as socio-political stability. All RE studies were reported to be

conducted in response to information gaps around a program’s outcomes, with little variation

observed in the outputs between studies.

We found ToCs to be an appropriate solution to issues of complexity by unpacking the change

pathways and assumptions made. However, when issues were framed solely in terms of

evaluation challenges or information gaps, there was potential for ToC misuse. Some of these

studies presented an overly simplified ToC, characterized by linearity or an absence of

assumptions, leading to a reduced ability of ToCs to guide program planning and evaluation as

ToCs were originally intended. As cautioned by Apgar et al. (2017), care needs to be taken

during ToC development otherwise ToC risks becoming “nothing more than a complex log

frame” (Apgar et al., 2017, p. 29). In ToC studies where pathways toward food security were

relatively predictable and understanding cause-and-effect assumptions was not an immediate

goal, alternative approaches to evaluation might be appropriate. For example, in the context of a

therapeutic feeding program focused on addressing malnutrition, Floate et al. (2018) created a

logic model to develop an initial program theory and then stated using a ToC to provide a more

in-depth depiction of the program theory. We found RE to be appropriate for addressing

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information gaps by providing a nuanced understanding of how, why, and for whom changes

occurred. However, for RE studies that also emphasized complexity, it would be helpful to clarify

how the dynamics of non-linear outcomes (e.g. poverty reduction) and multiple interacting

program components could be accounted for in context, mechanism, and outcome

configurations (Owusu-Addo et al., 2019).

4.4 Discussion

This review examined how and why theory-driven evaluation has been developed and used to

evaluate food security programs globally, drawing on ToC and RE as examples. The emphasis of

included studies was on the topic of food production, likely due to early conceptualizations of

food security when it was believed that producing more food led to food security (Hendriks,

2015). More recently, as awareness of the nature of malnutrition (undernutrition, overnutrition,

and micronutrient deficiencies) improved, studies equally focused on nutrition. Studies were

geographically concentrated in Africa and Asia, areas where the prevalence of malnutrition

remains the highest (FAO 2020). Indeed, we would expect studies to prioritize food security

programs in areas with high food security challenges.

While we found variations in the process of ToC development, in many studies little detail was

provided about the process. This finding was consistent with sentiments in the literature, which

highlighted the limited guidance, training, and agreement on how to develop a ToC (Maye,

2015; Maru et al., 2018). It is important to elaborate on the ToC development process as the

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absence of detail gave the impression that the ToC might have been developed superficially and

applied in a cursory manner. Opportunities exist for authors to describe and reflect on the

process, providing clarity for others in developing ToCs for food security programs. In contrast,

reporting on RE was consistent, likely due to the presence of standards to guide practice. For

example, the Realist and Meta-narrative Evidence Syntheses: Evolving Standards (RAMESES) II

Project developed resources, training materials, and reporting standards for REs (Wong et al.,

2017).

ToCs were used substantially more than RE, although the reason for choosing the evaluation

approach was rarely made explicit. Providing rationale is important for understanding when and

why a particular evaluation approach might be suitable for capturing the complexities of a food

security program, issue, or context. Moreover, as ToCs had a variety of stated purposes, being

explicit about what the ToC hopes to achieve is critical for establishing the foundation for

starting the process of developing program theories. Interestingly, we found few studies

reported using ToCs to support implementation purposes, similar to a review of ToCs used in

public health interventions (Breur et al., 2016). Revising ToCs as new information is learned is a

potential strategy to help guide food security practitioners and evaluators toward desired

outcomes during implementation (Ghate, 2018).

We identified several studies applying a ToC followed by an RE, supporting the hypothesis that

ToC and RE might be productively combined (Blamey & Mackenzie, 2007). In comparing these

151

studies, we found many RE studies typically concluded with a presentation of various context,

mechanism, and outcome configurations for a food security program. However, exploring how

such configurations might refine the initial program theory could lead to the generation of

middle-range theories relevant in another context (Owusu-Addo et al., 2019, p. 16). A middle-

range theory is “not abstract to the point of being disconnected from the on-the-ground

workings of programs, yet not so specific to pertain to one program” (Jagosh, 2019, p. 364).

Importantly, integrating key elements of context into program theories might also build context-

sensitive knowledge, allowing for better predictions of how programs function in diverse

contexts. Considering we identified very few studies combining ToC and RE, there is a need for

further studies combining ToC and RE approaches in different fields and different ways to

further substantiate our findings (Rolfe 2019).

Although the achievement of nutrition and other health outcomes is contextually contingent,

few ToC studies reported on the context in which programs were situated, particularly in relation

to climate change. And while all RE studies reported on context, climate change was rarely

considered as a component of that context. Integrating climate change mitigation and

adaptation into program theories is important because environmental sustainability is critical to

sustaining food security in the long term and essential to achieving the Paris Agreement’s

emissions targets (Fanzo et al., 2020). Nearly half of ToC and RE studies incorporated gender

dimensions, which acknowledge that the experiences of food security differ based on gender

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(Mbow et al., 2019). Continuing to question “for whom” program theories work might help

ensure pathways toward food security are socially inclusive (Forsyth, 2018; Lam et al., 2019).

The if/then logic presented in many ToC studies came from logic model thinking, which was in

contrast with some ToC thinking that acknowledges: “A ToC sets out testable hypotheses of a

change process by working back from long-term goals to identify all the conditions that

(theoretically) must be in place for the goals to occur” (Belcher et al., 2017, p. 3). This logic of

“for x to happen, y is essential” is an important tenet of ToC for focusing on how systems

change, before thinking about how programs might contribute to change. In doing so,

evaluations become outcome-based rather than objective-based. Clarifying how ToCs differ

from conceptually similar approaches might help ensure ToCs are used as originally intended

(Maru et al., 2018). One option for evaluators to consider is the checklist in Breuer et al. (2016)

which guides key aspects of ToC to include.

Based on our analysis, the inclusion of additional problem framings such as complexity might

lead to sufficiently detailed ToCs. For RE studies, it is important to consider how elements of

complexity such as emergence and non-linearity might be reflected in context, mechanism, and

outcome relationships. Potential strategies include the use of arrows showing the

interconnections between different relationships (Punton et al., 2016) or feedback loops

(Feather, 2018). In multisectoral programs with multiple food security outcomes, prioritizing key

context, mechanism, and outcome relationships were critical for ensuring the data produced are

153

manageable (Leavy et al., 2018). As problem framing sets boundaries on what aspects should be

studied and evaluated and what other aspects should be left out, reflecting on the problem

framing should be considered in theory-driven evaluation (Archibald, 2020; Bacchi, 2009).

4.4.1 Strengths and limitations

We acknowledge several limitations. First, GoogleTM was not able to capture all studies from

grey literature, especially from sources that do not allow GoogleTM to crawl their sites. We partly

addressed this limitation by complementing the search with a targeted website search of select

organizations (e.g. ToC community and CGIAR). Secondly, our ability to understand the

development of theory-driven evaluation was based on what was reported in studies. Given

word and space limits, articles and reports might have prioritized documenting evaluation

outcomes rather than process. For example, in several studies, evaluation experiences were

presented across multiple articles (e.g. Levay et al., 2018; Levay et al., 2019). Thirdly, this review

included multiple articles published by the same research team. For instance, Douthwaite et al.

published five included studies. Researchers may have used a similar approach across multiple

studies, which could have resulted in an over-emphasis of their research process in the results.

4.5 Conclusion

By synthesizing the literature on theory-driven evaluation, we showed the various ways in which

ToCs and RE were developed and used in food security contexts. Our review demonstrated that

ToCs arose in response to several issues, including the need to evaluate under complexity,

challenges with evaluation approaches, and information gaps surrounding a food security

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process, outcome, and strategy. In contrast, studies reported conducting an RE primarily to

understand a program’s outcomes in response to information gaps. In examining these

responses, we showed that problem framings focused on complexity contributed to more

nuanced program theories, possibly through improved understandings of the evaluation context

and adaptations to the evaluation approach. We recommend that practitioners working in food

security contexts consider reflecting on the problem to be addressed in the evaluation,

potentially leading to a more informed choice and design of evaluation approaches.

4.5.1 Lessons learned

1) Make explicit the purpose, process, and rationale for conducting a theory-driven evaluation.

This clarity from the beginning provides the foundation for the development of theory-driven

evaluation. Furthermore, this clarity helps readers understand when and why a particular

approach is suitable for a specific context.

2) Consider revising ToCs when new knowledge is gained. Adapting ToC during program

planning or implementation might inform important program adaptations, while refining ToCs

after an evaluation is completed may generate program theories that apply to other settings.

3) Consider how complexity might be accounted for in RE of complex programs. Many food

security outcomes have multiple interacting influences crossing socio-ecological levels and

require multi-level strategies to achieve food security. This complexity requires evaluative

thinking on how dynamics can be creatively captured in configurations that link context,

mechanisms, and outcomes.

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4) Question why a specific evaluation approach was adopted, for whom the approach supports,

and what might be included/excluded. This process might help evaluators discern which

evaluation approaches are suitable and what elements to include in these approaches.

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4.6 References

Álvarez-Mingote, C., Moore, A., & McNamara, P. (2020). Assessing the role of stakeholder

platforms as drivers of resilient communities: the case of Malawi. Journal of Agricultural

Education and Extension, 26(1), 75–95. https://doi.org/10.1080/1389224X.2019.1674169

Apgar, J. M., Allen, W., Albert, J., Douthwaite, B., Paz Ybarnegaray, R., & Lunda, J. (2017). Getting

beneath the surface in program planning, monitoring and evaluation: Learning from use of

participatory action research and theory of change in the CGIAR Research Program on

Aquatic Agricultural Systems. Action Research, 15(1), 15–34.

https://doi.org/10.1177/1476750316673879

Archibald, T. (2020). What’s the Problem Represented to Be? Problem Definition Critique as a

Tool for Evaluative Thinking. American Journal of Evaluation, 41(1), 6–19.

https://doi.org/10.1177/1098214018824043

Arriola, K. R. J., Ellis, A., Webb-Girard, A., Ogutu, E. A., McClintic, E., Caruso, B., & Freeman, M. C.

(2020). Designing integrated interventions to improve nutrition and WASH behaviors in

Kenya. Pilot and Feasibility Studies, 6, 10. https://doi.org/10.1186/s40814-020-0555-x

Bacchi, C. L. (2009). Analysing Policy: What’s the problem represented to be? Frenchs Forest,

Australia: Pearson Education.

Baker, J., Sanghvi, T., Hajeebhoy, N., Martin, L., & Lapping, K. (2013). Using an evidence-based

approach to design large-scale programs to improve infant and young child feeding. Food

and Nutrition Bulletin, 34(4): S146-55. https://doi.org/10.1177/15648265130343s202

Belcher, B., Suryadarma, D., & Halimanjaya, A. (2017). Evaluating policy-relevant research: lessons

from a series of theory-based outcomes assessments. Palgrave Communications, 3(1),

17017. https://doi.org/10.1057/palcomms.2017.17

Bene, C., Riba, A., & Wilson, D. (2020). Impacts of resilience interventions - Evidence from a

quasi-experimental assessment in Niger. International Journal of Disaster Risk Reduction, 43.

https://doi.org/10.1016/j.ijdrr.2019.101390

Béné, C., Riba, A., & Wilson, D. (2020). Impacts of resilience interventions – Evidence from a

quasi-experimental assessment in Niger. International Journal of Disaster Risk Reduction, 43,

101390. https://doi.org/10.1016/j.ijdrr.2019.101390

Bird, F. A., Pradhan, A., Bhavani, R. V., & Dangour, A. D. (2019). Interventions in agriculture for

nutrition outcomes: A systematic review focused on South Asia. Food Policy, 82, 39-49.

https://doi.org/10.1016/j.foodpol.2018.10.015

157

Blamey, A., & Mackenzie, M. (2007). Theories of Change and Realistic Evaluation: Peas in a Pod

or Apples and Oranges? Evaluation, 13(4), 439–455.

https://doi.org/10.1177/1356389007082129

Braun, V., Clarke, V., Hayfield, N., & Terry, G. (2018). Thematic analysis. In P. Liamputtong (Ed.),

Handbook of Research Methods in Health Social Sciences. Singapore: Springer.

Breuer, E., Lee, L., De Silva, M., & Lund, C. (2016). Using theory of change to design and evaluate

public health interventions: A systematic review. Implementation Science, 11(1). 63.

https://doi.org/10.1186/s13012-016-0422-6

Catholic Relief Services. (2017). Theory of Change, Metrics and Learning Agenda. Baltimore,

United States: Catholic Relief Services.

Child, K., Kidoido, M., Kanyuuru, C. (2015). Using the Theories of Change approach to monitor,

evaluate and learn in the CGIAR research program on Livestock and Fish. Nairobi, Kenya:

ILRI.

Cole, D. C., Levin, C., Loechl, C., Thiele, G., Grant, F., Girard, A. W., Sindi, K., & Low, J. (2016).

Planning an integrated agriculture and health program and designing its evaluation:

experience from Western Kenya. Evaluation and Program Planning, 56, 11–22.

https://doi.org/10.1016/j.evalprogplan.2016.03.001

Colquhoun, H. L., Levac, D., O’Brien, K. K., Straus, S., Tricco, A. C., Perrier, L., Kastner, M., & Moher,

D. (2014). Scoping reviews: Time for clarity in definition, methods, and reporting. In Journal

of Clinical Epidemiology, 67(12), 1291-1294. https://doi.org/10.1016/j.jclinepi.2014.03.013

Douthwaite, B., Getnet, K. (2019). Outcome Evaluation of the work of the CGIAR Research Program

on Land, Water and Ecosystems (WLE) on soil and water management in Ethiopia. Nairobi,

Kenya: CGIAR.

Douthwaite, B., Kamp, K., Longley, C., Kruijssen F., Puskur, R., Chiuta, T., Apgar, M., Dugan, P.

(2013). Using theory of change to achieve impact in AAS. Penang, Malaysia: WorldFish.

Douthwaite, B., & Hoffecker, E. (2017). Towards a complexity-aware theory of change for

participatory research programs working within agricultural innovation systems.

Agricultural Systems, 155, 88–102. https://doi.org/10.1016/j.agsy.2017.04.002

Douthwaite, B., Mayne, J., McDougall, C., & Paz-Ybarnegaray, R. (2017). Evaluating complex

interventions: A theory-driven realist-informed approach. Evaluation, 23(3), 294–311.

https://doi.org/10.1177/1356389017714382

158

Fanzo, J., Covic, N., Dobermann, A., Henson, S., Herrero, M., Pingali, P., & Staal, S. (2020). A

research vision for food systems in the 2020s: Defying the status quo. Global Food Security,

26, 100397. https://doi.org/10.1016/j.gfs.2020.100397

FAO. (2013). The State of Food Insecurity in the World 2013: The multiple dimensions of food

security. Rome, Italy: FAO.

Feather, J. L. (2018). Developing programme theories as part of a realist evaluation of a

healthcare quality improvement programme. International Journal of Care Coordination,

21(3), 68-72. https://doi.org/10.1177/2053434518779753

Fiorella, K. J., Chen, R. L., Milner, E. M., & Fernald, L. C. H. (2016). Agricultural interventions for

improved nutrition: A review of livelihood and environmental dimensions. Global Food

Security, 8, 39-47. https://doi.org/10.1016/j.gfs.2016.03.003

Floate, H., Durham, J., & Marks, G. C. (2019). Moving on from logical frameworks to find the

“missing middle” in international development programmes. Journal of Development

Effectiveness, 11(1), 89–103. https://doi.org/10.1080/19439342.2018.1551921

Forsyth, T. (2018). Is resilience to climate change socially inclusive? Investigating theories of

change processes in Myanmar. World Development, 111, 13–26.

https://doi.org/10.1016/j.worlddev.2018.06.023

Ghate, D. (2018). Developing theories of change for social programmes: co-producing evidence-

supported quality improvement. Palgrave Communications, 4(1), 90.

https://doi.org/10.1057/s41599-018-0139-z

Grace, D., Dipeolu, M., & Alonso, S. (2019). Improving food safety in the informal sector: nine

years later. Infection Ecology and Epidemiology, 9(1), 1579613.

https://doi.org/10.1080/20008686.2019.1579613

Hendriks, S. L. (2015). The food security continuum: a novel tool for understanding food

insecurity as a range of experiences. Food Security, 7(3), 609–619.

https://doi.org/10.1007/s12571-015-0457-6

Howland, F. (2019). Individual capacity baseline report. Rome, Italy: CIAT.

Hwalla, N., El Labban, S., & Bahn, R. A. (2016). Nutrition security is an integral component of food

security. Frontiers in Life Science, 9(3), 167-172.

https://doi.org/10.1080/21553769.2016.1209133

Jagosh, J. (2019). Realist Synthesis for Public Health: Building an Ontologically Deep

159

Understanding of How Programs Work, for Whom, and in Which Contexts. Annual Review

of Public Health, 40: 361-372. https://doi.org/10.1146/annurev-publhealth-031816-044451

Johnson, N., Mayne, J., Grace, D., & Wyatt, A. (2015). How will training traders contribute to

improved food safety in informal markets for meat and milk? A theory of change analysis.

Washington, DC: International Food Policy Research Institute.

Jones, A. D., Ngure, F. M., Pelto, G., & Young, S. L. (2013). What Are We Assessing When We

Measure Food Security? A Compendium and Review of Current Metrics. Advances in

Nutrition: An International Review Journal, 4(5), 481–505.

https://doi.org/10.3945/an.113.004119

Kidoido, M., Korir, L. (2013). Report of the Tanzania Dairy Value Chain Impact Pathways

Workshop, Dar-es-Salaam, Tanzania, 7-8 May 2013. Nairobi, Kenya: ILRI.

Lam, S, Dodd, W., Berrang-Ford, L., Ford, J., Skinner, K., Papadopoulos, A., & Harper, S. L. (2021).

How are climate actions evaluated? A review of United Nations food security evaluations.

Global Food Security, 28, 100509. https://doi.org/10.1016/j.gfs.2021.100509

Lam, S., Dodd, W., Whynot, J., & Skinner, K. (2019). How is gender being addressed in the

international development evaluation literature? A meta-evaluation. Research Evaluation,

28(2), 158-168. https://doi.org/10.1093/reseval/rvy042

Lam, S. (2020). Toward Learning from Change Pathways: Reviewing Theory of Change and Its

Discontents. Canadian Journal of Program Evaluation, 35(2), 188-203.

https://doi.org/10.3138/cjpe.69535

Landis, J. R., & Koch, G. G. (1977). The measurement of observer agreement for categorical data.

Biometrics, 33(1), 159–174. https://doi.org/10.2307/2529310

Leavy, J., Boydell, E., McDowell, S., Sladkova, B. (2018). Resilience results BRACED final evaluation.

Washington, DC: Itad.

Levay, A. V, Chapman, G. E., Seed, B., & Wittman, H. (2018). It’s just the right thing to do:

conceptualizing a theory of change for a school food and beverage sales environment

intervention and implications for implementation evaluation. Evaluation and Program

Planning, 70, 73–82. https://doi.org/10.1016/j.evalprogplan.2018.04.011

Levay V, A., Chapman, G. E., Seed, B., & Wittman, H. (2018). It’s just the right thing to do:

Conceptualizing a theory of change for a school food and beverage sales environment

interv ention and implications for implementation evaluation. Evaluation and Program

Planning, 70, 73–82. https://doi.org/10.1016/j.evalprogplan.2018.04.011

160

Levay, A. V, Chapman, G. E., Seed, B., & Wittman, H. (2019). District-level implementation of

British Columbia’s school food and beverage sales policy: a realist evaluation exploring

intervention mechanisms in urban and rural contexts. Canadian Journal of Public Health,

110(1), 21–30. https://doi.org/10.17269/s41997-018-0159-x

Marchal, B., van Belle, S., van Olmen, J., Hoerée, T., & Kegels, G. (2012). Is realist evaluation

keeping its promise? A review of published empirical studies in the field of health systems

research. Evaluation, 18(2), 192-212. https://doi.org/10.1177/1356389012442444

Maru, Y., Sparrow, A., Stirzaker, R., & Davies, J. (2018). Integrated agricultural research for

development (IAR4D) from a theory of change perspective. Agricultural Systems, 165, 310–

320. https://doi.org/10.1016/j.agsy.2016.09.012

Maru, Y. T., Sparrow, A., Butler, J. R. A., Banerjee, O., Ison, R., Hall, A., & Carberry, P. (2018).

Towards appropriate mainstreaming of “Theory of Change” approaches into agricultural

research for development: Challenges and opportunities. Agricultural Systems, 165, 344–

353. https://doi.org/10.1016/j.agsy.2018.04.010

Maye, D., Enticott, G., & Naylor, R. (2019). Theories of Change in Rural Policy Evaluation.

Sociologia Ruralis, 60(1): 198-221. https://doi.org/10.1111/soru.12269

Mayne, J., & Johnson, N. (2015). Using theories of change in the CGIAR Research Program on

Agriculture for Nutrition and Health. Evaluation, 21(4), 407–428.

https://doi.org/10.1177/1356389015605198

Mbow, C., Rosenzweig, C., Barioni, L.G., Benton, T.G., Herrero, M., Krishnapillai, M., Liwenga, E.,

Pradhan, P., Rivera-Ferre, M.G., Sapkota, T., Tubiello, F.N., Xu, Y., 2019. Food security. In:

Shukla, P.Z.P.R., Skea, J., Calvo Buendia, E., Masson- Delmotte, V., P¨ortner, H.-O., Roberts,

D.C., Slade, J.P.P.R., Connors, S., van Diemen, R., Ferrat, M., Haughey, E., Luz, S., Neogi, S.,

Pathak, M., Petzold, J., Vyas, J.M.P., Huntley, E., Kissick, K., Belkacemi, M. (Eds.), Climate

Change and Land: an IPCC Special Report on Climate Change, Desertification, Land

Degradation, Sustainable Land Management, Food Security, and Greenhouse Gas Fluxes in

Terrestrial Ecosystems. Cambridge, UK: Cambridge University Press.

McDonald, B. (2011). Managing water and land at the interface between fresh and saline

environments An impact evaluation. Colombo, Sri Lanka: CGIAR.

McHugh, M. L. (2012). Interrater reliability: the kappa statistic. Biochemia Medica, 22(3), 276–282.

https://doi.org/10.11613/BM.2012.031

Michelini, L., Grieco, C., Ciulli, F., & Di Leo, A. (2020). Uncovering the impact of food sharing

platform business models: a theory of change approach. British Food Journal, 122(5). 1437-

161

1462. https://doi.org/10.1108/BFJ-06-2019-0422

Nimpagaritse, M., Korachais, C., & Meessen, B. (2020). Effects in spite of tough constraints - A

theory of change based investigation of contextual and implementation factors affecting

the results of a performance based financing scheme extended to malnutrition in Burundi.

PLoS ONE, 15(1), e0226376. https://doi.org/10.1371/journal.pone.0226376

Obodai, J., Adjei, P. O. W., Hamenoo, S. V. Q., & Abaitey, A. K. A. (2018). Towards household food

security in Ghana: assessment of Ghana’s expanded forest plantation programme in Asante

Akim South District. GeoJournal, 83(2), 365–380. https://doi.org/10.1007/s10708-017-9776-

9

Ohly, H., Crossland, N., Dykes, F., Lowe, N., & Moran, V. H. (2019). A realist qualitative study to

explore how low-income pregnant women use Healthy Start food vouchers. 15, e12632.

Maternal and Child Nutrition. https://doi.org/10.1111/mcn.12632

Omore, A., Kidoido, M., Twine, E., Kurwijila, L., O’Flynn, M., & Githinji, J. (2019). Using “theory of

change” to improve agricultural research: recent experience from Tanzania. Development in

Practice, 29(7), 898–911. https://doi.org/10.1080/09614524.2019.1641182

Owusu-Addo, E., Renzaho, A. M. N., & Smith, B. J. (2019). Cash transfers and the social

determinants of health: Towards an initial realist program theory. Evaluation, 25(2), 224-

244. https://doi.org/10.1177/1356389018814868

Pradel, W., Cole, D.C., Prain, G. (2013). Mixing methods for rich and meaningful insight: Evaluating

changes in an agricultural intervention in the Central Andes. Available from:

https://www.betterevaluation.org/sites/default/files/Mixing%20Methods%20for%20Rich%2

0and%20Meaningful%20Insight.pdf. Accessed 10 Nov 2020.

Punton, M., Vogel, I., Lloyd, R. (2016). Reflections from a Realist Evaluation in Progress: Scaling

Ladders and Stitching Theory. Brighton, UK: IDS.

Rolfe, S. (2019). Combining Theories of Change and Realist Evaluation in practice: Lessons from a

research on evaluation study. Evaluation, 25(3), 294–316.

https://doi.org/10.1177/1356389019835229

Sally, H., Merrey, D. (2019). Outcome Evaluation of Research for Development Work Conducted in

Ghana and Sri Lanka under the Resource, Recovery and Reuse (RRR) Subprogram of the

CGIAR Research Program on Water, Land and Ecosystems (WLE). Colombo, Sri Lanka: CGIAR.

Salter, K. L., & Kothari, A. (2014). Using realist evaluation to open the black box of knowledge

translation: a state-of-the-art review. Implementation Science. 9(1), 115.

162

https://doi.org/10.1186/s13012-014-0115-y

Thornton, P. K., Schuetz, T., Förch, W., Cramer, L., Abreu, D., Vermeulen, S., & Campbell, B. M.

(2017). Responding to global change: A theory of change approach to making agricultural

research for development outcome-based. Agricultural Systems, 152, 145–153.

https://doi.org/10.1016/j.agsy.2017.01.005

Van Epp, M., & Garside, B. (2019). Towards an evidence base on the value of social learning-

oriented approaches in the context of climate change and food security. Environmental

Policy and Governance, 29(2), 118–131. https://doi.org/10.1002/eet.1835

Vellema, S., Maru, Y. T., Ekong, J., McNamara, P., Waters-Bayer, A., Watson, D., & Brouwers, J.

(2017). Do theories of change enable innovation platforms and partnerships to navigate

towards impact? Amsterdam, Netherlands: Royal Tropical Institute.

Wesley, A. S., De Plaen, R., Michaux, K. D., Whitfield, K. C., & Green, T. J. (2019). Integrating

nutrition outcomes into agriculture development for impact at scale: Highlights from the

Canadian International Food Security Research Fund. Maternal and Child Nutrition, 15(3),

e12812. https://doi.org/10.1111/mcn.12812

Westhorp, G. (2014). Realist Impact Evaluation. London, UK: ODI.

Wong, G., Westhorp, G., Greenhalgh, J., Manzano, A., Jagosh, J., & Greenhalgh, T. (2017). Quality

and reporting standards, resources, training materials and information for realist evaluation:

the RAMESES II project. Health Services and Delivery Research, 5, 28.

https://doi.org/10.3310/hsdr05280

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CHAPTER 5: “WE HAVE A LOT OF THINGS TO DO:” ON PLANNING AND EVALUATING A COMPLEX FOOD SAFETY PROGRAM OPERATING UNDER A CHANGING CLIMATE

Abstract

The multifaceted nature of food safety often requires coordinated action across sectors to

ensure safe food. Yet, minimal guidance exists on how to design and measure the outcomes of

multisectoral programs that operate under climate change. Our objective is to explore the

experiences of food safety actors to consider how we might better develop and evaluate food

safety programs. To do so, we draw on a case study of an ongoing, multi-year development

program aiming to improve pork safety in informal food markets of Vietnam called SafePORK.

We thematically analyze data from remote qualitative interviews conducted with program

researchers (n=7) and program participants (n=23). Researchers found the process of reflecting

on pathways toward program goals helped them acknowledge, document, and respond to the

adaptive nature of complex programs. Program participants, particularly slaughterhouse workers

and retailers, shared how they are adapting to the impacts of climate change, an aspect not

originally considered within the design of the program. We identified three lessons: 1) develop

the program theory; 2) attune to climate change; and, 3) design with gender equity in mind.

When applied, these lessons have the potential to bring a new level of nuance and focus to

evaluations of complex food safety programs.

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5.1 Introduction

Food safety risks are exacerbated by shocks to the food system, including environmental

degradation, market distortions, political upheavals, and now, the COVID-19 pandemic (Fanzo et

al., 2020). Increasingly coming into sharper focus is the shock of climate change, which has

multifaceted impacts on food safety. For instance, rising temperatures strengthen the survival of

foodborne pathogens (FAO et al., 2021). During flooding, food becomes unsafe to eat if the

food encounters contaminated floodwater (Mbow et al., 2019). The 2021 report on Food Security

and Nutrition in the World highlights that the number of people suffering from food insecurity is

increasing after decades of steady declines, contributed primarily by climate change and COVID-

19 (FAO et al., 2021). These impacts highlight the need for holistic action that addresses the

vulnerabilities of food safety to climate change and other drivers of food safety risk.

Recognizing the multifaceted nature of food safety, efforts are increasingly moving from

addressing a single driver of food safety to multisectoral approaches that strengthen food safety

(FAO et al., 2021; Havelaar et al., 2015). When governments, non-governmental organizations,

producers, consumers, and other actors in the agri-food sector work together, more effective

regulations, guidelines, and monitoring mechanisms can be created toward safer food. However,

these food control systems are often not feasible in low-resource settings where regulatory

enforcement capacity is weak and food production is highly fragmented and largely based on

small-scale producers (Bari & Yeasmin, 2018; Hoffmann & Jones, 2021; Vipham et al., 2020).

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5.1.1 Complex food safety programs

Food safety is a shared responsibility among many different actors, including governments at all

levels, the agri-food sector, consumers, media, and food safety researchers and practitioners

(WHO, 2021). Alongside measures to improve food control systems, multisectoral food safety

programs often focus on health promotion, incentives for behavioural change, and/or the

enabling environment show promise in addressing food safety risks (Grace, 2017). Such

programs can be considered complex programs14, defined as programs with “several interacting

components” (Moore et al., 2014). The Medical Research Council lists several characteristics of

complex programs, including, but not limited to: the number of components involved; the

number of groups, settings, or levels targeted; and, the level of flexibility of the program

(Skivington et al., 2021).

While multi-component, multisectoral programs in addressing food safety are promising, there

exists limited guidelines supporting their development. Further insights into how complex food

safety programs can best be supported are critical, especially now in the context of climate

change. This article explores strategies complex food safety programs are adopting in order to

support the development of future related programs. To do so, we draw on a case study of an

14 Programs are complex not only because of the properties of the program but also the context into which the

program is introduced (Hawe, 2015; Skivington et al., 2021; Thirsk & Clark, 2017). Context is the pre-existing

conditions, or anything external to the program, that may affect implementation and outcomes. Complexity arises

from the interaction of program components with the context.

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ongoing program aiming to improve food safety in Vietnam. Specifically, our objective is to

examine the experiences of researchers and participants involved in the program to characterize

how we might effectively implement and evaluate complex food safety programs.

5.1.2 Context: Food safety in Vietnam

Understanding how food safety programs in Vietnam work requires an understanding of

Vietnamese food systems. Because many Vietnamese have moved from the status of ‘having

enough food to eat’ to that of ‘needing safe food to eat’ (Nguyen-Viet et al., 2017), food safety

has become one of the most pressing issues among citizens (World Bank, 2016). Repeated

episodes of unsafe food practices receive widespread media attention in Vietnam (Nguyen-Viet

et al., 2017). A particular area of concern is pork safety, the main animal source food in

Vietnamese diets. Pork is often produced by smallholder systems and sold fresh in traditional

‘wet’ markets. Although wet markets are the primary access point for fresh vegetables, fruits,

and meat, wet markets often lack mechanisms for food safety control (Dang-Xuan et al., 2016).

Roles of smallholder pork producers in the pork value chain in Vietnam are gendered. Pig

collection and slaughtering activities are mostly done by men, whereas women are

predominately responsible for pork processing and retail (Mitchell, 2019). Because of gendered

roles, pork producers also have differential access to credit, resources, and agricultural training

(Tran et al., 2018). Research identifying opportunities for increased engagement of women in

agricultural value chains has highlighted constraints to participation, including social norms,

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asset constraints, and time constraints (Quisumbing et al., 2021). Programs aiming to improve

food safety must be responsive to the differential needs of different value chain actors.

In Vietnam, the demand for pork products is increasing but regulatory systems have not been

able to adapt to this change in food consumption (Pham & Dinh, 2020). For example, Vietnam’s

Law on Food Safety (No. 55/2010/QH12) defines regulations for managing regular occurrences

of food safety incidences of food businesses (The National Assembly, 2010). However, these

regulations do not apply to those exempted from business registration such as smallholders

producers (Pham & Dinh, 2020). Food safety policy in Vietnam is gradually shifting from an

inspection-and-enforcement approach to a risk-based approach, a direction that many food

safety programs in low-resource settings are supporting (Nguyen-Viet et al., 2018; WHO, 2021).

Importantly, Vietnamese agriculture is vulnerable to the impacts of climate change, as Vietnam

has experienced and will continue to experience dramatic climate change impacts (Hanh et al.,

2020). Temperature changes, increased extreme weather events, and increased rainfall variability

are already threatening rice and aquaculture production in the Mekong Delta (Anh & Nghiep,

2020). While the impacts of climate change on food production and food security are well

known, knowledge gaps remain in our understanding of how climate change affects food safety

(FAO, 2020; Mbow et al., 2019). As food systems shift, food safety researchers and practitioners

must be cognizant of climate change risks and integrate climate change considerations into

their programming.

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Since February 2019, African Swine Fever (ASF) has caused significant pig deaths across Vietnam.

Consequently, consumer demand for pork initially declined due to fears around food safety.

Once fears settled, the demand for pork rose. However, given the limited supply of pigs, pork

prices more than doubled (e.g. from 40.000 to 100.000 VNĐ per kg) (Chau, 2020). These shifts in

pork production and consumption patterns influence food safety programming in Vietnam. For

example, to maximize economic benefits, many pig farmers would raise heavier pigs, which

creates challenges in following guidelines for safe pork handling (e.g. difficulties lifting heavy pig

carcasses off the floor onto a grid for processing). Additionally, the enhanced biosecurity at pig

farms and slaughterhouses to control ASF limited access to facilities for food security

researchers and practitioners supporting existing food safety programs.

Since January 2020, Vietnam has been responding to COVID-19, which creates additional

challenges and opportunities for food safety programming. One notable challenge is the decline

in attention from local authorities engaged in food safety programming as their priorities shifted

to COVID-19 control. At the same time, pork producers are more concerned about public health

now compared to before the pandemic, improving interest in using personal protective

equipment during pork production (ILRI, 2020).

5.1.3 The SafePORK program

SafePORK is a five-year program (2017-2022) aiming to reduce the burden of foodborne disease

in informal markets of Vietnam through designing, piloting, and evaluating food safety

interventions (Lam et al., 2020). SafePORK builds on a previous five-year program called PigRISK

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(2012-2017) (Lam et al., 2016). There are five core objectives of SafePORK: (1) generate

actionable evidence on the efficacy of approaches for improving pork safety; (2) develop and

test light-touch interventions toward food safety; (3) validate the theory of change for market-

based interventions; (4) identify recommendations for enhanced engagement of pig value chain

actors; and, (5) build capacity in food safety risk communication (Figure 5.1).

SafePORK is guided by One Health, a conceptual framework considered promising for

addressing food safety in low- and middle-income countries (LMICs) (Grace, 2017). Recognizing

that human, animal, and environmental health are inextricably linked, One Health calls for

multiple disciplines to work together on complex health challenges (Zinsstag et al., 2011).

Responding to this call, SafePORK mobilized researchers from different fields and institutions

including veterinary epidemiology (International Livestock Research Institute), public health

(Hanoi University of Public Health), agricultural economics (Vietnam National University of

Agriculture), and farming systems (National Institute of Animal Science). SafePORK also works

with program participants (local authorities, slaughterhouse workers, retailers, market managers)

to shape the direction of the research and actions that follow (Baum et al., 2006).

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Figure 5.1. SafePORK program objectives and their interrelationships.

5.1.4 SafePORK locations

SafePORK takes place in Hung Yen (Red Mekong Delta), Nghe An (Central), and Hoa Binh

(Northwest) provinces (Figure 5.2). All SafePORK study sites were selected to build on previous

activities and relationships (e.g. from PigRISK). Hung Yen and Nghe An provinces represent rural

areas characterized by medium-scale and small-scale pork production systems, respectively. Hoa

Binh is a mountainous province inhabited mostly by ethnic minorities. Ethnic minority groups in

this province typically farm Ban pigs (lợn Bản), which are an Indigenous breed raised on a

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traditional free scavenging feeding system. Undernutrition and stunting are particularly common

among ethnic minority women and children in Vietnam, requiring targeted efforts to reduce

health inequities (World Bank Group, 2019). SafePORK is a program comprised of multiple ‘light-

touch’ interventions addressing community priorities within the three study sites (Lam et al.,

2021).

Figure 5.2. Map showing locations of study sites (Hung Yen, Nghe An, Hoa Binh provinces) and

the capital city of Vietnam (Hanoi).

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5.2 Methods

5.2.1 Data collection and analysis

We developed semi-structured interview guides for researchers and program participants

(Appendix 21). Interviews were conducted between August and September 2021. For SafePORK

researchers, interviews were carried out in English by the lead author (SL). For program

participants, interviews were conducted in Vietnamese by team members (SD-X, TL). Team

members had previous experience conducting qualitative interviews and received further

training from SL before data collection, as well as ongoing support throughout the study.

Participants were selected by team members based on occupation, age, and location, to ensure

a diversity of experiences. Interviews were audio-recorded with verbal informed consent and

varied in duration by group (e.g. 60-120 mins with researchers and 15-20 mins with program

participants).

We conducted a thematic analysis to identify patterns in the data using a deductive approach

(Braun et al., 2018). We paid specific attention to several elements. First, we considered how

context was reported as per guidelines for process evaluations of complex programs (Moore et

al., 2014). Secondly, we explored explicit or implicit mentions of climate change given its

growing impact on food security and other development programs (Lam, et al., 2021; Rowe,

2019; Uitto, 2021). Finally, we considered how differences and similarities in the social identities

of researchers and program participants (e.g. population, age, gender) shaped experiences with

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SafePORK. This approach enabled us to explore how SafePORK is responding to the needs and

priorities of different groups of people.

5.2.2 Data validity and management

As a way of assuring research quality, we kept an audit trail (Appendix 22) of decisions made

and wrote reflective memos. Additionally, the authorship team regularly discussed key themes

to ensure the accuracy of results and interpretation. Coding and analyses were performed using

NVivo© software (QSR International, Burlington, MA, USA).

5.2.3 A note on COVID-19 and ethics

At the time of this study, Vietnam experienced a surge in COVID-19 cases. Due to travel

restrictions, all interviews were conducted remotely via Microsoft Teams or by phone (see

Appendix 23 for notes on the impacts of COVID-19 on data collection). This research was made

possible through collaboration with the coordinators of SafePORK (H-NV, FU) who provided

regular guidance on this work. Additionally, the first author (SL) – and the primary research

instrument – had existing rapport with the SafePORK team as he worked as an evaluation

consultant for SafePORK. The research findings around barriers and facilitators to

implementation were reported separately and used by the team to adjust ongoing activities

(Appendix 24).

Rapport was also pre-established between S-DX, TL, and program participants. As rapport

facilitated access to research participants, the authorship team continually reflected on whether

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interviewees felt they had to participate, especially during a pandemic. All interviewees verbally

provided their informed consent to participate before the interview. Program participants also

received 50.000 VNĐ (approximately US$2.2) as compensation for their time. To protect the

identity of interviewees, while also allowing readers to see the breadth of interviews, we

identified quotations from each interviewee with a number assigned to the interviewee. This

work received research ethics approval from the University of Guelph (20-02-003) and Hanoi

University of Public Health (018-110/DD-YTCC).

5.3 Results

Seven researchers (4 men, 3 women) of the SafePORK team were interviewed. Researchers came

from public health (n=3), agricultural economics (n=3), veterinary science (n=2), and farming

systems (n=1) backgrounds. A total of 23 program participants also participated in an interview.

They included slaughterhouse workers (n=10), retailers (n=9), local authorities (n=3), and market

managers (n=1) from Hung Yen (n=13), Nghe An (n=7), and Hoa Binh provinces (n=3). The

market manager and two out of three local authorities were men. All slaughterhouse workers

interviewed were men and all but one retailer were women. There were two husband-and-wife

teams whereby the husband would process the pork for the wife to sell. Participants worked

their occupation anywhere from two to 35 years and engaged with SafePORK anywhere from

one to three years. Apart from two ethnic minority interviewees in Hoa Binh, all program

participants were the ethnic majority (n=22) (Appendix 25).

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In reviewing factors influencing implementation, we developed three overarching themes that

speak to how complex food safety interventions might be effectively supported: using program

theory to track changes to the program, attuning to climate change, and designing with equity

in mind (Appendix 26).

5.3.1 “We imagine how it can work in practice:” Using program theory to track changes to the program

The experiences of the SafePORK team suggested interventions were strongly influenced by

context (Figure 5.3). Six months after the launch of interventions (August 2020), the team

conducted formative research in Hanoi to identify strategies for improving the uptake of

hygienic practices. The team noted the adoption of practices was quicker in urban areas than

rural areas, likely because consumers there were more aware of food safety concerns. Urban

consumers tend to have greater risk perceptions because of higher reported food safety

incidents in urban regions (Ha et al., 2021). One researcher said: “As long as consumers are

concerned about microbial contamination, slaughterhouse workers and retailers have to do it

[safe practice]” (Interviewee #6). Another researcher, who previously worked on a project

involving Ban pig production in another province (Son La), reflected on how working in Hoa

Binh was easier because local authorities were concerned about Ban pigs. The scale of pork

production operations also influenced interventions. One researcher described difficulties

working in Hung Yen because of larger-scale pig operations compared to Nghe An:

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you can imagine from 2 am to 5 am, they have a few hours to slaughter seven or eight

pigs. So they have to do it quickly. Not like in Nghe An where there is sometimes only

one pig (Interviewee #4).

In response to these contextual factors, adaptations were made to SafePORK interventions. For

example, the program co-invested with slaughterhouse owners in Hung Yen in an additional

grid to facilitate the medium-scale pork processing. In Nghe An, only one grid was considered

necessary for the small-scale pork operations. SafePORK also adjusted engagement strategies. In

Hoa Binh, more time was dedicated to working with ethnic minority communities (often through

a translator) and adapting interventions to respond to priorities of ethnic minority communities

(e.g. focus on Ban pig production rather than slaughterhouse and market improvement). These

actions suggested complex food safety programs require tailoring of activities within specific

program components rather than a one-size-fits-all approach to the entire program. Reflecting

on the ongoing nature of program design, one researcher noted “we have a lot of things to do.”

The flexibility and adaptability of SafePORK led to emergent outcomes. For example, in response

to travel restrictions resulting from ASF control measures, researchers reported they were careful

when entering sites as they could be the vector bringing the virus to the pigs. The inability to

access certain slaughterhouse facilities led the team to focus on other activities such as raising

food safety awareness and improving pork preparation practices of consumers. Shifting the

focus from slaughterhouse workers to other food safety actors was viewed as an important

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strategy for indirectly supporting slaughterhouse workers. The team also reported increased

engagement with local authorities during this time, resulting in the agreement of local

authorities to certify ‘model’ small-scale slaughterhouses (e.g. those that meet some but not all

conditions of the Food Safety Law 2010), which was viewed as a notable achievement.

To track learnings from context, adjustments in program activities, and the emergence of

outcomes, the team reflected on the development of a program theory. To do so, the team used

Theory of Change and Outcome Mapping, two approaches often used within evaluations of

complex health interventions (Lam et al., 2021). One researcher described developing the

program theory to “imagine how it [SafePORK] can work in practice” (Interviewee #1). The

researcher then described using Outcome Mapping to track “changes in knowledge, attitudes,

and practices of value chain actors, and even researchers” identified by the Theory of Change

process. Operationally, monitoring of outcomes – and the strategies and context influencing

outcomes –was conducted after each field visit. According to the team, developing the program

theory using information collected from Theory of Change and Outcome Mapping is helping

them understand how, why, and under what context the program is contributing to safer pork.

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Figure 5.3. Timeline of implementation, key milestones, and barriers of SafePORK.

5.3.2 “When it rains, you have to cover the pork:” Attuning to climate change

When asked whether climate change was a factor influencing implementation, most researchers

believed climate factors had potential impacts on the program but noted evidence was lacking.

At the farm level, some researchers mentioned hearing from farmers that pigs are “more

sensitive and get sick more frequently” (Interviewee #7) from climate variation. To mitigate this

challenge, one local authority in Hung Yen reported some farmers would “do things that are not

needed” (lam những thứ không cần thiết) like using veterinary drugs, which contributed to

production costs and concerns of chemical residues in pork (Interviewee #10).

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Researchers and slaughterhouse workers commented on the impact of heatwaves on pigs and

pork during transportation. One slaughterhouse worker in Hung Yen explained how pigs are

transported using trucks equipped with water sprays to prevent heat stress. Though important

for supporting pigs, he acknowledged such practices were water- and energy-intensive. One

researcher noted it is common for pig carcasses to be transported uncovered and un-chilled on

the backs of motorbikes, especially in mountainous areas of Vietnam (e.g. Hoa Binh).

For slaughterhouse workers, times of drought also created challenges when processing pork.

One slaughterhouse worker in Hoa Binh with 22 years of experience explained because he

sourced water from the mountains, there was sometimes limited water availability, especially

during the dry season. And during periods of extreme flooding, researchers discussed the

possibilities of rain contaminating waterways through run-off from nearby farms. Researchers

reported many slaughterhouse workers used these open water sources to process pig carcasses

and/or clean tools, resulting in increased food safety risks from using contaminated floodwater.

Both retailers and slaughterhouse workers also mentioned that during storms, rain sometimes

blocked travel and prevented pork from reaching consumers. For those without trucks, they “try

to overcome this” (cũng cố gắng để khắc phục) (Interviewee #14) by using tarps to cover the

pork and traveling more carefully. Additionally, researchers reported heavy rain often prevented

them from traveling to the field:

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In Nghe An, Hung Yen, wherever we go, we could access these places to take samples or

discuss with stakeholders or just to do the interventions. For Hoa Binh, this was much

more difficult in the rainy season where there can landslides (Interviewee #9).

For some food safety actors, infrastructure was a factor influencing the extent of impacts from

rain. One slaughterhouse worker with 22 years of experience processing and selling pork

explained: “Rainy weather does not affect much because I work at home with a roof, only when

selling at the market there were impacts (because there are no shelters at this particular

market)” (Trời mưa gió không ảnh hưởng lắm do mình làm ở nhà có mái che, còn chỉ khi bán ở

chợ thì chỗ bán bị ảnh hưởng hơn) (Interviewee #17). Retailers were very careful to avoid getting

rain on the meat because it will “make the meat mushy” (làm nhã hết thịt) (Interviewee #15),

which detracted customers.

Retailers were particularly concerned about how heat spoiled pork faster. For example, one

retailer in Hung Yen with 15 years of experience explained “when the weather is hot, it can make

your meat worse, it is not fresh and beautiful anymore” (như thời tiết oi ả, thì có thể làm miếng

thịt của mình xấu hơn đi, nó không được tươi, đẹp bắt mắt nữa) (Interviewee #15). Retailers also

described how heat made meat ‘wet’ and would use cardboard to help absorb moisture. This

practice was observed by researchers, who emphasized placing meat on cardboard was

unsanitary. The market manager commented on how there were more flies around pork during

hot weather.

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Many researchers also mentioned heatwaves as a possible driver of microbial replication in pork

though could not say whether this driver was from climate change or simply seasonal influences.

One researcher reflected: “In Nghe An, in the summer, we had some days that were too hot. To

keep and maintain the quality of pork it is hard for retailers, they do not have refrigerators to

store the meat” (Interviewee #6). Another researcher explained retailers do not have

refrigerators because of the market infrastructure: “It is not their place. So, they cannot do that”

(Interviewee #9).

Asking questions about climate change revealed SafePORK activities are indirectly contributing

to climate change adaptation. One researcher believed following recommended hygienic

handling practices from SafePORK is one way of adapting to climate change: “if all interventions

are working they will adapt with those [climate] changes well. If hygiene is practiced well,

whatever summer or winter, will still have a good effect on microbiological levels” (8). Recalling a

risk communication activity conducted earlier in 2021, one researcher alluded to the important

role of keeping meat chilled during heatwaves when he stated:

Some small wet markets operate during the afternoon, between 4 to 7 pm. But most wet

markets operate early in the morning. We encouraged consumers to buy the pork early

morning and put it in the refrigerator. So that in the evening they use it for cooking

(Interviewee #2).

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5.3.3 “We always talk about gender in SafePORK:” Attuning to gender equity

Researchers emphasized the importance of designing programs with equity in mind. This view

was also reflected in objective three of SafePORK (ensuring equitable benefits among different

groups). The team stated roles within the pork value chain in Vietnam were highly gendered,

with pork processing viewed as a man’s job, whereas pork retailing was mostly done by women.

Indeed, all slaughterhouse workers interviewed were men and nearly all retailers interviewed

were women. As such, gender intersected with occupation in this context.

After participating in SafePORK, slaughterhouse workers noticed their businesses were doing

better than before, as one slaughterhouse worker in Nghe An with seven years of experience

explained “because customers see [slaughtering practices] directly, it’s clean, they like it, and

they introduce us other customers who buy more pork” (họ nhìn thấy trực tiếp sạch sẽ là họ

thích, họ ủng hộ, giới thiệu khách khác và mua nhiều hơn) (Interviewee #16). Retailers described

how meat is now cleaner, more beautiful, and had less odor than before, helping them attract

more customers. One retailer in Hung Yen shared she used to sell around sold 20 kg of pork per

day, but now she can sell 25-30 kg. Other outcomes reported by both slaughterhouse workers

and retailers included cleanliness of the work area, trust from consumers, and knowledge on

how to maintain hygiene during pork handling.

Slaughterhouse workers and retailers recalled key messages from the training sessions,

highlighting the contributions of SafePORK interventions in building food safety knowledge:

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Prevent knives from rusting… maintain cleanliness… wash pigs before slaughtering (dao

không để chỗ cao ráo nó han rỉ ra… vệ sinh chân tay… tắm cho sạch sẽ đã rồi mới giết mổ)

(Interviewee #21).

Raw and cooked food must be kept separate, or when you are done have to wash the

table (thớt dao đồ sống đồ 183hin phải để riêng, hoặc làm xong đau đấy mình phải rửa

bàn) (Interviewee #25).

Whether knowledge was applied in practice was dependent on certain enabling factors that

differed between food safety actors. For slaughterhouse workers, the convenience of proposed

recommendations was valued. They appreciated how equipment (e.g. grid, table) helped keep

the floor clean and relieved them of “not worrying about borrowing (from others)” (không lo

phải đi mượn) (Interviewee #18). For retailers, having access to water at the market was essential

for applying learned hygienic practices: “now that there’s water I’ll wash my hands, wash the

cutting board, and clean seats, then sell pork without the smell anymore” (có nước là chị rửa tay

sạch sẽ, rửa dao thớt và chỗ ngồi sạch sẽ, sau đấy bán nó không có mùi hôi thối nữa) (Interviewee

#24).

The reasoning behind the adoption of recommended practices slightly differed between food

safety actors. Both slaughterhouse workers and retailers talked about the need to maintain the

cleanliness of facilities to attract customers and protect the quality of pork. For slaughterhouse

workers, adopting safe hygienic practices was a way to protect their health (e.g. from rusty

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knives, dirty water) and the economic well-being of their families. Retailers more often than

slaughterhouse workers emphasized that changing habits was important for protecting

consumers’ health. As, as one retailer explained, “when we make the product clean, people’s

health will be guaranteed when they eat and drink” (mình làm sản phẩm nó sạch sẽ thì người

dân khi họ ăn uống vào sẽ đảm bảo sức khỏe) (Interviewee #16).

Food safety actors also faced unique and similar challenges, resulting from gendered differences

in occupation. Slaughterhouse workers, particularly those in medium-scale pork operations,

faced time pressures from having to process many pigs within a few hours (e.g. 2 am to 5 am).

For retailers we interviewed, time was also a scarce resource. One retailer described how she

could only clean her cutting boards when there were no customers: “I cut pork for this person

first, and when no one has come to buy pork, I bend down to wash quickly before someone

buys pork and I cut it again” (mình cắt cho người này trước, chưa có người đến mua mình cúi

xuống mình rửa lại có người ta mua mình lại cắt tiếp tục) (Interviewee #24). No matter how busy

they were, retailers said they had to practice safe hygiene or they would lose customers.

Slaughterhouse workers tended to work fewer hours compared to retailers. These findings

further suggested different genders provide much labour in pork value chains in Vietnam

(Mitchell, 2019).

Gendered roles in the pork value chain were also a factor in determining exposures to various

risks. Where men mainly worked in slaughterhouses, they reported the need to exercise caution

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with handling knives and preventing contact with dirty water. Because of the open-air market

environment where retailers worked, retailers more frequently than slaughterhouse workers

reported challenges associated with climatic events (e.g. the impact of extreme heat on pork

quality). With ASF, both retailers and slaughterhouse workers worried about sourcing pork/pigs

unaffected by the disease. Understanding these differences in risk exposures helped the team

manage risks faced by different pork value chain actors.

We also explored intra-gender differences between social groups. For example, examining how

gender intersects with ethnicity, we considered whether ethnic majority and ethnic minority men

had differential experiences with the program. While there were only two ethnic minority men

interviewed, it is worth noting that both interviewees reported challenges from heavy rain, while

few ethnic majority men reported facing this challenge. This difference in experiences was

primarily due to geographic reasons. The ethnic minorities SafePORK worked with primarily lived

in mountainous areas where heavy rain often led to poor driving conditions and thus difficulty

transporting pork to the market. Additionally, due to differences in travel restrictions across

geography, ethnic minority men reported the COVID-19 pandemic decreased sales (up to 50%)

while few ethnic majority men reported impacts of COVID-19 on their businesses. Exploring

intra-gender differences between younger and older women, younger women referred to the

same constraints that older women face (e.g. time, such as time resources split between cleaning

and selling pork). However, younger retailers tended to adopt hygienic practices more readily

compared to older retailers likely because younger retailers were more likely to listen to

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SafePORK researchers, many of whom are older or around the same age. Younger retailers also

might not have yet adopted ingrained practices. Identifying these patterns was a strategy to

understand progress toward achieving objective three of SafePORK (ensuring equitable benefits

among different groups).

Paying attention to gender roles also helped the team identify key individuals who can adopt

changes to food safety practices. For example, researchers shared how joint decisions were

made between husband and wife in upgrading their slaughterhouse, particularly in Hung Yen

and Nghe An. In this case, researchers emphasized the need to exchange ideas about the

intervention with both the husband and wife to improve uptake with the intervention.

When asked whether SafePORK contributed to behavioural changes in food safety practice,

slaughterhouse workers and retailers acknowledged the role of training, equipment, and

interactions with and reminders from the team. However, given the many changes to context

(e.g. ASF, COVID-19) during the duration of SafePORK programming, SafePORK was likely one of

many factors involved. One retailer in Hung Yen with 10 years of experience alluded to

economic development and shifting consumption patterns when she shared: “Before, I sold of

whatever quality is okay, but now everyone’s life is better, people have to eat clean” (tại vì trước

thì mình bán tào lao thế nào cũng được, chứ bây giờ cuộc sống của mỗi người nó một khá lên)

(24). These economic factors contributed to the adoption of safe food practices among different

food safety actors. In other ways, contextual factors affected different groups differently. For

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example, the work in slaughterhouses remained relatively unchanged during COVID-19. In

contrast, many retailers stressed the importance of handwashing and sanitizing liquid for

protecting their health and community health since COVID-19. Both COVID-19 prevention

measures and SafePORK food safety measures focused on proper hand hygiene. SafePORK also

started communicating how handwashing was not only needed to address COVID-19 but was an

important step in preventing food-borne disease. Understanding change processes as

contextual was helpful for the team in engaging with the context-specific realities of various

food safety actors.

5.4 Discussion

The increasing complexity of food security programs due to climate change and other

contextual factors introduces challenges for evaluation (Hendriks, 2020). In this paper, we add to

the limited evidence base on assessments of complex food safety programs through an analysis

of an ongoing program in Vietnam aiming to reduce foodborne diseases in informal markets.

We show how using program theory, attuning to climate change, and attuning to gender equity

are potential strategies for evaluating programs characterized by complexity. Many of these

evaluation strategies align with solutions proposed for a more sustainable and just food systems

transformation (Queiroz et al., 2021).

Guidance for considering context within public health intervention research encourages asking

“how does the intervention interact with its context?” at each phase of the intervention research

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(Skivington et al., 2021). However, in settings where external factors may change rapidly,

monitoring of context on an ongoing basis will be critical. Additionally, because complex

programs can have components with varying levels of complexity (Foran et al., 2014), different

program components will likely require different evaluations. In SafePORK, conventional

approaches to evaluation are being applied to assess components relatively unaffected by

context. For example, risk assessments in SafePORK aim to provide an estimate of risks to

human health at a particular point in time; because the nature and purpose of these

assessments are quite straightforward, the team is measuring changes in risk by comparing

baseline and endline risk estimates. Conversely, risk management involves identifying,

implementing, and monitoring control measures over a longer period. For risk management and

other multidimensional components, the team finds it helpful to develop a program theory,

which provides a structure for identifying and tracking influences from changing contexts on

program components in real-time. Of note, developing a program theory is one of many

strategies for considering context. Another promising strategy for assessing program context

change – though not used in our study – is to explore how context relates to constructs of

complexity theory (e.g. emergence, feedback, self-organization) (Bleecker et al., 2021).

An important contextual factor contributing to program complexity and uncertainty is climate

change. Although the integration of climate considerations into program planning and

evaluation within development contexts is increasingly encouraged (Rowe, 2019; Ssekamatte,

2018; Uitto 2019), the impacts of climate change on food security programs remain overlooked

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(Lam et al., 2021). Our findings showed asking questions about climate change – for a food

safety program where climate action was not an explicit objective – helped to uncover climate

vulnerabilities and adaptation strategies, highlighting the importance of climate change

mainstreaming in evaluation. Furthermore, research on the impact of climate change on food

safety has typically focused on the end food product (Fanzo et al., 2021); an important

contribution of this study is how intermediary links within the food value chain (e.g. processing,

retailing) are influenced by climate change, which can support programs aiming for more

holistic action toward food safety.

The social context in which programs are implemented is another critical dimension in

evaluations. For example, climate change will continue to have a disproportionate impact on

certain groups of people (Mbow et al., 2019). As our findings revealed, retailers reported

experiencing more severe disruptions to their livelihoods from climate change compared to

slaughterhouse workers. Additionally, food safety actors can have different rationales for

participating in food security programs. Feminist evaluators have acknowledged “there is

tremendous but largely untapped potential for evaluation to deepening understanding around

gender inequities” (Hay, 2012, p. 337). Our study examined program mechanisms – understood

as the reasoning and responses of participants – that produced intended program outcomes by

asking “how did the program contribute to change?” (Dalkin et al., 2015). In doing so, we

contributed an example of how gender considerations can go beyond simply reporting

outcomes for different groups of people to include reporting on program mechanisms (Dalkin et

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al., 2015; Lam et al., 2019). We suggest understanding program mechanisms can facilitate the

tailoring of food safety interventions toward equitable outcomes.

Importantly, food security challenges differ between ethnic majority and minority communities.

For example, extended maternity leave and restricted infant formula advertising are policies

designed to address Vietnam’s low breastfeeding rates. While seen as a major accomplishment

for the nutrition community, these policies target women working in the formal sector and thus

do not address issues faced by most ethnic minority women (Harris et al., 2021). As in Tavenner

& Crane (2019), applying intersectionality to an agricultural systems context, analyzing intra-

group differences helped identify factors that shape vulnerability. Programs should take into

account the particular needs and priorities of marginalised ethnic minority groups to address

determinants of food insecurity. Additionally, evaluations need to be sensitive to women’s and

men’s heterogeneity and pay attention to the differences in social positions.

We suggested several areas for future research. First, analyzing trade-offs and co-benefits

between economic productivity and safe food handling practices will be important for

identifying sustainable food safety pathways (Antle & Valdivia, 2021; Foran et al., 2014). For

example, food safety practices such as handwashing and cleaning work areas are being adopted

but maintaining these practices is not easy when slaughterhouse workers need to process pork

quickly or when retailers are dealing with multiple customers at once. Secondly, smallholder

producers are increasingly affected by government policies aiming to formalize, centralize, and

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intensify pork production systems. Given the potential public health, environmental, and animal

welfare impacts of industrialization of food animal production in low- and middle-income

countries (Lam et al., 2019), there is a need to continue legitimatizing and supporting informal

markets. As this study demonstrated, food safety actors were supportive of risk management

practices. Continuing to develop alternative approaches to reduce food safety risks – e.g. via

capacity building, adoption incentives, and an enabling environment – is important for

supporting the livelihoods of food safety actors and community food safety. Finally, such

programs often call for multidisciplinarity; however, the process and outcomes of

multidisciplinary collaborations are not well examined within food security contexts (Gaihre et

al., 2019; Lam, et al., 2019; Nguyen-Viet et al., 2021). To enhance multidisciplinary collaborations

toward food security under a changing climate, future research should continue exploring

strategies for working across disciplines and sectors in this area.

5.4.1 Limitations

We note a couple of limitations of our study. First, retailers and slaughterhouse workers largely

shared positive feedback, likely due to familiarity with the interviewer. After the interviewers

made this observation, interviewers reminded participants to openly share feedback on both

what worked well and what could be done better, so that the SafePORK team can better plan

future programming activities. Furthermore, additional questions were added to the interview

guide to probe for suggestions for improvement. Secondly, because interviews were conducted

remotely, many program participants were joining the interview from their homes. Children,

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customers, pets, and/or livestock sometimes created background noise that interrupted the flow

of the interview. Despite these limitations, this research enhanced our understanding of how

complex food safety programs could be effectively implemented and evaluated.

5.5 Conclusion

As food safety is a shared responsibility among many different actors in the agri-food sector,

complex programs – those that have multiple interacting components at multiple levels – are

often key to achieving desired food safety outcomes. However, complex food safety programs

are often challenging to evaluate and learn from, especially now given additional complexities

introduced by the changing climate. This study explored the experiences of the researchers and

program participants involved in an ongoing program aiming to reduce foodborne diseases in

Vietnam. Using program theory, attuning to climate change, and ensuring inclusivity were

identified as key strategies for implementing and evaluating complex food safety programs.

Although findings from this research are specific to Vietnam, these strategies can inform

contexts where researchers and evaluators are looking to measure the outcomes of multisector,

multicomponent programs operating under a changing climate.

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5.6 References

Anh, D.T., Nghiep, P. C. (2020). New challenges for food security in Vietnam.

Antle, J. M., & Valdivia, R. O. (2021). Trade-off analysis of agri-food systems for sustainable

research and development. Q Open. https://doi.org/10.1093/qopen/qoaa005

Bari, M. L., & Yeasmin, S. (2018). Foodborne Diseases and Responsible Agents. In Food Safety

and Preservation. https://doi.org/10.1016/b978-0-12-814956-0.00008-1

Baum, F., MacDougall, C., & Smith, D. (2006). Participatory action research. Journal of

Epidemiology and Community Health, 60(10), 854–857.

https://doi.org/10.1136/jech.2004.028662

Bleecker, L., Sauveplane-Stirling, V., Di Ruggiero, E., & Sellen, D. (2021). Evaluating the

integration of strategic priorities within a complex research-for-development funding

program. Evaluation and Program Planning.

https://doi.org/10.1016/j.evalprogplan.2021.102009

Braun, V., Clarke, V., Hayfield, N., & Terry, G. (2018). Thematic analysis. In P. Liamputtong (Ed.),

Handbook of Research Methods in Health Social Sciences.

Chau, H. (2020). Scarcity sends Vietnam pork prices to 20-year high. VN Express.

https://e.vnexpress.net/news/business/industries/scarcity-sends-vietnam-pork-prices-to-

20-year-high-4103700.html

Craig, P., Di Ruggiero, E., Frohlich, K. L., Mykhalovskiy, E., & White, M. (2018). Taking account of

context in population health intervention research: guidance for producers, users and funders

of research.

Dalkin, S. M., Greenhalgh, J., Jones, D., Cunningham, B., & Lhussier, M. (2015). What’s in a

mechanism? Development of a key concept in realist evaluation. Implementation Science.

https://doi.org/10.1186/s13012-015-0237-x

Dang-Xuan, S., Nguyen-Viet, H., Meeyam, T., Fries, R., Nguyen-Thanh, H., Pham-Duc, P., Lam, S.,

Grace, D., & Unger, F. (2016). Food safety perceptions and practices among smallholder

pork value chain actors in Hung Yen Province, Vietnam. Journal of Food Protection.

https://doi.org/10.4315/0362-028X.JFP-15-402

Fanzo, J., Bellows, A. L., Spiker, M. L., Thorne-Lyman, A. L., & Bloem, M. W. (2021). The

importance of food systems and the environment for nutrition. American Journal of Clinical

Nutrition. https://doi.org/10.1093/ajcn/nqaa313

194

Fanzo, J., Covic, N., Dobermann, A., Henson, S., Herrero, M., Pingali, P., & Staal, S. (2020). A

research vision for food systems in the 2020s: Defying the status quo. Global Food Security.

https://doi.org/10.1016/j.gfs.2020.100397

FAO, IFAD, UNICEF, W. and W. (2021). The State of Food Security and Nutrition in the World 2021.

FAO. (2020). Climate change: Unpacking the burden on food safety.

Foran, T., Butler, J. R. A., Williams, L. J., Wanjura, W. J., Hall, A., Carter, L., & Carberry, P. S. (2014).

Taking complexity in food systems seriously: An interdisciplinary analysis. World

Development, 61, 85–101. https://doi.org/10.1016/j.worlddev.2014.03.023

Gaihre, S., Kyle, J., Semple, S., Smith, J., Marais, D., Subedi, M., & Morgan, H. (2019). Bridging

barriers to advance multisector approaches to improve food security, nutrition and

population health in Nepal: transdisciplinary perspectives. BMC Public Health.

https://doi.org/10.1186/s12889-019-7204-4

Grace, D. (2017). Food safety and the Sustainable Development Goals.

Ha, T. M., Shakur, S., & Pham Do, K. H. (2021). Food risk in consumers’ eye and their

consumption responses: evidence from Hanoi survey. Journal of Asian Business and

Economic Studies. https://doi.org/10.1108/jabes-12-2019-0126

Harris, J., Huynh, P., Nguyen, H. T., Hoang, N., Mai, L. T., Tuyen, L. D., & Nguyen, P. H. (2021).

Nobody left behind? Equity and the drivers of stunting reduction in Vietnamese ethnic

minority populations. Food Security. https://doi.org/10.1007/s12571-021-01183-7

Havelaar, A. H., Kirk, M. D., Torgerson, P. R., Gibb, H. J., Hald, T., Lake, R. J., Praet, N., Bellinger, D.

C., de Silva, N. R., Gargouri, N., Speybroeck, N., Cawthorne, A., Mathers, C., Stein, C., Angulo,

F. J., Devleesschauwer, B., Adegoke, G. O., Afshari, R., Alasfoor, D., … Zeilmaker, M. (2015).

World Health Organization Global Estimates and Regional Comparisons of the Burden of

Foodborne Disease in 2010. In PLoS Medicine.

https://doi.org/10.1371/journal.pmed.1001923

Hawe, P. (2015). Lessons from Complex Interventions to Improve Health. Annual Review of Public

Health, 36(1), 307–323. https://doi.org/10.1146/annurev-publhealth-031912-114421

Hay, K. (2012). Engendering Policies and Programmes through Feminist Evaluation:

Opportunities and Insights. Indian Journal of Gender Studies, 19(2), 321–340.

https://doi.org/10.1177/097152151201900208

Hendriks, S. (2020). Food security policy, evaluation and impact assessment. Earthscan.

195

Hoffmann, V., & Jones, K. (2021). Improving food safety on the farm: Experimental evidence from

Kenya on incentives and subsidies for technology adoption. World Development.

https://doi.org/10.1016/j.worlddev.2021.105406

ILRI. (2020). Can COVID-19 spur transformations in food safety in traditional Vietnamese pork

value chains? https://www.ilri.org/news/can-covid-19-spur-transformations-food-safety-

traditional-vietnamese-pork-value-chains

Lam, S., Nguyen, H.T.T., Nguyen-Viet, H., Unger, F. (2020). Mapping pathways toward safer pork in

Vietnam.

Lam, S., Barot, M., Nguyen-Viet, H., & Unger, F. (2016). Changes in researcher capacity in

assessing food safety risks and value chains: Insights from PigRisk team. ILRI. Hanoi.

Lam, S., Dodd, W., Whynot, J., & Skinner, K. (2019). How is gender being addressed in the

international development evaluation literature? A meta-evaluation. Research Evaluation,

28(2), 158–168. https://doi.org/10.1093/reseval/rvy042

Lam, S., Nguyen, H. T. T., Tuan, H. N. H., Nguyen, L. T., Nguyen-Viet, H., Toribio, J.-A., Thanh, H. L.

T., Pham-Van, H., Grace, D., & Unger, F. (2021). Unpacking the Theory Behind One Health

Food Safety Programs : A Vietnam Case Study. Frontiers in Veterinary Science, 8(December),

763410. https://doi.org/10.3389/fvets.2021.763410

Lam, S., Dodd, W., Berrang-Ford, L., Ford, J., Skinner, K., Papadopoulos, A., & Harper, S. L. (2021).

How are climate actions evaluated? A review of United Nations food security evaluations. In

Global Food Security. https://doi.org/10.1016/j.gfs.2021.100509

Lam, S., Dodd, W., Wyngaarden, S., Skinner, K., Papadopoulos, A., & Harper, S. L. (2021). How and

why are Theory of Change and Realist Evaluation used in food security contexts? A scoping

review. Evaluation and Program Planning, 89(September), 102008.

https://doi.org/10.1016/j.evalprogplan.2021.102008

Lam, S., Thompson, M., Johnson, K., Fioret, C., & Hargreaves, S. K. (2019). Toward community

food security through transdisciplinary action research. Action Research.

https://doi.org/10.1177/1476750319889390

Lam, Y., Fry, J. P., & Nachman, K. E. (2019). Applying an environmental public health lens to the

industrialization of food animal production in ten low- A nd middle-income countries.

Globalization and Health. https://doi.org/10.1186/s12992-019-0479-5

Mbow, C., Rosenzweig, C., Barioni, L. G., Benton, T. G., Herrero, M., Krishnapillai, M., Liwenga, E.,

Pradhan, P., Rivera-Ferre, M. G., Sapkota, T., Tubiello, F. N., & Xu, Y. (2019). Food Security. In

196

P. Z. P.R. Shukla, J. Skea, E. Calvo Buendia, V. Masson-Delmotte, H.-O. Pörtner, D.C. Roberts,

J. P. P. R. Slade, S. Connors, R. van Diemen, M. Ferrat, E. Haughey, S. Luz, S. Neogi, M.

Pathak, J. Petzold, & J. M. P. Vyas, E. Huntley, K. Kissick, M. Belkacemi (Eds.), Climate Change

and Land: an IPCC special report on climate change, desertification, land degradation,

sustainable land management, food security, and greenhouse gas fluxes in terrestrial

ecosystems.

Mitchell, M. E. V. (2019). A review of the literature: gender, food safety and the pork value-chain in

Vietnam.

Moore, G., Audrey, S., Barker, M., Bond, L., Bonell, C., Cooper, C., Hardeman, W., Moore, L.,

O’Cathain, A., Tinati, T., Wight, D., & Baird, J. (2014). Process evaluation in complex public

health intervention studies: The need for guidance. In Journal of Epidemiology and

Community Health. https://doi.org/10.1136/jech-2013-202869

Nguyen-Viet, H., Grace, D., Pham-Duc, P., Dang-Xuan, S., Luu-Quoc, T., Unger, F., de Vlieger, S.,

Pham-Thi, N., Duong-Van, N., Nguyen-Hung, L., Tran-Dinh, L., & Tuyet-Hanh, T. T. (2018).

Research and training partnership to assist policy and capacity building in improving food

safety in Vietnam. In Global Food Security. https://doi.org/10.1016/j.gfs.2018.08.009

Nguyen-Viet, H., Pham, G., Lam, S., Pham-Duc, P., Dinh-Xuan, T., Jing, F., Kittayapong, P.,

Adisasmito, W., Zinsstag, J., & Grace, D. (2021). International, Transdisciplinary, and

Ecohealth Action for Sustainable Agriculture in Asia. Frontiers in Public Health.

https://doi.org/10.3389/fpubh.2021.592311

Nguyen-Viet, H., Tuyet-Hanh, T. T., Unger, F., Dang-Xuan, S., & Grace, D. (2017). Food safety in

Vietnam: Where we are at and what we can learn from international experiences. In

Infectious Diseases of Poverty (Vol. 6, Issue 1). https://doi.org/10.1186/s40249-017-0249-7

Pham, H. V., & Dinh, T. L. (2020). The Vietnam’s food control system: Achievements and

remaining issues. Food Control. https://doi.org/10.1016/j.foodcont.2019.106862

Queiroz, C., Norström, A. V., Downing, A., Harmáčková, Z. V., De Coning, C., Adams, V., Bakarr,

M., Baedeker, T., Chitate, A., Gaffney, O., Gordon, L., Hainzelin, É., Howlett, D., Krampe, F.,

Loboguerrero, A. M., Nel, D., Okollet, C., Rebermark, M., Rockström, J., … Matthews, N.

(2021). Investment in resilient food systems in the most vulnerable and fragile regions is

critical. In Nature Food. https://doi.org/10.1038/s43016-021-00345-2

Quisumbing, A., Heckert, J., Faas, S., Ramani, G., Raghunathan, K., Malapit, H., Malapit, H.,

Heckert, J., Eissler, S., Faas, S., Martinez, E., Myers, E., Pereira, A., Quisumbing, A., Ragasa, C.,

Raghunathan, K., Rubin, D., & Seymour, G. (2021). Women’s empowerment and gender

197

equality in agricultural value chains: evidence from four countries in Asia and Africa. Food

Security. https://doi.org/10.1007/s12571-021-01193-5

Rowe, A. (2019). Sustainability-Ready Evaluation: A Call to Action. New Directions for Evaluation,

2019(162), 29–48. https://doi.org/10.1002/ev.20365

Skivington, K., Matthews, L., Simpson, S. A., Craig, P., Baird, J., Blazeby, J. M., Boyd, K. A., Craig, N.,

French, D. P., McIntosh, E., Petticrew, M., Rycroft-Malone, J., White, M., & Moore, L. (2021). A

new framework for developing and evaluating complex interventions: Update of Medical

Research Council guidance. The BMJ. https://doi.org/10.1136/bmj.n2061

Ssekamatte, D. (2018). The role of monitoring and evaluation in climate change mitigation and

adaptation interventions in developing countries. African Evaluation Journal, 6(1).

https://doi.org/10.4102/aej.v6i1.254

Tavenner, K., & Crane, T. A. (2019). Beyond “women and youth”: Applying intersectionality in

agricultural research for development. Outlook on Agriculture.

https://doi.org/10.1177/0030727019884334

The National Assembly. (2010). Law No. 55/2010/QH12. https://vanbanphapluat.co/law-no-55-

2010-qh12-of-june-17-2010-on-food-safety

The World Bank. (2016). Vietnam Food Safety Risks Management Challenges and Opportunities.

Thirsk, L. M., & Clark, A. M. (2017). Using Qualitative Research for Complex Interventions: The

Contributions of Hermeneutics. International Journal of Qualitative Methods.

https://doi.org/10.1177/1609406917721068

Tran, T. K. Van, Elahi, E., Zhang, L., Abid, M., Pham, Q. T., & Tran, T. D. (2018). Gender differences

in formal credit approaches: rural households in Vietnam. Asian-Pacific Economic Literature.

https://doi.org/10.1111/apel.12220

Tuyet Hanh, T. T., Huong, L. T. T., Huong, N. T. L., Linh, T. N. Q., Quyen, N. H., Nhung, N. T. T., Ebi,

K., Cuong, N. D., Van Nhu, H., Kien, T. M., Hales, S., Cuong, D. M., Tho, N. T. T., Toan, L. Q.,

Bich, N. N., & Van Minh, H. (2020). Vietnam Climate Change and Health Vulnerability and

Adaptation Assessment, 2018. Environmental Health Insights.

https://doi.org/10.1177/1178630220924658

Uitto, J.I. (2021). Evaluating Environment in International Development. Routledge.

Uitto, Juha I. (2019). Sustainable Development Evaluation: Understanding the Nexus of Natural

and Human Systems. New Directions for Evaluation, 2019(162), 49–67.

198

https://doi.org/10.1002/ev.20364

Vipham, J. L., Amenu, K., Alonso, S., Ndahetuye, J. B., Zereyesus, Y., Nishimwe, K., Bowers, E.,

Maier, D., Sah, K., Havelaar, A., & Grace, D. (2020). No food security without food safety:

Lessons from livestock related research. In Global Food Security.

https://doi.org/10.1016/j.gfs.2020.100382

WHO. (2021). Draft WHO global strategy for food safety 2022-2030.

World Bank Group. (2019). Persistent Malnutrition in Ethnic Minority Communities of Vietnam :

Issues and Options for Policy and Interventions.

Zinsstag, J., Schelling, E., Waltner-Toews, D., & Tanner, M. (2011). From “one medicine” to “one

health” and systemic approaches to health and well-being. Preventive Veterinary Medicine.

https://doi.org/10.1016/j.prevetmed.2010.07.003

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CHAPTER 6: HOW THE WORLD WILL MEASURE PROGRESS ON THE PARIS CLIMATE AGREEMENT AND KEEP COUNTRIES ACCOUNTABLE

Climate change is a global problem that knows no national borders

[https://www.un.org/sustainabledevelopment/blog/2015/11/climate-change-knows-no-

national-borders-un-chief-says]. All countries will have to work together and take bold actions

to reduce greenhouse gas emissions and demonstrate that their emissions are declining if we

are to meet the Paris Agreement goal of keeping the global temperature rise to no more than

1.5 C above pre-industrial levels [https://unfccc.int/process-and-meetings/the-paris-

agreement/the-paris-agreement].

To achieve any goal, targets must be set and progress measured. When it comes to climate

change, that assessment is called the “global stocktake”

[https://unfccc.int/topics/science/workstreams/global-stocktake-referred-to-in-article-14-of-

the-paris-agreement]. The stocktake, which will occur every five years beginning in 2023, takes a

look at the collective progress the world’s nations have made on climate action.

Several reports [https://unfccc.int/news/climate-commitments-not-on-track-to-meet-paris-

agreement-goals-as-ndc-synthesis-report-is-published] have found that countries’ climate

pledges (called nationally determined contributions, or NDCs) [https://unfccc.int/process-and-

meetings/the-paris-agreement/nationally-determined-contributions-ndcs/nationally-

determined-contributions-ndcs/ndc-synthesis-report] aren’t ambitious enough to meet the

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goals of the Paris Agreement. Even if current pledges are achieved, there are few ways to further

reduce emissions after 2030 quickly enough to limit global warming to 1.5 C. The expert

reviewers for the reports published by the Intergovernmental Panel on Climate

Change [https://www.ipcc.ch/reports] say strong, rapid and sustained emissions reductions

would limit global warming and prevent the worst climate impacts.

When country representatives gather at the United Nations climate conference (COP26) in

Glasgow, Scotland, in November 2021, they will finalize the plans for the global stocktake —

how the parties to the agreement will measure and report their climate actions — so they can

then strengthen their own country’s climate pledges.

6.1 Where are we?

Article 14 [https://unfccc.int/topics/science/workstreams/global-stocktake-referred-to-in-article-

14-of-the-paris-agreement] of the Paris Agreement offers some information about what the

global stocktake might look like, but falls short in naming specific accountability and reporting

mechanisms.

That’s a bit like working together on a community garden to grow healthy food without those

involved agreeing upon some clear ground rules, such as how plots are assigned, which crops

are appropriate and how to make the garden thrive.

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Five-year submission cycle for Nationally Determined Contributions, and how the global stocktake influences

them. (Authors, adapted from UNFCCC 2016 [https://unfccc.int/process-and-meetings/the-paris-agreement/nationally-

determined-contributions-ndcs/nationally-determined-contributions-ndcs])

The 191 parties (190 countries plus the European Union) aren’t without some guidance,

however. At the COP24 meeting in Katowice, Poland, in 2019, they agreed on a three-phase

process [https://www.wri.org/insights/how-will-paris-agreements-global-stocktake-work] for the

stocktake.

1. Information collection and preparation.

2. Technical assessment.

3. Communicating and acting on findings.

This process does not specify what data are needed and in what format. The absence of a

harmonized approach to data collection, and the fragmented evidence that comes with that, will

constrain our ability to measure progress.

6.2 How are we doing?

Some countries [https://www.climate-chance.org/en/comprehend/global-synthesis-report-on-

local-climate-action], such as Germany and Canada, are already producing progress reports on

climate action. But it is unlikely all these reports will be in a format that allows them to be

compared, which is important for aggregating findings and answering the question: How are we

collectively doing?

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Establishing reporting mechanisms is nothing new. Guidelines

exist [https://www.undp.org/content/dam/LECB/docs/pubs-reports/undp-wri-ndcsp-ndc-

enhancement-report-2019] to help governments structure their nationally determined

contributions, which feed into the NDC Synthesis [https://unfccc.int/process-and-meetings/the-

paris-agreement/nationally-determined-contributions-ndcs/nationally-determined-

contributions-ndcs/ndc-synthesis-report], a report that provides an overview of national climate

ambitions. Similar guidelines for reporting on national climate actions are essential to support

the global stocktake.

For efforts to reduce emissions, also called mitigation, one way of determining success is by

measuring the size of the emission reductions. But it’s unclear if a comparable method exists to

measure efforts to respond to and manage actual or expected climate and its effects, called

adaptation.

The global goal on adaptation [https://unfccc.int/news/the-adaptation-committee-considers-

methods-to-review-the-global-goal-on-adaptation], such as enhancing the capacity to adapt,

strengthening resilience and reducing vulnerability to climate change, is vague, leading to

challenges in measuring its success [ https://unfccc.int/documents/268841].

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Green roofs, like this one in the Netherlands, can reduce heat transfer through the building roof, improving comfort

inside and reducing heat stress from heat waves. (Shutterstock)

When governments make decisions about addressing climate change, they often overlook how

they will measure climate progress. In his 2021 executive

order [https://www.whitehouse.gov/briefing-room/presidential-actions/2021/01/27/executive-

order-on-tackling-the-climate-crisis-at-home-and-abroad] on tackling the climate crisis, U.S.

President Joe Biden noted that agencies will develop “climate action plans and data and

information products to improve adaptation” without elaborating on how those plans will be

evaluated.

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The limited attention to climate action measurement risks poorly understanding progress on

climate action and designing subsequent climate targets that miss the mark.

6.3 Collecting and preparing information

UN agencies often conduct evaluations to measure outcomes of their programs. We

recently reviewed UN evaluation reports published from 2014 to

2019 [https://doi.org/10.1016/j.gfs.2021.100509] to assess how climate change was accounted

for in programs intended to bolster food security — the availability of food and access to it.

Climate change — including increasing temperatures, changing rainfall patterns and a greater

risk of extreme weather — has strong negative effects on crop yields and livestock health.

Our review provided insights into how food security programs are managed and how the results

are measured in the context of climate change. We identified three things countries can do now

to prepare for the stocktake.

Build strong monitoring and evaluation systems for climate action. Credible data systems need

to be put in place, developed and sustained. Monitoring and evaluation specialists require

training. Training must also extend to decision-makers who use the information.

Measure climate action. Although a program may not have intentionally addressed climate

change, some activities may have contributed to unexpected outcomes. One study of a rural

development project in

Morocco [https://www.ifad.org/documents/38714182/39736369/pdrzmh_ppa_e.pdf/b70c0bb6-

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dc4a-47e8-8ba2-d5249daa8da9?version=2.0] noted that while nothing was specifically done to

improve the climate resilience of farmers, efforts to protect water, soil and vegetation cover did

have that effect.

Concern for climate change may not be enough to catalyze support to implement more

ambitious climate mitigation and adaptation efforts. Documenting additional benefits for health,

ecosystems and economy, also called co-benefits [https://www.ipcc.ch/report/ar5/wg2/human-

health-impacts-adaptation-and-co-benefits], can increase interest in taking climate action.

Integrate climate measures into programs that are at risk of the impacts of climate change, such

as planning for climate impacts or incorporating climate resilience training. Unpacking the

pathway by which climate change influences programs can help identify entry points for

mitigating those climate impacts. For example, a study in El Salvador that focused on the

management of natural resources, including vegetation cover and soil quality

[http://www.fao.org/3/ca5009en/CA5009EN], spelled out how farmers could improve their

management practices and how adaptation might support this goal.

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CHAPTER 7: CONCLUSION

7.1 Reflecting on the journey

My professional experiences in evaluation have largely centered on food security contexts,

contributing to my interest in research at the intersection of food security and evaluation.

Initially, my dissertation focused on co-developing and co-evaluating a community-based

monitoring system for Indigenous food security in Uganda in collaboration with the Indigenous

Health Adaptation to Climate Change (IHACC) team and communities. I was introduced to the

IHACC project through my advisors (Drs. Sherilee Harper and Warren Dodd) who are principal

investigators and collaborators of the program. The first research chapter (Chapter 2) reviewed

community-based food security monitoring systems globally, contributing to research objective

1 (characterize how food security is monitored under a changing climate). Learnings from this

chapter were intended to provide a scaffolding foundation for co-developing and co-evaluating

community-based monitoring systems in Chapter 3 and subsequent chapters. However, when it

came time for community collaboration in January 2019, there were Ebola cases reported in the

Democratic Republic of the Congo in areas near the Ugandan border (and near the IHACC

project location). The travel restrictions, uncertainties, and risks presented by Ebola encouraged

me to explore existing food security program evaluation efforts rather than support the

development of a new food security program. The review of food security monitoring programs

presented in Chapter 2 found there was a limited number of evaluations considered climate

change indicators. This review established a basis for exploring the ways in which evaluations

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can better measure and encourage climate action outcomes. As such, my dissertation aimed to

enhance evaluations primarily by learning from past evaluations of food security programs

rather than developing and evaluating a food security program.

For Chapter 3, I developed and applied a tool assessing climate change integration into food

security program evaluation, contributing to research objective 2 (assess how food security

evaluations are considering climate change). Because United Nations agencies often measure the

outcomes of their development programs, I drew on United Nations food security evaluation

reports as a case study. A key finding was the supportive role of program theories in thinking

through how food security programs – and measures used to assess them – can respond to

climate change. While program theories show promise in supporting food security programs

operating under climate change, it was unclear how and under what circumstances theory-

driven evaluation should be used.

To address this knowledge gap, Chapter 4 reviewed common theory-driven approaches to

evaluation, contributing to research objective 3 (characterize the use of theory-driven evaluation

in food security contexts). This study found that theory-driven evaluations respond to different

evaluation challenges; for example, Theories of Change were often developed to address the

need to evaluate programs operating under complexity while Realist Evaluation was generally

used to understand outcomes of programs. Additionally, Chapter 4 highlighted how reflecting

on context can further shape the design of the evaluation.

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The important role of the context in shaping the evaluation raised the question: How are food

security program evaluations responding to context? Chapter 5 presented a qualitative study

exploring the perspectives and experiences of researchers and community members engaged in

a food security program in Vietnam (SafePORK), contributing to objective 4 (capture lessons

learned from designing and evaluating complex food security programs). This chapter explored

how climate change and other contextual factors influence the implementation and evaluation

of SafePORK. My existing connection to SafePORK – as a contracted evaluation consultant for

the program during my PhD studies – was critical in getting support for this research. Because

the program is ongoing, the study findings are timely for informing ongoing programming. A

key finding was that asking about climate change – in a program where climate action was not

an explicit/implicit objective – yielded important entry points for future climate responses.

The practice-based chapter in this dissertation, Chapter 6, was written for a public audience (The

Conversation Canada) to broadly disseminate research findings from this dissertation. A key

message amplified in this piece was the importance of measuring climate action outcomes.

Importantly, it provided insights into how we can support this measurement, drawing on

findings from Chapter 3. This news article was timely considering the rapidly approaching global

2023 climate change stocktake – a mandatory step of the Paris Agreement assessing collective

progress toward long-term climate goals – and the need for countries to prepare information

for the stocktake. Additionally, the piece expanded on how developing a program theory can

help identify entry points for mitigating climate impacts, thus bridging Chapters 3 and 4.

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7.2 Synthesis of findings

Exploring the intersection of food security, climate change, and evaluation, findings across all

four research chapters (2-5) point to the importance of 1) exploring program theory in

evaluations of complex food security programs; 2) considering gender and other social

identities; and, 3) considering climate change (Figure 7.1).

Figure 7.1. Visual representation of key findings from this dissertation.

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7.2.1 Exploring program theory in food security program evaluation

Underscoring much of this dissertation is the role of program theory in developing and

evaluating complex food security programs. As suggested in Chapter 4, theory-driven evaluation

places a focus on the assumptions underlying the linkages between food security outcomes and

activities. In identifying the causal relationships thought to be of greatest importance to the

program’s success, program theories help to prioritize data collection and analysis. This step is

particularly helpful for programs with multiple components and thus multiple potential

pathways toward food security outcomes (Hendriks, 2020).

Program theories should also contain information about contextual factors expected to

influence causal relationships. This information provides a structure for identifying and

addressing potential challenges for implementation. For example, in Chapter 3, thinking about

the climate context can help conceptualize pathways toward climate-responsive food security

outcomes (e.g. UNEP, 2016; Howland, 2019; Béné et al., 2020). Finding ways of tracking

intermediate outcomes toward coupled food security and climate action goals – along with the

final outcomes – is of timely importance in the current context of the climate crisis (Mbow et al.,

2019).

In exploring the factors influencing the successful implementation of a multi-component food

safety program in Vietnam, Chapter 5 also considered program theory, alongside other

evaluation tools, as a key success factor. This chapter provided an empirical example of how

program theories are being used in practice, contributing to the evidence base of theory-driven

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evaluations in food security contexts (Chapter 4). Importantly, program theories are not meant

to be static. In Apgar et al., (2017), the initial broad program theory for an aquatic agricultural

systems program was revised after a planning workshop, leading to the integration of gender

equity, nutrition, and climate change into the revised program theory. Program theories should

be regularly revisited following new information obtained from implementation and/or changes

in context (Lam, 2020; Mayne, 2015).

7.2.2 Considering gender and other social identities in evaluation processes

Global calls have long been made for action and accountability on gender equity, notably the

1995 Fourth World Conference on Women, the Millennium Development Goals, and the 2030

Agenda for Sustainable Development (Heidari et al., 2018). Many international development

institutions today acknowledge the importance of gender by implementing gender

mainstreaming policies. For example, since the release of evaluation guidelines by the United

Nations Evaluation Group in 2011, entities across the United Nations system have adopted

gender integration into all evaluations (UNEG, 2011). Evaluators have acknowledged “there is

tremendous but largely untapped potential for evaluation to deepen understanding around

gender inequities” (Hay, 2012, p. 337). And scholars are increasingly encouraging gender and

sex considerations in research and practice (Heidari et al., 2018; McLean & Sen, 2019;

Tannenbaum et al., 2016).

This dissertation responds to these calls to integrate gender and other social identities into their

work. Food insecurity and climate change impacts are most significant for underserved

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populations, particularly women, girls, and Indigenous Peoples, who do not always have access

to the resources they need to protect themselves and recover from these shocks (Preet et al.,

2010; Ford, 2012; Saxena et al., 2016; van Daalen et al., 2020). Chapters 2 and 4 integrated

gender in research on evaluation by assessing how and to what extent gender was considered in

studies. Chapter 2 found gender was often considered by providing gender-disaggregated data

on who participated in the program and what their experiences were like. This finding is

consistent with other studies exploring gender considerations in evaluation (Fletcher, 2015; Lam

et al., 2019). In Chapter 4, theory-driven evaluations considered gender primarily by outlining

outcome pathways for women as the main program beneficiaries. These studies also identified

gaps in gender considerations. For example, in Chapter 2, only one-third of the reviewed articles

provided gender-disaggregated data, resulting in an incomplete understanding of how women,

men, and gender-diverse people may differentially participate in, and experience programs.

While this review explored how different social groups (e.g. population, age, gender) were

reported on, only gender implications were explicitly mentioned in studies. Continuing to

question “for whom” program theories work might help ensure pathways toward food security

are socially inclusive (Lam et al., 2019).

7.2.3 Integrating climate change into all stages of an evaluation

This dissertation offered strategies for considering complexities arising from climate change and

other contextual factors. In the program description of evaluations, Chapter 3 suggested

providing an overview of potential climate risks, which would facilitate the consideration of

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climate factors throughout evaluation processes. Chapter 4 identified ways in which theory-

driven approaches to evaluation considered climate change within food security situations; for

example, Realist Evaluation studies tracked contextual influences including climate change on

program implementation and outcomes through context-mechanism-outcome configurations

(e.g. Maye et al., 2019). Chapter 5 described how the climate context alongside program

outcomes and strategies on a real-time basis through an evaluation tool called Outcome

Mapping (Earl et al., 2001). These strategies are consistent with those offered in evaluation

studies in public health settings (Craig et al., 2018; Skivington et al., 2021).

This dissertation joins calls by other evaluators to consider climate change in evaluations of food

security and other development programs (Rowe, 2019; Ssekamatte, 2018; Uitto 2019). Research

findings from this dissertation highlighted opportunities for enhanced inclusion of climate

change considerations in evaluation. In Chapter 3, evaluation studies scoring high in terms of

climate change integration included a climate risk assessment, an explicit strategy for measuring

climate action outcomes, and dedicated reporting of climate action outcomes. In Chapter 4,

evaluation studies applying theory-driven approaches to evaluation accounted for climate

change considerations by examining how climate change might influence program outcome

pathways (e.g. Béné et al., 2020) or how program operations under the context of climate

variability (e.g. Howland, 2019). In Chapter 5, asking researchers and community members

involved in a food safety program where climate change was not an explicit consideration

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identified climate change implications, highlighting the importance of examining climate change

in programs where climate change seems far removed from the program.

The practice of integrating climate change into evaluation builds on efforts to mainstream

environmental and climatic considerations into development programming (UNDP, 2015;

Vincent & Colenbrander, 2018; World Resources Institute, 2018). For example, the Government

of Canada developed the Environmental Integration Process to guide mainstreaming of

environment and climate change considerations in all sectors of Canadian international

assistance programming (GAC, 2017). This mainstreaming process involves assessing all policy,

program, and project initiatives and integrating appropriate environmental and climatic

measures into their design, implementation, and monitoring. Mainstreaming climate change

into evaluations of food security programs might encourage programs to consider measures to

respond to climate change.

7.3 Strengths and limitations

There are several strengths and limitations of the dissertation approach worth noting. First, the

ability to discern how evaluation approaches (e.g. community-based monitoring, climate change

integration into evaluation, theory-driven evaluation) have shifted over time in the review-based

chapters was dependent on what was reported in the reviewed studies. Given word and space

limits, articles and reports might have prioritized documenting evaluation outcomes rather than

processes. For example, in several studies, evaluation experiences were presented across

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multiple articles (e.g. Levay et al., 2018; Levay et al., 2019). Related to the above limitation is that

review-based chapters often do not provide adequate insights into context; accounting for

variations in implementation context is critical as some differences in context can determine

whether outcomes are achieved (Hammersley, 2020). Nevertheless, incorporating qualitative

analysis within review-based chapters allowed for in-depth insights into how and why

evaluations of food security programs were conducted. Furthermore, these chapters synthesized

bodies of evaluation knowledge that are often scattered across disciplines and countries.

A key strength of this work was collaborating with users of the research. The review of

community-based monitoring systems presented in Chapter 2 addressed an important research

priority of the IHACC team. In Chapter 5, the qualitative research uncovered insights that are

guiding ongoing implementation efforts for the SafePORK team. Furthermore, Chapter 5 adds

community members’ voices to the literature on how the program is impacting them and how

climate change is influencing their food safety practices. Additionally, this chapter integrated the

rich experiences of SafePORK coordinators who joined bi-weekly meetings to discuss the

research process and findings. Debrief sessions were also held with research assistants to reflect

on the research process, adjust the interview guide, and co-interpret the data. Importantly, the

existing strong relationships between research assistants and participants was key in facilitating

data collection remotely during a pandemic.

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Another strength of the research presented in Chapter 5 was how this work was informed by my

previous experience of living in Vietnam for several years before starting my dissertation. I

became familiar with the local food safety situation which allowed me to probe this context.

Additionally, I had already worked alongside SafePORK researchers and community members in

Vietnam. This access to research participants is likely not available to individuals without pre-

existing relationships. My status as an insider-outsider also provided faster access to

participants. While going through informed consent, many members of the SafePORK team

stated they were willing to talk with me openly as they were interested in learning from the

results of the study.

7.4 Suggestions for future research

This dissertation highlighted strategies reported in research and evaluation studies for

measuring climate action outcomes within food security programs. An important area for future

research is developing guidance for integrating climate action into evaluation. For example,

should climate change be assessed in some or all food security programs? Are there different

levels of climate assessment, depending on the extent that programs impact (and are impacted

by) climate change? How should climate action outcomes be reported? We encourage

researchers to grapple with these questions and reflect on strategies used to measure climate

action outcomes. Importantly, findings from this dissertation drew primarily on studies in the

published and grey literature; engaging with evaluators and evaluation partners involved in this

work could yield additional insights not captured from the literature.

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There are many indicators, criteria, and frameworks for measuring climate action outcomes in

development settings (Bours et al., 2014; Fisher et al., 2015; Wojewska et al., 2021). Future

research is needed to develop measurement tools that apply to agriculture and food security

settings, where climate change impacts are especially visible. Measurement tools attuned to the

needs, priorities, and operational constraints of organizations on the ground are important for

developing practical food security program evaluations. And because climate change is a global

problem, future research should consider how findings from individual evaluation studies and

settings can be aggregated to promote learning of and accountability toward collective climate

action.

7.5 Concluding thoughts

As I write the conclusion of my dissertation near the end of 2021, several high-level events took

place. The Secretary-General of the United Nations convened a Food Systems Summit as a way

of setting the stage for global food systems transformation toward achieving the 2030

Sustainable Development Goals (UN, 2021). Expert reviewers for the sixth assessment report

published by the Intergovernmental Panel on Climate Change stated strong, rapid, and

sustained emissions reductions are needed to limit global warming and prevent the worst

climate impacts (IPCC, 2021). The United Nations climate change conference (COP26) resulted in

an outcome document, known as the Glasgow Climate Pact, which calls on 197 countries to

report their progress toward more ambitious climate commitments (United Nations, 2021).

Because food systems impact (and are impacted by) climate change, food systems reform is

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critical for addressing the climate emergency. In response to the growing impacts of climate

change on food security globally, public investments made in climate action, and the need to

demonstrate progress toward climate change goals, interest in evaluating climate action within

food security and other development contexts is growing.

Against this backdrop, I offer two key messages to take away from this dissertation. The first is

for evaluators to ask about climate change. Opportunities exist for enhanced inclusion of climate

considerations in evaluations of food security and other development programs, provided the

design is responsive to the needs, priorities, and operational constraints of evaluation. A strong

entry point into initially thinking about climate change is the risk management/context section

of program and evaluation planning. Asking how food security programs affect (and are affected

by) climate risks and whether risks differ by gender and other social identities can help identify

opportunities for addressing possible climate vulnerabilities. These considerations could

improve the climate resilience programs and avoid investments that unintentionally lead to

climate maladaptation.

Secondly, there is a need for further research on evaluation about complex food security

programs to keep up to date on shifts in evaluation priorities and tools. Although widely used,

conventional assessments of program performance against desired outcomes are often not

effective for supporting complex programs where program activities and intended outcomes

shift during implementation. The use of alternative approaches to evaluation – mixed-methods,

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qualitative, context-sensitive, theory-based – shows promise in supporting the learning and

accountability needs of complex programs. Funders and evaluation commissioners should

encourage bold methods where experiences are still quite limited. And evaluators should keep

up to date with shifts in evaluation priorities and continue investigating evaluation processes

and products to inform food security evaluation theory and practice.

This dissertation makes substantial contributions to the global literature by providing syntheses

of evaluations that measure climate action outcomes within food security programs. From these

syntheses, promising alternative approaches to evaluation supporting climate action outcome

measurements are highlighted. Additionally, this dissertation provides a practical case study

illustrating how asking about climate change (for a food security program where climate change

impacts are not immediately obvious) can yield important insights for future climate action.

Funders, evaluation commissioners, evaluators, and practitioners working in food security

contexts should encourage climate considerations in evaluation, and in doing so, contribute to

climate-responsive food security programming.

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7.6 References

Apgar, J. M., Allen, W., Albert, J., Douthwaite, B., Paz Ybarnegaray, R., & Lunda, J. (2017). Getting

beneath the surface in program planning, monitoring and evaluation: Learning from use of

participatory action research and theory of change in the CGIAR Research Program on

Aquatic Agricultural Systems. Action Research, 15(1), 15–34.

https://doi.org/10.1177/1476750316673879

Béné, C., Riba, A., & Wilson, D. (2020). Impacts of resilience interventions – Evidence from a

quasi-experimental assessment in Niger. International Journal of Disaster Risk Reduction.

https://doi.org/10.1016/j.ijdrr.2019.101390

Bours, D., McGinn, C., & Pringle, P. (2014). Monitoring & evaluation for climate change

adaptation and resilience : A synthesis of tools , frameworks and approaches. SEA Change

CoP, Phnom Penh and UKCIP, May, 1–67.

Craig, P., Di Ruggiero, E., Frohlich, K. L., Mykhalovskiy, E., & White, M. (2018). Taking account of

context in population health intervention research: guidance for producers, users and funders

of research.

Earl, Sarah, Carden, Fred, Smutylo, T. (2001). Outcome mapping. In Evaluation (Issue Idrc 1999).

https://doi.org/10.1007/978-981-10-0983-9_6

Fisher, S., Dinshaw, A., Mcgray, H., Rai, N., & Schaar, J. (2015). Evaluating Climate Change

Adaptation: Learning From Methods in International Development. New Directions for

Evaluation, 2015(147), 13–35. https://doi.org/10.1002/ev.20128

Fletcher. (2015). Addressing gender in impact evaluation: a methods lab publication.

Ford, J. D. (2012). Indigenous health and climate change. American Journal of Public Health,

102(7), 1260–1266. https://doi.org/10.2105/AJPH.2012.300752

GAC. (2017). Environmental Integration Process – Development Programming.

Hammersley, M. (2020). Reflections on the Methodological Approach of Systematic Reviews. In

Systematic Reviews in Educational Research. https://doi.org/10.1007/978-3-658-27602-7_2

Hay, K. (2012). Engendering Policies and Programmes through Feminist Evaluation:

Opportunities and Insights. Indian Journal of Gender Studies, 19(2), 321–340.

https://doi.org/10.1177/097152151201900208

Heidari, S., Babor, T. F., De Castro, P., Tort, S., & Curno, M. (2018). Sex and gender equity in

221

research: rationale for the SAGER guidelines and recommended use. Gaceta Sanitaria.

https://doi.org/10.1016/j.gaceta.2018.04.003

Hendriks, S. (2020). Food security policy, evaluation and impact assessment. Earthscan.

Howland, F. (2019). Individual capacity baseline report.

IPCC. (2021). AR6 Synthesis Report: Climate Change 2022. https://www.ipcc.ch/assessment-

report/ar6/

Keleman Saxena, A., Cadima Fuentes, X., Gonzales Herbas, R., & Humphries, D. L. (2016).

Indigenous Food Systems and Climate Change: Impacts of Climatic Shifts on the Production

and Processing of Native and Traditional Crops in the Bolivian Andes. Frontiers in Public

Health, 4. https://doi.org/10.3389/fpubh.2016.00020

Lam, S., Dodd, W., Whynot, J., & Skinner, K. (2019). How is gender being addressed in the

international development evaluation literature? A meta-evaluation. Research Evaluation,

28(2), 158–168. https://doi.org/10.1093/reseval/rvy042

Lam, S. (2020). Toward Learning from Change Pathways: Reviewing Theory of Change and Its

Discontents. Canadian Journal of Program Evaluation, 35(2), 188-203.

https://doi.org/10.3138/cjpe.69535

Maye, D., Enticott, G., & Naylor, R. (2019). Theories of Change in Rural Policy Evaluation.

Sociologia Ruralis. https://doi.org/10.1111/soru.12269

Mayne, J. (2015). Useful theory of change models. Canadian Journal of Program Evaluation,

30(2), 119–142. https://doi.org/10.3138/cjpe.230

Mbow, C., Rosenzweig, C., Barioni, L. G., Benton, T. G., Herrero, M., Krishnapillai, M., Liwenga, E.,

Pradhan, P., Rivera-Ferre, M. G., Sapkota, T., Tubiello, F. N., & Xu, Y. (2019). Food Security. In

P. Z. P.R. Shukla, J. Skea, E. Calvo Buendia, V. Masson-Delmotte, H.-O. Pörtner, D.C. Roberts,

J. P. P. R. Slade, S. Connors, R. van Diemen, M. Ferrat, E. Haughey, S. Luz, S. Neogi, M.

Pathak, J. Petzold, & J. M. P. Vyas, E. Huntley, K. Kissick, M. Belkacemi (Eds.), Climate Change

and Land: an IPCC special report on climate change, desertification, land degradation,

sustainable land management, food security, and greenhouse gas fluxes in terrestrial

ecosystems.

McLean, R. K. D., & Sen, K. (2019). Making a difference in the real world? A meta-analysis of the

quality of use-oriented research using the Research Quality Plus approach. Research

Evaluation, 28(2), 123–135. https://doi.org/10.1093/reseval/rvy026

222

Preet, R., Nilsson, M., Schumann, B., & Evengård, B. (2010). The gender perspective in climate

change and global health. Global Health Action. https://doi.org/10.3402/gha.v3i0.5720

Rowe, A. (2019). Sustainability-Ready Evaluation: A Call to Action. New Directions for Evaluation,

2019(162), 29–48. https://doi.org/10.1002/ev.20365

Skivington, K., Matthews, L., Simpson, S. A., Craig, P., Baird, J., Blazeby, J. M., Boyd, K. A., Craig, N.,

French, D. P., McIntosh, E., Petticrew, M., Rycroft-Malone, J., White, M., & Moore, L. (2021). A

new framework for developing and evaluating complex interventions: Update of Medical

Research Council guidance. The BMJ. https://doi.org/10.1136/bmj.n2061

Ssekamatte, D. (2018). The role of monitoring and evaluation in climate change mitigation and

adaptation interventions in developing countries. African Evaluation Journal, 6(1).

https://doi.org/10.4102/aej.v6i1.254

Tannenbaum, C., Greaves, L., & Graham, I. D. (2016). Why sex and gender matter in

implementation research. BMC Medical Research Methodology, 16(1).

https://doi.org/10.1186/s12874-016-0247-7

Uitto, J. I. (2019). Sustainable Development Evaluation: Understanding the Nexus of Natural and

Human Systems. New Directions for Evaluation, 2019(162), 49–67.

https://doi.org/10.1002/ev.20364

UN. (2021). The food systems summit. https://www.un.org/food-systems-summit

UNDP. (2015). Mainstreaming Environment and Climate for Poverty Reduction and Sustainable

Development.

UNEP. (2016). Terminal Evaluation of the UNDA 7th Tranche funded UNEP project “Capacity

Building in National Planning for Food Security.”

United Nations. (2021). COP26 closes with ‘compromise’ deal on climate, but it’s not enough, says

UN chief. https://news.un.org/en/story/2021/11/1105792

United Nations Evaluation Group. (2011). Integrating Human Rights and Gender Equality in

Evaluation - Towards UNEG Guidance.

http://www.unevaluation.org/documentdownload?doc_id=980&file_id=1294

van Daalen, K., Jung, L., Dhatt, R., & Phelan, A. L. (2020). Climate change and gender-based

health disparities. In The Lancet Planetary Health. https://doi.org/10.1016/S2542-

5196(20)30001-2

223

Vincent, K., & Colenbrander, W. (2018). Developing and applying a five step process for

mainstreaming climate change into local development plans: A case study from Zambia.

Climate Risk Management. https://doi.org/10.1016/j.crm.2018.04.005

Wojewska, A. N., Singh, C., & Hansen, C. P. (2021). A policy tool for monitoring and evaluation of

participation in adaptation projects. Climate Risk Management.

https://doi.org/10.1016/j.crm.2021.100326

World Resources Institute. (2018). FROM PLANNING TO ACTION: MAINSTREAMING CLIMATE

CHANGE ADAPTATION INTO DEVELOPMENT.

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Appendices

Appendix 1: Search strategy to identify published articles on Indigenous community-based

monitoring of Indigenous food security and climate change in AGRICOLA©, PRISMA©,

MEDLINE®, CabDirect©, and the Web of Science™ CORE Collection databases.

Main terms Expanded terms

Indigenousa Aasax OR Aboriginal OR "Aboriginal-Malay" OR Aborigine OR Achi OR

Achuar OR Adibashi OR Adivasi OR Adivasis OR Afar OR Ainu OR Aka OR

Akatek* OR Akawai OR Akha OR Akie OR Akoula OR Akurio OR Akwoa OR

"al-Kaabneh" OR "al-Asarmeh" OR "al-Ramadin" OR "al-Rshaida" OR Aleut

OR Alutor OR Amazigh OR Ambo OR Ameridian OR Amuesha OR Anak OR

"Andean Kichwe" OR "Andoa" OR "Andorrans" OR Angaite OR Anikhwe

OR Anu OR Arara OR Arawak OR "Arawak-Taino" OR Arwak OR Ashaninka

OR Atayal OR Austronesian OR "Ava Guarani" OR Awajun OR Awa OR

Awakateco OR Aweer OR Ayeoreo OR Aymara OR Ayoreo OR Aztec OR

Baaka OR Baantonu OR Babi OR Bahnar OR Babongo OR Bacwa OR

Bagame OR Bagombe OR Bagyeli OR BaGyeli OR Bajuni OR Baka OR

Bakgalagadi OR Bakola OR Bakongo OR Bakoya OR Balala OR Bambara

OR Bambuti OR Bantu OR Barabaig OR Bariba OR Barimba OR Basarwa OR

Bassari OR Batwa OR Bawarwa OR BaWka OR Bawn OR BaYeyi OR Bedzam

OR Benet OR Berabis OR Berawan OR Berber OR Berbers OR Bidayuh OR

Bigombe OR Biharis OR Bilma OR Bisayah OR Bobo OR Boeschs OR Bofi

OR Boni OR Bonis OR Boranna OR Boro OR Bororo OR Boruka OR

Botsarwa OR Bozo OR Brao OR Bribri OR "Bri Bri" OR Brunca OR Bugakhwe

OR Bulu OR Bumipeuteras OR Bunak OR Bunun OR Bwiti OR Cabecar OR

Cacaopera OR Campeche OR Carib OR Caribs OR "Ch’orti" OR Chachi OR

Chaima OR Chakma OR Chalchiteco OR Chamorro OR Chamorru OR

Chamorous OR "Chao-Khao" OR "Chao Ley" OR Charrua OR Chelkancy OR

Chiapas OR Chibcha OR Chibchense OR Chipaya OR Chiriguano OR

Chiquito OR Chiquitano OR Chorotega OR Chorti OR Cofan OR Chuaa OR

Chuj OR Chukchi OR Chulymcy OR Chuvancy OR Ciboney OR "Ciboney-

Taino-Arawak" OR "Cocama-Cocomilla" OR Colla OR Copts OR Cotier OR

Cree OR Cumanagoto OR Dabou OR Dagiri OR Dahalo OR Danisi OR

Daroobe OR Datoga OR Daza OR Degar OR Deti OR Diaguita OR Dinka

OR Dioula OR Ditammari OR Dogon OR Dolgan OR Doma OR Dukha OR

Dusun OR Ebrie OR "egga hodaabe" OR Elmolo OR "El Mono" OR Embera

OR Emerillon OR Ency OR Endorois OR "Enlhet Norte" OR Enxet OR "Enxet

Sur" OR Epera OR Eskimo OR "Ese Eja" OR Evenk OR Ewondo OR Fatukuku

OR "First Nation*" OR "Forest dwell*" OR Fuegian OR Fulani OR Fulbe OR

225

Galibia OR Galibi OR Garifuna OR Gaoshan OR Gio OR Guadalcanese OR

Guana OR Guaicuru OR Guarani OR "Guarani Mbya" OR Guyami OR

Guaymi OR Guerrero OR Gurani OR Guransi OR Gurung OR "G//ana" OR

"G/wi" OR "Gwich’in" OR Hadzabe OR Hadza OR Haida OR Herero OR

Hidalgo OR "Hill People" OR "Hill Person" OR Hmong OR Hoa OR

Huambisa OR Huastec OR Hui OR Huetar OR Hutu OR Iban OR Igotot OR

Ik OR Imazighn OR Imazighen OR Indigenous OR Ingarico OR Inuit OR

Inupiat OR Inuvialut OR Iroquoian OR Itelmen OR Itza OR Ixil OR Jacalteco

OR "Jahalin Bedouin" OR Jarai OR Jivi OR Jumma OR "Ju’hoansi" OR

"K’iche" OR "Ka Pei Aina" OR Kachin OR Kaiowa OR Kalanga OR Kalina OR

"Kalina-go" OR Kalinago OR "Kalinago-Taino" OR "Kali’na" OR Kamchadal

OR Kanak OR "Kanaka Maoli" OR Kanuri OR Kaqchikel OR Karamajong OR

Karenni OR Kavalan OR Kayapo OR Kawashkar OR Kayan OR Kazakh OR

Kedayan OR Kelait OR Kenyah OR Kereki OR Kety OR "Khali’nago" OR

Khamu OR Khanty OR Khengs OR "Khmer Krom" OR Khoekhoe OR "Khoe-

San" OR Khoikhoi OR Khoisan OR Khomani OR "Khudro Nrigoshthhi" OR

Khumi OR Khwe OR Khyang OR Kichwas OR Kipsigis OR Kirdi OR Koba OR

Koryak OR Krio OR Krohn OR Kua OR Kumandincy OR Kuna OR Kuy OR

Kwisi OR Lahu OR Lao OR "Laotian Tribes" OR Lenca OR Lickanantay OR

Limbu OR Lisu OR Livs OR Lobi OR Lokono OR Loma OR Lua OR Lumad

OR "Lunda-Chokwe" OR Lushai OR Maasai OR Macourai OR Macuxi OR

Macuzi OR Magar OR Makasae OR Makuxi OR Malagasy OR Malakote OR

Malay OR "Malayo-Polynesian" OR Maleku OR Mangyan OR Mani OR

Mano OR Mansi OR Maori OR Mam OR Manjo OR Marma OR "Marsh

Dwellers" OR Mapuche OR Maskoy OR "masyarakat adat" OR Mataco OR

"Mataco Matguayo" OR Matagulpa OR Maya OR "Maya Chorti" OR

Mayagna OR Mbanderu OR Mbini OR Mbororo OR Mbukushu OR

Mbundu OR Mbuti OR Mbri OR Mbya OR Mdendjele OR Melanesian OR

"Melanesian-Papauan" OR Mestico OR Mestizo OR Merina OR Metis OR

Miao OR Mien OR Mikaya OR Miskito OR Miskitu OR Misquito OR Mixte

OR Mnong OR Mogeno OR "Mon-Khmer" OR Montagnards OR Mopan

OR Moxeno OR Mozabite OR Mpukushu OR Mru OR Muong OR Murut OR

"N/oakhwe" OR "N’guigmi" OR Nagas OR Nahoa OR Nahua OR Nahuatl

OR Nama OR Nambiquara OR Nanaicy OR Nandeva OR "Nandevi Guarani"

OR Naro OR "Naso Tjerdi" OR Native OR Negidalcy OR Negeri OR Negrito

OR Nemadi OR Nenets OR Nganasan OR Ngabe OR Ngobe OR "Ngobe-

Bugle" OR Nivkhy OR Nuer OR "Nyaneka-Nkumbi" OR Oaxaca OR Ocanxiu

OR Ogiek OR Ogoni OR Ojibway OR Okinawans OR "Orang Asli" OR

Orochi OR Oroki OR Otomi OR Ovimibundu OR Oyampi OR "Pai Tavytera"

OR Paiwan OR Palenqueros OR Palikur OR Pankho OR Patamona OR Pech

226

OR Pemon OR Peul OR Peulh OR Penan OR Piaroa OR "Ping Pu" OR Pipil

OR Pocomam OR Pokot OR Poqomam OR "Poqomchi’" OR Puebla OR

Punan OR Puyuma OR "Q’anjob’al" OR "Q’eqchi" OR Qawasqar OR

Qicaque OR Quechua OR Quenchua OR "Quintano Roo" OR Qom OR Rai

OR Raisales OR Rakhine OR Rama OR Rapanui OR “Rapa Nui” OR Raute

OR Rhade OR Roraima OR Rotumans OR Rukai OR Saami OR Sabaot OR

Saharawis OR Saisyat OR Sakapulteco OR Sakizaya OR Sami OR (San AND

Africa) OR Sanapan OR Sanapana OR Sandawe OR "Santa Rosa Carib" OR

Sanya OR Saramancas OR ("Scheduled Tribes" AND India) OR Secoya OR

Sediq OR Selkup OR Semang OR Sengwer OR Senoi OR Shan OR Sherpa

OR Shipibo OR "Shipibo-Conibo" OR Shiwiar OR Shorcy OR Shua OR

Shuar OR Siona OR Sipakapense OR Soioty OR "South Sea Islander*" OR

Stieng OR "Sumu-Mayangna" OR Sutiaba OR Tachangya OR "Tai-Kadai"

OR Taino OR "Taino-Kalingo" OR Tamang OR Tampuan OR Tapeba OR

Tapebo OR Tareno OR Taurepang OR Tawahka OR Tazy OR Teda OR

Teenek OR Teko OR Tektiteko OR Telengity OR Teleuty OR Temenbe OR

Teribe OR Tesker OR Thakali OR Tharu OR Thao OR Tikuna OR Tikigaq OR

Tirio OR Toba OR "Toba Maskoy" OR Tofolar OR Tolai OR Toloupan OR

Tomarao OR Topnaars OR "Torres Straight Islander*" OR Totonac OR

Toubou OR Truku OR Tsexakhwe OR Tripura OR Tsaatan OR Tsachila OR

Tsou OR Tsumkwe OR Tshwa OR Tuareg OR Tuaregare OR Tubolar OR

Tubu OR Tugen OR Tukano OR Tupi OR Tutong OR Tutsi OR "Tuvin-

Todjin" OR Twa OR Tyua OR "Tz’utujil" OR Tzeltal OR Tzotzil OR Uchay OR

Udege OR Ulchi OR "Ureueu-Wau-Wau" OR Uru OR Uspanteko OR Vadda

OR Vadema OR Vai OR Veddhas OR Veps OR Vyadha OR "Waaniy-a-

Laato" OR Waata OR Wadoma OR Wagashi OR Wapaichana OR Waorani

OR Wapixana OR Warao OR Warrau OR "Warrau Wayana" OR Wayampi

OR Wayana OR Wayeyi OR Wayuu OR Wichi OR Wodaabe OR Wounaan

OR Xinka OR Yaaku OR Yami OR Yamana OR Yanomami OR Yukpa OR

Yvytoso OR Zamuco OR Zapara OR Zapotec OR "!Xoo" OR "//’Xauesi" OR

"/Xaisa"

Surveillance surveillance OR tracking OR monitoring OR reporting OR "information

system" OR "early warning" OR "early detection" OR "early notification"

OR "timely warning" OR "timely detection" OR "timely notification"

Food security

and climate

change

food OR agriculture OR nutrition OR livestock OR fish* OR animal OR

plant OR wildlife OR hunt* OR gather* OR environment* OR ecological OR

ecosystem OR "natural resource" OR "resource management" OR "co-

management" OR "cooperative management" OR "joint management" OR

water OR sea OR ocean OR "climate change" OR "climate variability" OR

"climate hazard" OR "extreme weather" OR "natural hazard" OR disaster

227

OR flood OR drought OR hurricane OR storm OR cyclone OR "sea level

rise" OR "irregular rainfall" OR "intense rainfall" OR resilience OR poverty

OR livelihood OR welfare OR income

Community-

based

"community-based" OR "community-centred" OR "community-centered"

OR "community-engaged" OR "community-led" OR "locally-based" OR

participatory OR collaborative OR "citizen-led" OR "citizen-engaged" OR

"citizen-based" OR "citizen science" a Search terms used to identify Indigenous peoples globally were adapted from Bishop-Williams

et al. 2017 (1). We removed several terms that were captured under other umbrella terms (e.g.

"Indigenous Palestinians" was captured by the term Indigenous and so was removed).

228

Appendix 2: Complete list of included articles and select article characteristics on Indigenous

community-based monitoring of food security and climate change.

Author Year Country Study

regiona

Indigenous

community

Food

security

theme

Wong (2) 2017 Canada Nunavut

(Arctic Bay,

Kimmirut,

and Arviat)

Inuit Wildlife

McKay (3) 2017 Canada Northcentral

British

Columbia

Takla Lake

First Nations

Natural

resource

management

Delgado-

Aguilar (4)

2016 Ecuador Sumaco

Biosphere

Reserve,

Napo,

central-

northern

Ecuador

Kichwa

community

Environmenta

l change

Dobbs (5) 2016 Australia Beagle Bay,

Dampier

Peninsula

north of

Broome,

Western

Australia

Nyul Nyul

community

Aquatic

ecosystems

Wiseman (6) 2015 Australia Alinytjara

Wilurara

Natural

Resources

Management

region,

Northwest of

South

Australia

Anangu Natural

resource

management

Harmsworth

(7)

2016 New Zealand Aotearoa Maori Aquatic

ecosystems

229

Cochran (8) 2016 Brazil Tiquie River,

Northwestern

Amazonia

Tukano and

Seana

communities

Climate

Alessa (9) 2016 Multiple

countries

Arctic Multiple

Indigenous

communities

Environmenta

l change

Johnson (10) 2015 Multiple

countries

Arctic Multiple

Indigenous

communities

Environmenta

l change

Torres (11) 2014 Mexico Chihuahua,

Chiapas,

Yucatan

Peninsula,

Oaxaca

Multiple

Indigenous

communities

Reducing

Emissions

from

Deforestation

and Forest

Degradation

(REDD+)

Holmes (12) 2014 Multiple

countries

Not specified Multiple

Indigenous

communities

REDD+

Torres (13) 2014 Multiple

countries

Not specified Multiple

Indigenous

communities

REDD+

Galabuzi (14) 2014 Uganda Mabira Forest

Reserve

Bantu ethnic

groups

Forest

resources

Gunn (15) 2014 Canada Northwest

Territories

Lutsel K’e

Dene First

Nation

Wildlife

Bell (16) 2012 Canada Canada Inuvialuit Multiple

Peace (17) 2012 Canada Northern

Canada

First Nations

and Inuit

Climate

Laidler (18) 2011 Canada Cape Dorset,

Igloolik, and

Pangnirtung,

Nunavut

Inuit Climate

Lauer (19) 2010 Solomon

Islands

Roviana

Lagoon

Pacific Island

Communities

Environmenta

l change

Valdivia (20) 2010 Bolivia Northern and

Central

Altiplano

Andean

communities

Climate

230

Heaslip (21) 2008 Canada British

Columbia

Kwakwaka'wa

kw First

Nations

Aquatic

Ntk (22) 2008 Canada Sanikiluaq,

Hudson Bay

Multiple

Indigenous

communities

(Inuit and

Cree)

Aquatic

Berkes (23) 2007 Canada Hudson and

James Bay

Multiple

Indigenous

communities

(Inuit and

Cree)

Aquatic

Robinson

(24)

2004 Australia Kakadu

National Park

Jawoyn

people

Wildlife

Wiber (25) 2004 Canada Nova Scotia

and Prince

Edward

Island

Mi’Kmaq First

Nation

Fisheries

Danby (26) 2003 Multiple

countries

Saint Elias

Mountains

(Alaska,

Yukon, British

Columbia)

First Nations

in general

Environmenta

l change

Berkes (27) 2001 Canada Arctic Multiple

Indigenous

communities

Aquatic

Kendrick (28) 2013 Canada Arctic Inuit Wildlife

Oba (29) 2012 Multiple

countries

Rangelands Multiple

Indigenous

communities

(Orma, Afar,

Karamojong)

Environmenta

l change

Dabasso (30) 2012 Kenya Central

Division of

Marsabit

Central

District

Borana Environmenta

l change

231

Kouril (31) 2016 Multiple

countries

Arctic region Multiple

Indigenous

communities

Environmenta

l change

Ens (32) 2012 Australia Arnhem Land Multiple

Indigenous

communities

Multiple

Moller (33) 2004 Multiple

countries

Not

specified

Multiple

Indigenous

communities

Wildlife

Armitage (34) 2005 Canada Bassin Island

region,

Nunavut

Inuit Fisheries

Jollands (35) 2007 New Zealand Not specified Maori Natural

resource

management

Paneque-

Galvez (36)

2017 Multiple

countries

Kukama

Kukamiria

Territory

(Peru),

Wapichana

Territory

(Guyana),

Embera-

Wounaan

Territory

(Panama)

Multiple

indigenous

communities

Environmenta

l change

Macherera

(37)

2017 Zimbabwe Gwanda

district

Gwanda

Indigenous

communities

Multiple

Vigilante (38) 2017 Australia Wunambal

Gaambera

Country,

North

Kimberley

Wunambal

Gaambera

Aboriginal

people

Forest

resources

Shaffer (39) 2017 Guyana Masakenari

Village,

Southern

Guyana

Indigenous

Waiwai

Wildlife

Oviedo (40) 2017 Brazil Kaxinawá

Nova Olinda

Indigenous

Kaxinawá

Fisheries

232

Indigenous

Territory,

State of Acre

Mateo-Vega

(41)

2017 Panama Tierras

Colectivas,

Darien

Embera and

Wounaan

people

REDD+

de Paula (42) 2017 Brazil XIL, Brazilian

Cerrado

Xerente

community

Wildlife

Ferguson (43) 2016 United States Colorado

Plateau,

northeastern

Arizona

Hobi tribe Climate

Fragoso (44) 2016 Guyana Rupununi

region

Makushi and

Wapishana

people

Wildlife

Iverson (45) 2016 Canada Nunavik,

Quebec

Inuit Wildlife

Constantino

(46)

2015 Brazil Acre State,

western Brazil

Brazilian

Amazon

Kaxinawa Wildlife

Bellfield (47) 2015 Guyana Annai

District,

North

Rupunini

Makushi

communitites

communities

REDD+

Gill (48) 2014 Canada Fort

McPherson,

Northwest

Territories

Teetł’it

Gwich’in

Environment

change

Lagasse (49) 2014 Canada Great Bear

Rainforest of

British

Columbia

Coastal First

Nations

(Heiltsuk,

Metlakatla,

Wuikinuxw,

Haisla,

Gwa'sala'Nak

waxda'xw,

Nuxalk)

Fisheries

233

Housty (50) 2014 Canada Coastal

British

Columbia

Heiltsuk First

Nation

Multiple

Ford (51) 2013 Canada Iqaluit,

Nunavut

Inuit Multiple

Constantino

(52)

2012 Multiple

countries

Brazilian

Amazonia

and one in

Namibian

Caprivi

conservancie

Multiple

Indigenous

communities

Wildlife

Luzar (53) 2011 Guyana North

Repununi

and South

Rupunini

Makushi and

Wapisana

communities

Wildlife

Wesche (54) 2011 Canada Old Crow,

Yukon

Vuntut

Gwitchin First

Nation

Multiple

Marcoux (55) 2011 Canada Nunavut Inuit Wildlife

Gearheard

(56)

2011 Canada Kangiqtugaa

pik, Nunavut

Inuit Multiple

Ens (57) 2010 Australia Arnhem

Plateau,

Northern

Territory

Aboriginal

Rangers

Multiple

Mahoney (58) 2009 Multiple

countries

Barrow,

Alaska; Clyde

River,

Nunavut,

Canada; and

Qaanaaq,

Greenland

Arctic

communities

Multiple

(including

climate

change)

Setty (59) 2008 India Biligiri

Rangaswamy

Temple

Wildlife

Sanctuary,

South India

Soliga

harvesters

Forest

resources

Constantino

(60)

2008 Brazil Acre Kaxinawa

people

Wildlife

234

Tremblay (61) 2008 Canada Nunavik,

Quebec

Multiple

Indigenous

communities

(Five Inuit

communities

and one

Naskapi

community)

Climate

Ohl-

Schacherer

(62)

2007 Peru Manu

National Park

in Peruvian

Amazonia

Matsigenka c

ommunities

Wildlife

Noss (63) 2004 Bolivia Bolivian

Chaco

Isoseno-

Guarani

Wildlife

Noss (64) 2001 Bolivia Bolivian

Chaco

Isoseno-

Guarani

Wildlife

Torres (65) 2001 Mexico Michoacan in

Central

Mexico

Purepecha

community

Multiple

Brook (66) 2009 Canada Sahtu

Settlement

Area,

Northwest

Territories

Multiple

Indigenous

communities

(De´-line,

Tulita,

Norman

Wells, Fort

Good Hope,

and Colvill)

Multiple

Boissiere (67) 2014 Lao PDR Luang

Prabang

Province

Multiple

ethnic groups

(Hmong,

Khmu and

Tai-Lao)

Forest

resources

Krause (68) 2013 Ecuador Amazon

provinces of

Napo,

Orellana and

Pastaz

Kitchwa Multiple

Larter (69) 2009 Canada Dehcho

Region NWT

Dehco First

Nations

Wildlife

235

Noss (70) 2005 Bolivia Gran Chaco Isoseno-

Guarani

Wildlife

Pacheco-

Cobos (71)

2015 Mexico

La Malinche

National Park

(LMNP) in

Central

Mexico

Multiple

communities

(Nahua,

Otomi and

Mestizo

communities)

Forest

resources

Gratani (72) 2016 Australia Wet Tropics

of northern

Queensland

Malanbarra

and Dulabed

Yidinji people

Environment

Kofinas (73) 2003 MC Arctic regions Multiple

Indigenous

Wildlife

Lyver (74) 2017 New Zealand Ruatahuna,

Te Urewera

region

Tuhoe

Tuawhenua

community

Multiple

Van Vliet (75) 2017 Colombia Ticoya

Indigenous

Reserve of

Puerto

Nariño,

Amazonas,

Colombia

Multiple

Indigenous

groups

(Ticuna,

Cocama and

Yagua ethnic

groups)

Wildlife

Driscoll (76) 2013 United States Alaska Multiple

Indigenous

communities

(8

communities

across three

different

regions)

Multiple

Driscoll (77) 2016 United States Alaska Multiple

Indigenous

communities

(11

communities

across three

regions)

Multiple

Vieira (78) 2015 Brazil Piagacu-

Purus

Indigenous

communities

Wildlife

236

Reserve,

Brazilian

Amazon

(5

communities)

Obura (79) 2001 Kenya Diani-Chale

coral reef

area, South

Mombasa

Digo people Fisheries

Pollock (80) 2005 Canada Northwest

territories

Multiple

Indigenous

communities

(Dene,

Inuvialuit,

Gwich'in

people)

Multiple

Funder (81) 2013 Tanzania Iringa

Region,

southern

Tanzania

Hehe Multiple

Fidel (82) 2014 Multiple

countries

Bering Sea

(Alaska,

Russian

Federation)

Multiple

Indigenous

communities

Wildlife

Herrmann

(83)

2014 Multiple

countries

Quebec

(Canada),

northern

Sweden

Multiple

Indigenous

communities

(Sami, the

Cree, and the

Naskapi)

Wildlife

Parlee (84) 2014 Canada Northwest

Territories

Łutsël K’é

Dene First

Nation

Wildlife

Cummings

(85)

2017 Guyana Pupununi,

Southern

Guyana

Amerindian

communities

Forest

resources

Rijsoort (86) 2005 China Yunnan

province

Han, Dai,

Lisu, and yi

minorities

Multiple

Sheil (87) 2015 Indonesia Mamberamo-

Foja region,

Kay,

Metaweja,

Environmenta

l change

237

Province of

Papua

and Yoke

communities a Note that countries define their geographic boundaries differently and that articles provided

varying levels of detail on the study region. We extracted data on the study region as is

described by the articles.

238

Appendix 3: Complete list of references.

1. Bishop-Williams K, Sargeant JM, Berrang-Ford L, Edge V, IHACC Research Team, Harper

SL. A protocol for a systematic narrative synthesis review: The global impact of

environment on acute respiratory infections in Indigenous populations. BMC Syst Rev

[Internet]. 2017;In preparation. Available from: http://dx.doi.org/10.1186/s13643-016-

0399-x

2. Wong PBY, Dyck MG, Hunters A, Hunters I, Hunters M, Murphy RW. Inuit perspectives of

polar bear research: Lessons for community-based collaborations. Vol. 53, Polar Record.

2017. p. 257–70.

3. McKay AJ, Johnson CJ. Confronting barriers and recognizing opportunities: Developing

effective community-based environmental monitoring programs to meet the needs of

Aboriginal communities. Environ Impact Assess Rev. 2017;64:16–25.

4. Delgado-Aguilar MJ, Konold W, Schmitt CB. Original Articles: Community mapping of

ecosystem services in tropical rainforest of Ecuador. Ecol Indic [Internet]. 2017;73:460–71.

Available from:

http://10.0.3.248/j.ecolind.2016.10.020%0Ahttps://proxy.mendelu.cz/auth/login?url=http:/

/search.ebscohost.com/login.aspx?direct=true&db=edselp&AN=S1470160X16306069&la

ng=cs&site=eds-live

5. Dobbs RJ, Davies CL, Walker ML, Pettit NE, Pusey BJ, Close PG, et al. Collaborative

research partnerships inform monitoring and management of aquatic ecosystems by

Indigenous rangers. Rev Fish Biol Fish. 2016;26(4):711–25.

6. Wiseman ND, Bardsley DK. Monitoring to Learn, Learning to Monitor: A Critical Analysis of

Opportunities for Indigenous Community-Based Monitoring of Environmental Change in

Australian Rangelands. Geogr Res. 2016;54(1):52–71.

7. Harmsworth G, Awatere S, Robb M. Indigenous Māori values and perspectives to inform

freshwater management in aotearoa-New Zealand. Ecol Soc. 2016;21(4).

8. Cochran F V., Brunsell NA, Cabalzar A, van der Veld PJ, Azevedo E, Azevedo RA, et al.

Indigenous ecological calendars define scales for climate change and sustainability

assessments. Sustain Sci. 2016;11(1):69–89.

9. Alessa L, Kliskey A, Gamble J, Fidel M, Beaujean G, Gosz J. The role of Indigenous science

and local knowledge in integrated observing systems: moving toward adaptive capacity

indices and early warning systems. Sustain Sci. 2016;11(1):91–102.

10. Johnson N, Behe C, Danielsen F, Nickels S, Pulsifer PL. Community-Based Monitoring and

Indigenous Knowledge in a Changing Arctic : [Internet]. Available from:

239

http://www.inuitcircumpolar.com/uploads/3/0/5/4/30542564/cbm_final_report.pdf

11. Torres AB. Potential for integrating community-based monitoring into REDD+. Forests.

2014;5(8):1815–33.

12. Holmes I, Potvin C. Avoiding re-inventing the wheel in a people-centered approach to

REDD+. Conserv Biol. 2014;28(5):1380–93.

13. Torres AB, Acuña LAS, Vergara JMC. Integrating CBM into land-use based mitigation

actions implemented by local communities. Forests. 2014;5(12):3295–326.

14. Galabuzi C, Eilu G, Mulugo L, Kakudidi E, Tabuti JRS, Sibelet N. Strategies for empowering

the local people to participate in forest restoration. Agrofor Syst. 2014;88(4):719–34.

15. Gunn A, Russell D, Greig L. Insights into integrating cumulative effects and collaborative

comanagement for migratory tundra caribou herds in the Northwest Territories, Canada.

Ecol Soc. 2014;19(4).

16. Bell RK, Harwood LA. Harvest-based monitoring in the inuvialuit settlement region: Steps

for success. Arctic. 2012;65(4):421–32.

17. McClymont Peace D, Myers E. Community-based participatory process--climate change

and health adaptation program for Northern First Nations and Inuit in Canada. Int J

Circumpolar Health. 2012;71(0):1–8.

18. Laidler GJ, Hirose T, Kapfer M, Ikummaq T, Joamie E, Elee P. Evaluating the Floe Edge

Service: How well can SAR imagery address Inuit community concerns around sea ice

change and travel safety? Can Geogr. 2011;55(1):91–107.

19. Lauer M, Aswani S. Indigenous knowledge and long-term ecological change: Detection,

interpretation, and responses to changing ecological conditions in pacific island

communities. Environ Manage. 2010;45(5):985–97.

20. Valdivia C, Seth A, Gilles JL, García M, Jiménez E, Cusicanqui J, et al. Adapting to climate

change in Andean ecosystems: Landscapes, capitals, and perceptions shaping rural

livelihood strategies and linking knowledge systems. Ann Assoc Am Geogr.

2010;100(4):818–34.

21. Heaslip R. Monitoring salmon aquaculture waste: The contribution of First Nations’ rights,

knowledge, and practices in British Columbia, Canada. Mar Policy. 2008;32(6):988–96.

22. Ntk. A life vest for Hudson Bay’s drifting stewardship. In: Arctic. 2008. p. 35–47.

23. Berkes F, Berkes MK, Fast H. Collaborative integrated management in Canada’s North: The

role of local and traditional knowledge and community-based monitoring. Coast Manag.

2007;35(1):143–62.

240

24. Robinson CJ, Smyth D, Whitehead PJ. Bush tucker, bush pets, and bush threats:

Cooperative management of feral animals in Australia’s Kakadu National Park. Conserv

Biol. 2005;19(5):1385–91.

25. Wiber M, Berkes F, Charles A, Kearney J. Participatory research supporting community-

based fishery management. Mar Policy. 2004;28(6):459–68.

26. Danby RK, Hik DS, Slocombe DS, Williams A. Science and the St Elias: An evolving

framework for sustainability in North America’s highest mountains. Geogr J.

2003;169(3):191–204.

27. Berkes F, Mathias J, Kislalioglu M, Fast H. The Canadian arctic and the Oceans Act: The

development of participatory environmental research and management. Ocean Coast

Manag. 2001;44(7–8):451–69.

28. Kendrick A. Canadian Inuit sustainable use and management of Arctic species. Int J

Environ Stud. 2013;70(3):414–28.

29. Oba G. Harnessing pastoralists’ indigenous knowledge for rangeland management: three

African case studies. Pastor Res Policy Pract [Internet]. 2012;2(1):1. Available from:

http://pastoralismjournal.springeropen.com/articles/10.1186/2041-7136-2-1

30. Dabasso BH, Oba G, Roba HG. Livestock-based knowledge of rangeland quality

assessment and monitoring at landscape level among borana herders of northern Kenya.

Pastoralism. 2012;2(1).

31. Kouril D, Furgal C, Whillans T. Trends and key elements in community-based monitoring:

a systematic review of the literature with an emphasis on Arctic and Subarctic regions.

Environ Rev [Internet]. 2016;24(2):151–63. Available from:

http://www.nrcresearchpress.com/doi/10.1139/er-2015-0041

32. Ens EJ, Towler GM, Daniels C. Looking back to move forward: Collaborative ecological

monitoring in remote Arnhem Land. Ecol Manag Restor. 2012;13(1):26–35.

33. Moller H, Berkes F, Lyver POB, Kislalioglu M. Combining Science and Traditional Ecological

Knowledge : Monitoring Populations for Co-Management. Ecol Soc. 2004;9(3):2.

34. Armitage D. Adaptive capacity and community-based natural resource management. Vol.

35, Environmental Management. 2005. p. 703–15.

35. Jollands N, Harmsworth G. Participation of indigenous groups in sustainable development

monitoring: Rationale and examples from New Zealand. Ecol Econ. 2007;62(3–4):716–26.

36. Paneque-Gálvez J, Vargas-Ramírez N, Napoletano B, Cummings A. Grassroots Innovation

Using Drones for Indigenous Mapping and Monitoring. Land [Internet]. 2017;6(4):86.

241

Available from: http://www.mdpi.com/2073-445X/6/4/86

37. Macherera M, Chimbari MJ, Mukaratirwa S. Indigenous environmental indicators for

malaria: A district study in Zimbabwe. Acta Trop. 2017;175:50–9.

38. Vigilante T, Ondei S, Goonack C, Williams D, Young P, Bowman D. Collaborative Research

on the Ecology and Management of the “Wulo” Monsoon Rainforest in Wunambal

Gaambera Country, North Kimberley, Australia. Land [Internet]. 2017;6(4):68. Available

from: http://www.mdpi.com/2073-445X/6/4/68

39. Shaffer CA, Milstein MS, Yukuma C, Marawanaru E, Suse P. Sustainability and

comanagement of subsistence hunting in an indigenous reserve in Guyana. Conserv Biol.

2017;31(5):1119–31.

40. Oviedo AFP, Bursztyn M. Community-based monitoring of small-scale fisheries with

digital devices in Brazilian Amazon. Fish Manag Ecol. 2017;24(4):320–9.

41. Mateo-Vega J, Potvin C, Monteza J, Bacorizo J, Barrigón J, Barrigón R, et al. Full and

effective participation of indigenous peoples in forest monitoring for reducing emissions

from deforestation and forest degradation (REDD+): Trial in Panama’s Darién. Ecosphere.

2017;8(2).

42. de Paula M, Xerente V, Pezzuti J. Hunting and monitoring: Community-based research in

xerente indigenous land, Brazilian Cerrado. Hum Ecol Rev [Internet]. 2017;23(1):23–44.

Available from: https://www.scopus.com/inward/record.uri?eid=2-s2.0-

85038815827&doi=10.22459%2FHER.23.01.2017.02&partnerID=40&md5=f35ffbb57e5cf9

6acc97f18422006b8f

43. Ferguson DB, Masayesva A, Meadow AM, Crimmins MA, Ferguson DB, Masayesva A, et al.

Rain Gauges to Range Conditions: Collaborative Development of a Drought Information

System to Support Local Decision-Making. Weather Clim Soc [Internet]. 2016;8(4):345–59.

Available from: http://journals.ametsoc.org/doi/10.1175/WCAS-D-15-0060.1

44. Fragoso JMV, Levi T, Oliveira LFB, Luzar JB, Overman H, Read JM, et al. Line transect

surveys underdetect terrestrial mammals: Implications for the sustainability of subsistence

hunting. PLoS One. 2016;11(4).

45. Iverson SA, Forbes MR, Simard M, Soos C, Gilchrist HG. Avian cholera emergence in arctic-

nesting northern Common Eiders: Using community-based, participatory surveillance to

delineate disease outbreak patterns and predict transmission risk. Ecol Soc. 2016;21(4).

46. Constantino PAL. Dynamics of hunting territories and prey distribution in Amazonian

Indigenous Lands. Appl Geogr. 2015;56:222–31.

47. Bellfield H, Sabogal D, Goodman L, Leggett M. Case study report: Community-based

242

monitoring systems for REDD+ in Guyana. Forests. 2015;6(1):133–56.

48. Gill H, Lantz T. A Community-Based Approach to Mapping Gwich’in Observations of

Environmental Changes in the Lower Peel River Watershed, NT. J Ethnobiol [Internet].

2014;34(3):294–314. Available from: http://www.bioone.org/doi/abs/10.2993/0278-0771-

34.3.294

49. Lagasse CR, Ou W, Honka LD, Atlas WI, Hutton CN, Kotaska J, et al. Design considerations

for community-based stream monitoring to detect changes in pacific salmon habitats.

Ecol Soc. 2014;19(4).

50. Housty WG, Noson A, Scoville GW, Boulanger J, Jeo RM, Darimont CT, et al. Grizzly bear

monitoring by the Heiltsuk people as a crucible for First Nation conservation practice.

Ecol Soc. 2014;19(2).

51. Ford JD, McDowell G, Shirley J, Pitre M, Siewierski R, Gough W, et al. The Dynamic

Multiscale Nature of Climate Change Vulnerability: An Inuit Harvesting Example. Ann

Assoc Am Geogr. 2013;103(5):1193–211.

52. Constantino P de AL, Carlos HSA, Ramalho EE, Rostant L, Marinelli CE, Teles D, et al.

Empowering local people through community-based resource monitoring: A comparison

of Brazil and Namibia. Vol. 17, Ecology and Society. 2012.

53. Luzar JB, Silvius KM, Overman H, Giery ST, Read JM, Fragoso JM V. Large-scale

Environmental Monitoring by Indigenous Peoples. Bioscience [Internet]. 2011;61(10):771–

81. Available from: https://academic.oup.com/bioscience/article-

lookup/doi/10.1525/bio.2011.61.10.7

54. Wesche S, Schuster RC, Tobin P, Dickson C, Matthiessen D, Graupe S, et al. Community-

based health research led by the Vuntut Gwitchin First Nation. Int J Circumpolar Health

[Internet]. 2011;70(4):396–406. Available from:

https://www.tandfonline.com/doi/full/10.3402/ijch.v70i4.17846

55. Marcoux M, Auger-Méthé M, Chmelnitsky EG, Ferguson SH, Humphries MM. Local passive

acoustic monitoring of Narwhal presence in the Canadian Arctic: A pilot project. Arctic.

2011;64(3):307–16.

56. Gearheard S, Aporta C, Aipellee G, O’Keefe K. The Igliniit project: Inuit hunters document

life on the trail to map and monitor arctic change. Can Geogr. 2011;55(1):42–55.

57. Ens EJ, Cooke P, Nadjamerrek R, Namundja S, Garlngarr V, Yibarbuk D. Combining

aboriginal and non-aboriginal knowledge to assess and manage feral water buffalo

impacts on perennial freshwater springs of the aboriginal-owned arnhem plateau,

Australia. Environ Manage. 2010;45(4):751–8.

243

58. Mahoney A, Gearheard S, Oshima T, Qillaq T. Sea ice thickness measurements from a

community-based observing network. Bull Am Meteorol Soc. 2009;90(3):370–7.

59. Setty RS, Bawa K, Ticktin T, Gowda CM. Evaluation of a participatory resource monitoring

system for nontimber forest products: The case of Amla (Phyllanthus spp.) fruit harvest by

Soligas in South India. Ecol Soc. 2008;13(2).

60. Constantino P de AL, Fortini LB, Kaxinawa FRS, Kaxinawa AM, Kaxinawa ES, Kaxinawa AP,

et al. Indigenous collaborative research for wildlife management in Amazonia: The case of

the Kaxinawá, Acre, Brazil. Biol Conserv. 2008;141(11):2718–29.

61. Tremblay M, Furgal C, Larrivee C, Annanack T, Tookalook P, Qiisik M, et al. Climate

Change in Northern Quebec: Adaptation Strategies from Community-Based Research.

Arctic. 2008;61:27–34.

62. Ohl-Schacherer J, Shepard GH, Kaplan H, Peres CA, Levi T, Yu DW. The sustainability of

subsistence hunting by Matsigenka native communities in Manu National Park, Peru.

Conserv Biol. 2007;21(5):1174–85.

63. Noss AJ, Cuéllar E, Cuéllar RL. An evaluation of hunter self-monitoring in the Bolivian

Chaco. Hum Ecol. 2004;32(6):685–702.

64. Noss AJ, Cuéllar RL. Community attitudes towards wildlife management in the Bolivian

Chaco. ORYX. 2001;35(4):292–300.

65. Torres AVG. Turning scientific approaches into practical conservation actions: The case of

Comunidad Indigena de Nuevo San Juan Parangaricutiro, Mexico. Environ Manage.

2001;27(5):655–65.

66. Brook RK, Kutz SJ, Veitch AM, Popko RA, Elkin BT, Guthrie G. Fostering community-based

wildlife health monitoring and research in the Canadian North. Ecohealth. 2009;6(2):266–

78.

67. Boissière M, Bastide F, Basuki I, Pfund JL, Boucard A. Can we make participatory NTFP

monitoring work? Lessons learnt from the development of a multi-stakeholder system in

Northern Laos. Biodivers Conserv. 2014;23(1):149–70.

68. Krause T, Zambonino H. More than just trees – animal species diversity and participatory

forest monitoring in the Ecuadorian Amazon. Int J Biodivers Sci Ecosyst Serv Manag

[Internet]. 2013;9(3):225–38. Available from:

http://www.tandfonline.com/doi/abs/10.1080/21513732.2013.822930

69. Larter NC. A PROGRAM TO MONITOR MOOSE POPULATIONS IN THE DEHCHO REGION,

NORTHWEST TERRITORIES, CANADA. ALCES. 2009;45:89–99.

244

70. Noss AJ, Oetting I, Cuéllar RL. Hunter self-monitoring by the Isoseño-Guaraní in the

Bolivian Chaco. Biodivers Conserv. 2005;14(11):2679–93.

71. Pacheco-Cobos L, Rosetti MF, Esquivel AM, Hudson R. Towards a traditional ecological

knowledge-based monitoring scheme: a proposal for the case of edible mushrooms.

Biodivers Conserv. 2015;24(5):1253–69.

72. Gratani M, Royee F, Butler JRA. A research process and criteria indicators framework for

developing indigenous freshwater ecosystem health monitoring. Cogent Environ Sci

[Internet]. 2016;2(1):1–14. Available from:

https://www.cogentoa.com/article/10.1080/23311843.2016.1214228

73. Kofinas G, Lyver POB, Russell D, White R, Nelson A, Flanders N. Towards a protocol for

community monitoring of caribou body condition. Rangifer. 2003;Special Is:29–38.

74. Lyver POB, Timoti P, Jones CJ, Richardson SJ, Tahi BL, Greenhalgh S. An indigenous

community-based monitoring system for assessing forest health in New Zealand.

Biodiversity and Conservation. 2016;1–30.

75. Van Vliet N, Sandrin F, Vanegas L, L’haridon L, Fa JE, Nasi R. High-tech participatory

monitoring in aid of adaptive hunting management in the Amazon. Unasylva.

2017;68(249):53–62.

76. Driscoll DL, Sunbury T, Johnston J, Renes S. Initial findings from the implementation of a

community-based sentinel surveillance system to assess the health effects of climate

change in Alaska. Circumpolar Heal Suppl [Internet]. 2013;72:946–54. Available from:

http://10.0.13.74/ijch.v72i0.21405%5Cnhttp://search.ebscohost.com/login.aspx?direct=tru

e&AuthType=ip,url,cookie,uid&db=aph&AN=109175649&site=ehost-live&scope=site

77. Driscoll DL, Mitchell E, Barker R, Johnston JM, Renes S. Assessing the health effects of

climate change in Alaska with community-based surveillance. Clim Change. 2016;137(3–

4):455–66.

78. de Mattos Vieira MR, von Muhlen E, Shepard G. Participatory Monitoring and

Management of Subsistence Hunting in the Piagaçu-Purus Reserve, Brazil. Conserv Soc

[Internet]. 2015;13(3):254. Available from:

http://www.conservationandsociety.org/text.asp?2015/13/3/254/170399

79. Obura DO. Participatory monitoring of shallow tropical marine fisheries by artisanal

fishers in Diani, Kenya. In: Bulletin of Marine Science. 2001. p. 777–91.

80. Pollock RM, Whitelaw GS. Community-based monitoring in support of local sustainability.

Local Environ. 2005;10(3):211–28.

81. Funder M, Ngaga Y, Nielsen M, Poulsen M, Danielsen F. Reshaping Conservation: The

245

Social Dynamics of Participatory Monitoring in Tanzania′s Community-managed Forests.

Conserv Soc [Internet]. 2013;11(3):218. Available from:

http://www.conservationandsociety.org/text.asp?2013/11/3/218/121011

82. Fidel M, Kliskey A, Alessa L, Sutton O (Olia) P. Walrus harvest locations reflect adaptation:

a contribution from a community-based observation network in the Bering Sea. Polar

Geogr. 2014;37(1):48–68.

83. Herrmann TM, Sandström P, Granqvist K, D’Astous N, Vannar J, Asselin H, et al. Effects of

mining on reindeer/caribou populations and indigenous livelihoods: Community-based

monitoring by Sami reindeer herders in Sweden and First Nations in Canada. Polar J.

2014;4(1):28–51.

84. Parlee BL, Goddard E, First Nation ŁKD, Smith M. Tracking Change: Traditional Knowledge

and Monitoring of Wildlife Health in Northern Canada. Hum Dimens Wildl. 2014;19(1):47–

61.

85. Cummings A, Cummings G, Hamer E, Moses P, Norman Z, Captain V, et al. Developing a

UAV-Based Monitoring Program with Indigenous Peoples. J Unmanned Veh Syst.

2017;5(4):115–25.

86. Van Rijsoort J, Jinfeng Z. Participatory resource monitoring as a means for promoting

social change in Yunnan, China. Biodivers Conserv. 2005;14(11):2543–73.

87. Sheil D, Boissière M, Beaudoin G. Unseen sentinels: local monitoring and control in

conservation's blind spots. Ecol Soc [Internet]. 2015;20(2). Available from:

http://www.ecologyandsociety.org/vol20/iss2/art39/

246

Appendix 4: Questions to guide deductive qualitative analysis conducted on United Nations

food security evaluation reports published from 2014 to 2019.

Category Definition

Context Describes the social, political, economic, environmental, cultural, and/or

organizational setting within which a food security program was evaluated.

Evaluation

approach

Describes the purpose of the evaluation, role of the stakeholders, stages of

evaluation, and/or method of data collection and analysis.

Challenges and

opportunities

Describes limitations, challenges, opportunities, lessons learned, and/or

recommendations of evaluating climate action.

247

Appendix 5. Codebook of climate-responsive food security evaluation challenges.

Theme / codes Description Example

1. Inadequate

resources for

evaluation

The quality of the evaluation function is dependent on the amount of

resources allocated and whether resources are sufficient to cover the

scope of the evaluation.

Limited

evaluation

resources

Describes limited

resources available for

the final evaluation

function conducted at

the end of the initiative

including human

resources, capacity, time,

funding, and logistics

support.

“Given the limited time and resources

available, it was not possible for the PPE to

visit all project locations, undertake extensive

quantitative surveys, or examine the full

spectrum of project activities, achievements

and drawbacks” (IFAD 11, p. 6).

“Limited evaluation resources”

2. Weak M&E

systems

The evaluation function depends on data, support, and experiences from

existing M&E systems; yet, M&E systems are constrained by resource

availability and M&E design issues, leading to data quality and quantity

challenges for the evaluation function.

Limited M&E

systems

resources

Describes limited

resources available for

M&E

planning/implementation

conducted throughout

the initiative including

human resources,

capacity, time, logistics,

and funding.

“Historically the CO’s M&E Unit has had

limited human resources and funding and this

remains the case. WFP has insufficient human

resources to undertake adequate monitoring

of its SF programme and relies on the MoE

CCs and DFPs” (WFP 25, p. 24).

M&E design

issues

Describes challenges in

the design of the M&E

system including

indicators, targets,

criteria, and data

collection.

“In-house M&E is also an issue – some

cooperating partners found it burdensome,

and the system does not enable the reasons

for the changes in beneficiaries’ food security

status to be attributed or improved resilience

to be measured” (WFP 1, p. 43).

M&E data quality

and/or quantity

Describes implications of

M&E systems on data

quality and quantity.

“Beneficiaries reported an increase in

agricultural production and improvements in

food security at the household level. However,

quantitative data in addition to the data from

the RIMS survey reported below are not

248

available to support the attribution of these

benefits to the project” (IFAD 11, p. 29).

“Limited M&E resources” OR “M&E design issues” OR “M&E data quality and quantity”

3. Limited

climate action

focus

Lack of climate action focus in programming leads to limited prioritization

of climate change in the evaluation design, and consequently, limited

activities, outputs, and outcomes to be assessed in the evaluation.

Climate-related

programming

Describes climate

considerations in the

program objectives,

components, or activities.

“… strengthen the resilience of rural

populations and agricultural production

systems in the central part of the cattle

corridor and build the capacity of

communities, commercial farmers and the

Government of Uganda to cope with climate

change” (FAO 4, p. 5).

Climate-related

evaluation

Describes climate

considerations in

evaluation methodology,

methods, or analysis

“Crosscutting issues such as gender and other

equity issues, human rights, climate change

and partnerships are addressed under each of

the evaluation questions” (FAO 1, p. 14).

Climate-related

outcomes

Describes climate-related

outcomes.

“Adaptation to climate change was not part of

the project design. However, this criterion is

assessed for two reasons: climate change is a

threat for a country like Guyana that is heavily

agriculture-based, and where parts of the

country are below sea level; and some of the

project's activities could have helped in

climate change adaptation” (IFAD 3, p. 24).

Implications of

climate focus

Describes implications of

lack of climate action

focus on climate action

assessment and

outcomes.

There was also no indication of contribution to

climate change adaptation over the life of the

3PAD project, even if the awareness and

reporting on severe weather events and the

negative effects on crops and livestock

increased over the 3PAD project life time”

(IFAD 2, p. 32).

“climate-related programming” OR climate-related evaluation” OR (“climate-related outcomes”

AND “implications of climate focus”)

4. Dependency

on food security

evaluations

That the final evaluation function relies on how food security evaluations

are conducted present challenges if the quality of food security

evaluations are poor.

Food security

measurement

challenges

Describes challenges of

measuring food security

including attribution,

“This issue of attribution also arises strongly in

the sustainable agriculture development

component. There are a range of other

249

data availability, and data

quality.

programmes supporting agriculture in the

CBARDP states” (IFAD 40, p. 25).

Influence of

external factors

on food security

measurement

Describes influence of

external factors on food

security measurement

including climate change,

animal/crop diseases,

and poverty.

“Performance on results measurement for the

PRRO has been very minimal, for a variety of

reasons, of which the main ones are lack of a

well-developed M&E system, attribution

problems, dependability of food security on

external factors like rainfall and access to

agricultural inputs, incomplete sets of final

reports prepared by the partners, etc.” (WFP 3,

p. 40).

“Food security measurement challenges” OR “influence of external factors on food security

measurement”

250

Appendix 6. Codebook of climate-responsive food security evaluation solutions.

Theme Description Example

5. Invest in M&E

systems

To integrate climate action considerations into food security evaluations, a

strong M&E foundation is needed.

Provide

evaluation

support

Describes the need for

evaluation support

including mentoring,

guidance documents, or

manuals.

“Support the teams of future projects to

develop simple and effective devices for

monitoring and evaluation through the

development of a manual or monitoring-

evaluation guide and set up a database of the

project to contribute to better supervision

and better capitalization of actions and

results of future projects” (UNDP 1, p. 41).

Invest resources Describes the need for

resources including

human resources,

capacity, time, and

funding, communication,

and logistics support.

“Recommendation 4. Ensure sufficient

investment in and support for M&E, analytical

studies and documentation” (IFAD 3, p. 37).

Focus on

outcomes

Describes the value of

assessing outcomes /

impacts over activities /

outputs.

“The collection of the mass of output data

leaves limited space and time for the

collection of more detailed and useful

information on impact, attribution, and the

strength and sustainability of institutions

formed– issues which will be particularly

important in the move towards resilience

programming” (WFP 10, p. 48).

Link to decision-

making

Describes the need to link

data collection to data

needs of decision-makers.

“In terms of developing methods to measure

resilience and gathering and analysing data

for decisions, data need to be better linked to

decision making and the needs of decision

makers. FAO should better coordinate

activities so that resilience measurement

occurs in the same areas where social

protection analysis and policy and capacity

development are occurring” (FAO 5, p. 6).

“Strengthen evaluation capacity” OR “provide evaluation guidance” OR “invest resources” OR

“focus on outcomes” OR “link to decision-making”

251

6. Prioritize

climate action in

programming

Climate change considerations should be integrated into program and

evaluation planning.

Include climate

action strategies

Describes the importance

for programs to include

climate action goals,

strategies, or plans.

“Climate change is expected to have various

effects, requiring different coping strategies

for affected people in Guatemala’s diverse

eco-geographical environment. To enhance

impacts, FFA programming should pay more

attention to environmental factors” (WFP 4, p.

xiii).

Integrate climate

change in

program theory

Discusses how climate

change is integrated into

the program theory, logic,

or impact pathway.

See FAO 3, FAO 4, and UNEP 1.

Measure climate

action outcomes

Describes the need to

systematically measure

climate action outcomes

alongside food security

outcomes.

“Resilience measurement should be more

effectively linked to programme and policy

work carried out by FAO and should be more

crosscutting, linking to social protection,

nutrition and Disaster Risk Reduction” (FAO 5,

p. 6).

“include climate action strategies” OR “integrate climate change in program theory” OR

“measure climate action outcomes”

7. Prioritize

climate action in

evaluation.

During the conduct of the evaluation, it is important to integrate climate

change in throughout evaluation processes and products.

Climate change

as a cross-cutting

theme in the

evaluation

Describes the need to

integrate climate change

as a cross-cutting theme

in the evaluation.

“Crosscutting issues such as gender and other

equity issues, human rights, climate change

and partnerships are addressed under each of

the evaluation questions” (FAO 1, p. 14).

Climate action

co-benefits

Describes co-benefits of

climate action.

“The ET identified a number of environmental

benefits from the CO’s use of FFA to build

productive assets… There was also

widespread support for the FFA component’s

focus on water resources management

because of its ability to address Productive

(irrigation/drought) and Risk (drainage/ flood)

vulnerabilities at the target sites” (WFP 10, p.

19).

252

Climate action

trade-offs

Describes trade-offs of

climate action.

“The strategic choice to envisage an in-depth

community consultation processes, as was

done with the Joint Resilience Programme, is

very positive and consistent with the

resilience building aim. However, priorities

and trade-offs between different components

within a programme aiming to improve

something as broad as ‘resilience’ need to be

managed…” (FAO 8, p. 76).

Assess relevance

to climate

agendas

Describes a need for

establishing program

coherence with climate-

related programs,

policies, or strategies of

the national government

or UN entity.

“Given the thematic areas covered by the

PRRO, and especially with the introduction of

SO2 in July 2013, it could have been relevant

for the PRRO to seek coherence with national

policies and strategies focusing on rural

development, food security and adaptation

and mitigation to climate changes, and as

such to develop forms of coordination with

some technical directions of the Ministries in

charge of Agriculture, Livestock and

Environment” (WFP 3, p. 12).

Develop and

apply climate-

responsive M&E

tools

Describes the need for

dedicated tools to

account for climate action

outcomes.

“There is a need to provide useful and readily

available information and analysis tools to

stakeholders in order to allow them to

identify and take advantage of climate

change mitigation opportunities linked to

food security, resilience, adaptation and rural

development goals” (FAO 6, p. 36).

“Climate change as a cross-cutting theme in evaluation” OR “climate action co-benefits” OR

“climate action trade-offs” OR “assess relevance to climate agendas” OR “develop and apply

climate-responsive M&E tools”

253

Appendix 7: Thematic map of challenges and opportunities for climate-responsive evaluation.

Challenges are presenting in the upper half and opportunities are presented in the lower half.

Dotted arrows represent relationships between themes. Positive and negative signs highlight

feedback loops; for example, increasing investment in M&E systems (+) will mitigate weaknesses

in M&E systems (-), leading to increase in climate evaluation (+).

254

Appendix 8: List of all included United Nations food security evaluation reports published from

2014 to 2019.

Author Title Year

FAO 1 Final evaluation of Sudan Food Security Policy and Strategy Capacity

Building programme

2017

FAO 2 Final Evaluation of the Project “Strengthening Climate Change Resilience

and Disaster Risk Reduction in Agriculture to Improve Food Security in

Haiti After the Earthquake”

2018

FAO 3 Final Evaluation of the Project “Integrating Climate Resilience into

Agricultural Production for Food Security in Rural Areas of Mali”

2018

FAO 4 Final Evaluation of the Global Climate Change Alliance (GCCA) – Uganda:

Agricultural Adaptation to Climate Change project

2017

FAO 5 Final evaluation of the Improved Global Governance for Hunger

Reduction Programme

2016

FAO 6 Final Evaluation of “Monitoring and Assessment of GHG Emissions and

Mitigation Potentials in Agriculture Project” - GCP /GLO/286/GER

2014

FAO 7 Final Evaluation of the Project: "Management of Chimborazo’s Natural

Resources"

2019

FAO 8 Final Evaluation of the Joint Resilience Project in Kassala 2018

FAO 9 Final evaluation of the project “Mainstreaming the use and conservation

of agrobiodiversity in public policy through integrated strategies and in

situ implementation in four Andean Highlands provinces

2018

FAO 10 Final Evaluation of the Conservation Agriculture Scaling-Up (CASU)

Project Funded by the European Union

2018

FAO 11 Evaluation of the Benefit-sharing Fund second project cycle International

Treaty on Plant Genetic Resources for Food and Agriculture

2017

FAO 12 Evaluation of the Emergency Prevention System (EMPRES) Programme in

Food Chain Crises

2018

FAO 13 Final evaluation of the project “Climate Change Adaptation to Reduce

Land Degradation in Fragile Micro-Watersheds located in the

Municipalities of Texistepeque and Candelaria de la Frontera”

2019

FAO 14 Final Evaluation of the Project for Building Resilience and Self-reliance of

Livestock Keepers by Improving Control of Foot-and-Mouth Disease and

other Transboundary Animal Diseases in Afghanistan

2019

FAO 15 Final Evaluation of the Project on Decentralized Supply and Water Use

Management in the Sana’a Basin to Sustain Water Resources and Rural

Livelihoods

2019

FAO 16 Final Evaluation of the project “Forestry and Protected Area

Management in Fiji, Samoa, Vanuatu and Niue (GEFPAS-FPAM)”

2017

255

FAO 17 Final Evaluation of the Project “Increased Household Food, Income and

Nutrition Security through Commercialization of an Integrated and

Sustainable Smallholder Livestock Sector in Zimbabwe”

2018

FAO 18 Final Evaluation of the Programme for Improvement of Irrigation

Systems in Kabul, Bamyan and Kapisa Provinces

2017

FAO 19 Evaluation of the project on Strategies for Trawl Fisheries Bycatch

Management

2017

FAO 20 Final evaluation of the project: Food Security and Nutrition Analysis Unit

for Somalia

2017

FAO 21 Final evaluation of Capacity building for South African Professionals in

the Field of Agriculture and Food Security (GCP/RAF/412/SAF)

2017

FAO 22 Final Evaluation of the Groundwater Governance: A Global Framework

for Action

2016

FAO 23 Establishing a sustainable National Information and Early Warning

System (NIEWS) on Food Security in Timor-Leste

2016

FAO 24 End of project evaluation report of the Programme for Improvement of

Irrigation Systems and Construction of Micro-hydro Power Facilities in

Kabul and Bamyan Provinces and Mid-term evaluation report of the

Programme for Improvement of Irrigation Systems in Kabul and Bamyan

Provinces

2014

FAO 25 End of project evaluation report of the Programme for Improvement of

Irrigation Systems and Construction of Micro-hydro Power Facilities in

Kabul and Bamyan Provinces and Mid-term evaluation report of the

Programme for Improvement of Irrigation Systems in Kabul and Bamyan

Provinces

2014

FAO 26 Final Evaluation of the Project for Assistance to the Recovery and

Development of the Agricultural Economy in the Federally Administered

Tribal Areas (FATA) of Pakistan

2018

FAO 27 Final Evaluation of the Project “Building a Global Agenda of Action in

Support of Sustainable Livestock Sector Development”

2019

FAO 28 Final Evaluation of the Institutional Level Component of the Project

“Support for Livestock-based Livelihoods of Vulnerable Populations in

the Occupied Palestinian Territory"

2018

FAO 29 Final Evaluation of the Project “Capacity Development of the Irrigation

Department of the Ministry of Agriculture, Irrigation and Livestock of the

Islamic Republic of Afghanistan”

2018

FAO 30 Final evaluation of the Global Programme to Support the

implementation of the Voluntary Guidelines on the Responsible

Governance of Tenure of Land, Fisheries and Forests (2012 – 2016)

2017

256

FAO 31 Final Evaluation of the Environmentally Sustainable Food Security

Programme (ESFSP)

2017

FAO 32 Final evaluation of Sustainable Management of the Bay of Bengal Large

Marine Ecosystem (BOBLME) project

2016

FAO 33 Final Evaluation of Agriculture and Food Information Systems for

Decision Support in South Sudan

2016

FAO 34 Evaluation of the project Protecting and Improving Household Food

Security and Nutrition in HIV/AIDS Affected Areas in Manica and Sofala

Provinces. GCP/MOZ/079/BEL

2015

FAO 35 Final evaluation of the project “Securing tenure rights for forest

landscape-dependent communities: linking science with policy to

advance tenure security, sustainable forest management and people’s

livelihoods”

2019

FAO 36 Evaluation of the Global Strategy to Improve Agricultural and Rural

Statistics (GSARS)

2019

FAO 37 Evaluation of the project on Mainstreaming Food and Nutrition Security

and the Right to Food into the Smallholder Commercialization

Programme of Sierra Leone

2016

FAO 38 Final Evaluation of the Project “Strengthening Agricultural Market

Information Systems Globally and in Selected Countries (Bangladesh,

India and Nigeria) Using Innovative Methods and Digital Technology”

2017

FAO 39 Final Evaluation of “Progressive Control of Peste des Petits Ruminants in

Pakistan”

2017

FAO 40 Final evaluation of the project National Food Security Information

System in Kyrgyzstan

2015

FAO 41 Final Evaluation of the Project, Development of a Framework for the

Progressive Control of Foot and Mouth Disease in Pakistan

2016

FAO 42 The Agribusiness Support for Smallholders Project in Kenya –

GCP/KEN/070/GER

2014

FAO 43 Final evaluation of the project Education for Effective Nutrition in Action

(ENACT)

2016

FAO 44 Final Evaluation of the Integrated Food Security Phase Classification

(IPC) Global Strategic Programme (GSP) 2014 -2018

2019

IFAD 1 Pastoral Community Development Project II 2016

IFAD 2 Pro-poor partnerships for agroforestry development project 2018

IFAD 3 Rural enterprise and agricultural development project 2018

IFAD 4 Post-Tsunami Agricultural and Fisheries Rehabilitation Programme 2017

IFAD 5 Root and tuber improvement and marketing programme 2018

257

IFAD 6 Rural Livelihoods Improvement Project in Kratie, Preah Vihear and

Ratanakiri

2017

IFAD 7 Post-tsunami coastal rehabilitation and resource management

programme

2017

IFAD 8 Rural Livelihoods Support Programme (2017) 2017

IFAD 9 Finance for Enterprise Development and Employment Creation Project 2016

IFAD 10 Kenya: Smallholder horticulture marketing programme 2018

IFAD 11 Northern region sustainable livelihoods through livestock development

project

2018

IFAD 12 Participatory Natural Resource Management Programme 2017

IFAD 13 Georgia: Agricultural Support Project 2017

IFAD 14 West Noubaria Rural Development Project 2017

IFAD 15 Republic of Mozambique: Sofala Bank Artisanal Fisheries Project 2016

IFAD 16 Rural Microenterprise Promotion Programme 2016

IFAD 17 Rural Livelihoods Improvement Programme in Attapeu and Sayabouri 2015

IFAD 18 Gente de Valor - Rural Communities Development Project in the Poorest

Areas of the State of Bahia

2015

IFAD 19 India: Jharkhand Chhattisgarh Tribal Development Programme 2015

IFAD 20 Community Development Programme 2015

IFAD 21 Programme for Sustainable Development in Rural Mountain Areas 2015

IFAD 22 Gash Sustainable Livelihoods Regeneration Project 2014

IFAD 23 Sustainable Agriculture and Natural Resource Management Programme 2014

IFAD 24 Rural Development Project in the Mountain Zones of Al-Haouz 2014

IFAD 25 Agriculture, Marketing and Enterprise Promotion Programme 2014

IFAD 26 Rural Development Programme for Mountainous and Highland Areas 2014

IFAD 27 Microfinance for Marginal and Small Farmers Project 2014

IFAD 28 Rural Financial Services and Agribusiness Development Project 2019

IFAD 29 Agricultural Investments and Services Project 2016

IFAD 30 Livelihoods Improvement Project in the Himalayas 2015

IFAD 31 Support Project for the Strategic Plan for the Transformation of

Agriculture

2015

IFAD 32 Western Uplands Poverty Alleviation Project 2019

IFAD 33 Kirehe Community-based Watershed Management Project 2019

IFAD 34 Rural Finance and Enterprise Development Programme 2019

IFAD 35 Smallholder Plantations Entrepreneurship Development Programme 2019

IFAD 36 Northern Region Sustainable Livelihoods through Livestock

Development Project

2018

IFAD 37 Rural Financial Intermediation Programme 2017

IFAD 38 Rural Diversification Programme 2014

258

IFAD 39 Environment Conservation and Poverty-Reduction Programme in

Ningxia and Shanxi

2016

IFAD 40 Community-Based Agricultural and Rural Development Programme 2016

IFAD 41 Sivas-Erzincan Development Project 2015

UNDP 1 Final evaluation of the project "building the capacity of the agriculture

sector in DR Congo to plan for and respond to the additional threats

posed by climate change on food production and security" or pana-asa

project DR Congo

2015

UNDP 2 TUVALU NATIONAL PROGRAMME OF ACTION: INCREASING RESILIENCE

OF COASTAL AREAS AND COMMUNITY SETTLEMENTS TO CLIMATE

CHANGE IN TUVALU

2017

UNDP 3 TERMINAL EVALUATION: ADDRESSING CLIMATE CHANGE RISKS ON

WATER AND FOOD SECURITY IN THE DRY ZONE OF MYANMAR

2019

UNDP 4 TERMINAL EVALUATION OF ENABLING ENVIRONMENT FOR SLM TO

OVERCOME LAND DEGRADATION IN THE UGANDA CATTLE CORRIDOR

DISTRICTS OF UGANDA

2016

UNDP 5 TERMINAL EVALUATION OF ENHANCING ADOPTION OF CLIMATE

SMART AGRICULTURE PRACTICES IN UGANDA'S FARMING SYSTEMS

2016

UNDP 6 EVALUATION OF FOOD & NUTRITION SECURITY PROJECT IN JORDAN

TOWARDS POVERTY ALLEVIATION

2014

UNDP 7 Evaluation of Improved Seed Production for Sustainable Agriculture and

Reduction of Post-Harvest Losses for Food Security projects

2014

UNDP 8 Evaluation of Improved Seed Production for Sustainable Agriculture and

Reduction of Post-Harvest Losses for Food Security projects

2014

UNDP 9 PROMOTION OF DEVELOPMENT AND CONFIDENCE BUILDING IN THE

CHITTAGONG HILL TRACTS FINAL EVALUATION

2015

UNEP 1 TERMINAL EVALUATION OF UNEP GEF PROJECT: A GLOBAL INITIATIVE

ON LANDSCAPES FOR PEOPLE, FOOD AND NATURE

2015

UNEP 2 Terminal Evaluation of the UNDA 7th Tranche funded UNEP project:

Capacity Building in National Planning for Food Security

2016

UNEP 3 Terminal Evaluation of the UN Environment Project: Resource Efficiency

and Eco-Innovation in Developing and Transition Economies

2017

UNEP 4 TERMINAL EVALUATION OF THE UNEP GEF PROJECT: REDUCING

DEPENDENCE ON POPS AND OTHER AGRO-CHEMICALS IN THE

SENEGAL AND NIGER RIVER BASINS THROUGH INTEGRATED

PRODUCTION, PEST AND POLLUTION MANAGEMENT

2016

UNICEF

1

2017 Uganda: End of project Evaluation Enhanced Resilience Karamoja

Program (ERKP)

2017

259

UNICEF

2

2016 Pakistan: Evaluation of Humanitarian Actions - Nutrition

Emergency Response in District Tharparkar, Sindh, Pakistan

2016

UNICEF

3

2018 Ethiopia: Summative Evaluation of the Nutrition Component of the

EU-SHARE program in Ethiopia (2015-2018)

2018

UNICEF

4

2016 Malawi: Evaluation of Community Management of Acute

Malnutrition (CMAM) in Malawi

2016

UNICEF

5

2018 Lesotho: Impact evaluation of Lesotho’s Child Grants Programme

(CGP) and Sustainable Poverty Reduction through Income, Nutrition and

access to Government Services (SPRINGS) project

2018

UNICEF

6

2018 Korea: Evaluation of Community-based Management of Acute

Malnutrition Programme supported by UNICEF in DPR Korea 2015–2017

2018

UNICEF

7

2016 ROSA/EAPRO: Maternal and Young Child Nutrition Security

Initiative in Asia [MYCNSIA]: External Evaluation of the EU-UNICEF

Partnership 2011-2015

2016

UNICEF

8

2016 ESARO/WCARO: Evaluation of the EU/UNICEF Partnership on

Nutrition Security

2016

UNICEF

9

2019 Pakistan: United Nations Maternal and Child Stunting Reduction

Programme in three target Districts in Sindh, Pakistan

2019

UNICEF

10

Zimbabwe’s Harmonised Social Cash Transfer Programme Endline

Impact Evaluation Report

2018

UNICEF

11

Impact evaluation of Lesotho’s Child Grants Programme (CGP) and

Sustainable Poverty Reduction through Income, Nutrition and access to

Government Services (SPRINGS) project

2018

WFP 1 Zimbabwe PRRO 200453 Responding to Humanitarian Needs and

Strengthening Resilience to Food Insecurity: An Operation Evaluation

2014

WFP 2 Tajikistan PRRO 200122 Restoring Sustainable Livelihoods for Food-

Insecure People: An Operation Evaluation

2014

WFP 3 Madagascar PRRO 200065 Response to Recurrent Natural Disasters and

Seasonal Food Insecurity

2014

WFP 4 Food for Assets on Livelihood Resilience in Guatemala: An Impact

Evaluation

2014

WFP 5 Food for Assets on Livelihood Resilience in Senegal: An Impact

Evaluation

2014

WFP 6 Food for Assets on Livelihood Resilience in Uganda: An Impact

Evaluation

2014

WFP 7 The Gambia PRRO 200557 Targeted Nutrition and Livelihood Support

for Vulnerable People Impacted by Floods and Drought: An Operation

Evaluation

2016

WFP 8 Bangladesh, School Feeding Programme (2015-2017): an evaluation 2018

260

WFP 9 Ethiopia, School Feeding Programme: an evaluation 2018

WFP 10 Cameroon PRRO 200552 Food and Nutrition Assistance to Nigerian and

Central African Refugees and Host Populations in Cameroon: An

Operation Evaluation

2016

WFP 11 Kenya, Food for Education and Child Nutrition: an endline evaluation 2017

WFP 12 Myanmar PRRO 200299 "Supporting Transition by Reducing Food

Insecurity and Undernutrition among the Most Vulnerable": An

Operation Evaluation

2017

WFP 13 Ethiopia PRRO 200700 (2015-2018) Food Assistance for Eritrean, South

Sudanese, Sudanese and Somali Refugees: An Operation Evaluation

2016

WFP 14 Philippines PRRO 200296 Support for Returnees and Other Conflict

Affected Households in Central Minanao, and National Capacity

Development in Disaster Preparedness and Response: An Operation

Evaluation

2014

WFP 15 Pakistan, Food Assistance to Temporarily Dislocated Persons (2015-

2017): an evaluation

2018

WFP 16 Algeria PRRO 200301: Evaluation of the Nutrition Components 2018

WFP 17 Malawi, School Meals Programme (2013-2015): an evaluation 2018

WFP 18 Sierra Leone, PRRO 200938: an evaluation 2018

WFP 19 Kenya PRRO 200174 Food Assistance to Refugees (2011-2013): An

Operation Evaluation

2014

WFP 20 Swaziland DEV 200422 Support to children and students affected by HIV

and AIDS (2013-2014): An Operation Evaluation

2014

WFP 21 Swaziland DEV 200422 Support to children and students affected by HIV

and AIDS (2013-2014): An Operation Evaluation

2014

WFP 22 Cambodia, United States Department of Agriculture (USDA) McGovern-

Dole Grant Food for Education Programme: An Endline Evaluation

2018

WFP 23 Impact Evaluation of WFP’s Fresh Food Voucher Pilot Programme in

Ethiopia

2019

WFP 24 Laos, School Feeding Programme (2014-2016): an endline evaluation 2018

WFP 25 Liberia, Food for Education and Child Nutrition: an evaluation 2017

WFP 26 Liberia PRRO 200550 Food Assistance For Refugees And Vulnerable Host

Populations: An Operation Evaluation

2016

WFP 27 India, Target Public Distribution Reforms in Bhubaneswar: Evaluation 2019

261

Appendix 9: Performance of United Nations food security evaluations published from 2014 to

2019 (n = 136) according to components of the climate assessment rubric.

Category 0 points 1 point 2 points 3 points

Evaluation scope 50 (36.8%) 65 (47.8%) 21 (15.4%) N/A

Evaluation approach 126 (92.6%) 10 (7.4%) N/A N/A

Evaluation results 38 (27.9%) 57 (41.9%) 7 (5.1%) 34 (25.0%)

262

Appendix 10: Climate change mandates of United Nations agencies.

Box 1. Climate change mandates of United Nations agencies.

UN agencies are driving many aspects of global food systems. Below, we outline the mandates of UN

agencies related to climate change action according to most-up-to-date policy or strategy document.

According to UNDP’s 2015 Social and Environmental Standards, UNDP ensures that all of its projects

are sensitive to climate change and disaster risks and do not contribute to increased vulnerability to

climate change and natural hazards.

According to WFP’s 2017 Climate Change Policy, WFP’s goal is to support food-insecure communities

in building their capacities to address the impacts of climate change on hunger. WFP will do so

through three main disaster risk reduction objectives.

According to FAO’s 2017 Strategy on Climate Change, climate action is a cross-cutting theme of FAO’s

strategic framework and is being integrated into every facet of FAO’s work.

According to IFAD’s 2019 Strategy and Action Plan on Environment and Climate Change, IFAD will

address environment and climate change across all of IFAD’s policies, strategies, and operations.

According to UNEP’s 2008 Climate Change Strategy, climate change is one of the six cross-cutting

thematic priorities in UNEP’s medium-term strategy.

According to UNICEF’s 2015 Strategic Framework on Environmental Sustainability for Children, UNICEF

is committed to increase its contribution to environmental sustainability. Five priorities were outlined

such as strengthening UNICEF policy and guidance on environmental sustainability as a cross-cutting

issue.

263

Appendix 11: Comparison between average climate action integration score of United Nations

evaluations and average program duration.

UN agency Average climate change

integration score

Median program duration

(years)

UNDP 3.3 3

WFP 2.4 3

FAO 2.3 4

IFAD 1.9 8

UNEP 1.3 3

UNICEF 0.7 2

264

Appendix 12: Comparison in climate-related reporting between high and low scoring climate

action integration of United Nations evaluations.

High climate action integration Low climate action integration

- Evaluation of a protracted relief and

recovery program focused on restoring

sustainable livelihoods in Tajikistan (WFP 2)

- Program timeline: 2010 to 2014

- Context outlined risks of Tajikistan to

disasters including floods and drought

- Assessed whether climate change

adaptation principles were integrated in the

program

- Presented climate-related outcomes and

recommended the development of a country

strategy that includes contingency plans

framed by a broader context analysis

(including climate risk and regional insecurity)

beyond food insecurity

- Evaluation of a protracted relief and

recovery program focused on food assistance

to refugees in Kenya (WFP 19)

- Program timeline: 2011 to 2014

- Context outlined the impact of more

extreme and frequent droughts in Kenya

- Logic model mentioned the risk of droughts

and floods on program impacts

- Stated the program objective of

contributing to disaster preparedness and

mitigation “cannot be adequately measured

due to lack of data” (p. 46)

- Evaluation of a food security policy in Sudan

(FAO 1)

- Program timeline: 2012 to 2015

- Context mentioned climatic variability

resulting in recurrent droughts and floods

- Stated crosscutting issues of climate change

were addressed under evaluation questions

- Presented outcomes related to drought and

flood response

- Evaluation of a food information systems

program in Sudan (FAO 33)

- Program timeline: 2013 to 2015

- No mention of climate change in the

context or methods section

- Findings included the effectiveness of the

program in contributing to the collection,

analysis, and dissemination of food security

information such as climate

- Evaluation of a climate change resilience

building program in Tuvalu (UNDP 2)

- Program timeline: 2009 to 2016

- Context mentioned the vulnerability of

Tuvalu to the impacts of climate change

- Several indicators reflected climate

considerations (e.g. % of planners with

improved understanding of climate change

risks and adaptation measures)

- Presented outcomes related to enhanced

capacity of communities in identifying

climate-related risks

- Evaluation of a program aiming to build

capacity of institutions in community

development in Bangladesh and India (UNDP

9)

Program timeline: 2003 to 2015

- No mention of climate change in the

context or methods section

- Findings included the increase use of

cooking stoves, reducing the impact of

firewood use on climate change

265

Appendix 13: Search strategy used to identify Theory of Change and Realist Evaluation studies

from AGRICOLA©, CabDirect©, Web of Science™ CORE Collection, Medline®, Scopus®, EconLit©,

and Google™.

Database/search engine/website Search string

- AGRICOLA©

- CabDirect©

- Web of Science™ CORE Collection

- Medline®

- Scopus®

- EconLit©

(food OR agriculture OR nutrition OR livestock OR

fish* OR animal OR plant OR wildlife) AND ((“theor*

of change”) OR (realist AND evaluation) OR (realism

AND evaluation))

Google™ a 1) “food security” AND “theory of change”

2) “food security” AND “realist evaluation”

Theory of Change community b food

CGSpace c “theory of change” AND “realist evaluation” a We conducted two Google™ searches using the search string (“food security” AND “theory of

change”) and (“food security” AND “realist evaluation”). The first 100 sources from each Google™

search were reviewed for inclusion in the review. As Google™ returns results based on relevance

criteria related to the search term entered, every 50 sources were reviewed. If deemed relevant,

the next source (e.g. 51st, 52nd, and so on) were reviewed until a source not relevant to the

search goal was found at which point another 50 sources were skipped to check for relevancy.

This process was repeated until the 500th source (as in Kouril et al. 201615). b We selected this resource for their repository of Theory of Change related publications. c We selected this resource because the Consultative Group on International Agricultural

Research (CGIAR) is a major feature in the agri-development space with 15 research centres

headquartered in 15 countries. Theories of Change and related impact pathways are important

evaluation tools used by CGIAR research centres.

15 Kouril D, Furgal C and Whillans T (2016) Trends and key elements in community-based monitoring: a systematic

review of the literature with an emphasis on Arctic and Subarctic regions. Environmental Reviews 24(2): 151–163.

DOI: 10.1139/er-2015-0041.

266

Appendix 14: Summary of the screening tools used in the title and abstract screening stage and

full text screening stage to identify relevant Theory of Change and realist evaluation studies.

Title and abstract screening questions and responses (level 1) a

Does this study describe the development, implementation, and/or evaluation of a food

security program?

Food security: a situation that exists when all people, at all times, have physical, social and

economic access to sufficient, safe and nutritious food that meets their dietary needs and food

preferences for a healthy life.

• Yes – include

• No – exclude (if no, questions 2 and 3 are skipped)

• Unsure - include

Does this study explicitly mention using a Theory of Change and/or Realist Evaluation

approach?

Theory of Change is an ongoing process of reflection to explore change and how it happens –

and what that means for the part we play in a particular context, sector and/or group of people.

ToC is often presented as a visual depicting the change pathway. Realist evaluation is a member

of a family of theory-based evaluation approaches which begin by clarifying the ‘program

theory’: the mechanisms that are likely to operate, the contexts in which they might operate and

the outcomes that will be observed if they operate as expected.

• Yes – include

• No – exclude (if no, question 3 is skipped)

• Unsure – include

Is this an individual research study and published in a journal or report?

Exclude conference abstracts, letters to the editor, news articles, dissertations, and reviews

• Yes – include

• No – exclude

• Unsure – include

Title and abstract screening questions and responses (level 2)

Does this study describe the development, implementation, and/or evaluation of a food

security program?

Food security: a situation that exists when all people, at all times, have physical, social and

economic access to sufficient, safe and nutritious food that meets their dietary needs and food

preferences for a healthy life.

• Yes – include

• No – exclude

Does this study explicitly mention using a Theory of Change and/or Realist Evaluation

267

approach?

Theory of Change is an ongoing process of reflection to explore change and how it happens –

and what that means for the part we play in a particular context, sector and/or group of people.

ToC is often presented as a visual depicting the change pathway. Realist evaluation is a member

of a family of theory-based evaluation approaches which begin by clarifying the ‘program

theory’: the mechanisms that are likely to operate, the contexts in which they might operate and

the outcomes that will be observed if they operate as expected.

• Yes – include

• Yes but not used correctly as per definitions of ToC and/or RE – exclude

• No – exclude

Is this an individual research study and published in a journal or report?

Exclude conference abstracts, letters to the editor, news articles, dissertations, and reviews

• Yes – include

• No – exclude a For level one screening, these criteria were stacked (i.e., if the first criterion is not met, then the

second two criteria will not be not examined). For level two screening, all of these criteria were

examined.

268

Appendix 15: The data charting form used to extract relevant information from Theory of

Change and Realist Evaluation studies.

Guiding questions Response type Response options

Characteristics of included studies

What year was the study

published online?

Radio (i.e.

select one)

2011; 2012; 2013; 2014; 2015; 2016; 2017;

2018; 2019; 2020

Is this study from the

published or grey

literature?

Radio Published literature (e.g. research article,

letter, review);

Grey literature (e.g. workshop report,

research report, book chapter)

What food security topic(s)

did the study focus on? a

Checkbox Nutrition (addresses malnutrition,

including overnutrition, undernutrition,

and associated conditions such as

stunting);

Agricultural productivity (supports the

production and productivity of crop,

livestock, and aquaculture systems);

Market-based (supports consumer

linkage to markets, value chain

development, and agri-food business

development);

Climate change (supports adaptation of

food systems to climate change);

Agricultural innovation systems

(supports collective action and

coordination, exchange of knowledge

among diverse actors, and enabling

conditions that make it possible for

actors to innovate);

Natural resource management

(supports the sustainable management,

use, and protection of forests, land, soil,

water, and biodiversity)

Food safety (addresses threats to food

security from food-borne diseases)

Community food security (address

needs and priorities within a local food

system)

Food security risk management

269

(supports management of risks including

marketing mechanisms and financial

insurance.

Food loss (supports efforts to reduce

food loss and waste including improved

harvesting techniques, on-farm storage,

and infrastructure)

What was the scale of the

study?

Checkbox Local (community level);

Provincial (regional level);

National (country level);

International (more than one country)

What region(s) was the

study conducted in?

Checkbox North America; South America; Europe;

Asia; Africa; Australia and Oceania; Not

applicable

Theory of Change studies

Did this study include a

ToC?

If yes, the following

questions below are asked:

Radio Yes; No; Not applicable

What was the purpose of

the ToC?

Checkbox Program planning; Program

implementation; Program evaluation;

Other (specify)

What evaluation approach

was used?

Checkbox Qualitative (workshops, group

discussions/meetings, interviews);

Quantitative (surveys, experiments);

Mixed qualitative-quantitative (uses

both qualitative and quantitative

methods);

Not applicable (study did not specify

characteristics of case studies);

Not specified (study did not provide

sufficient detail to categorize the

evaluation approach)

Who was involved in the

development of the ToC?

Checkbox Program staff; Program participants;

Evaluation team; Funders; Other (specify)

Did the ToC mention the

influence of contextual

factors on the program?

Radio

Yes; No; Not applicable

270

If yes, which?

Checkbox

Cultural (beliefs, attitudes, and practices

of participants);

Socio-economic (distribution of social

and economic resources);

Environment (features of the physical

environment);

Political (the political landscape);

Other (specify)

Was climate change (i.e.

climate change adaptation,

mitigation, impacts)

mentioned in the outcome

of the ToC (i.e. program

theory)?

Radio Yes; No; Not applicable

Did the study disaggregate

data by social identity?

If yes, which?

Radio

Checkbox

Yes; No; Not applicable

Age; Gender; Population (e.g. Indigenous

peoples); Other

Realist Evaluation studies

Did this study include a RE?

If yes, the following

questions below are asked:

Radio Yes; No; Not applicable

What is the purpose of the

RE?

Checkbox Program planning; Program

implementation; Program evaluation;

Other (specify)

What evaluation approach

was used?

Checkbox Qualitative (workshops, group

discussions/meetings, interviews);

Quantitative (surveys, experiments);

Mixed qualitative-quantitative (uses

both qualitative and quantitative

methods);

Not applicable (study was a

conceptual/theoretical paper);

Not specified (study did not provide

sufficient detail to categorize the

evaluation approach)

271

Who was involved in the

development of the RE?

Checkbox Program staff; Program participants;

Evaluation team; Funders; Other (specify)

Did the RE mention the

influence of contextual

factors on the program?

If yes, which?

Radio

Checkbox

Yes; No; Not applicable

Cultural (beliefs, attitudes, and practices

of participants);

Socio-economic (distribution of social

and economic resources);

Environment (features of the physical

environment);

Political (the political landscape);

Other (specify)

Was climate change (i.e.

climate change adaptation,

mitigation, impacts)

mentioned in the outcome

of the RE (i.e. program

theory)?

Radio Yes; No; Not applicable

Did the study disaggregate

data by social identity?

If yes, which?

Radio

Checkbox

Yes; No; Not applicable

Age; Gender; Population (e.g. Indigenous

peoples); Other a These food security topics were developed through an inductive thematic analysis of studies

captured in this review. Of note, these topics are not mutually exclusive and do overlap; for

example, agricultural systems that contribute to sustainable increases in food production can

relate to climate change and agricultural productivity.

272

Appendix 16: List of references of all included studies on food-related Theory of Change and

Realist Evaluation.

Álvarez-Mingote C, Moore A and McNamara P (2020) Assessing the role of stakeholder

platforms as drivers of resilient communities: the case of Malawi. Journal of Agricultural

Education and Extension. DOI: 10.1080/1389224X.2019.1674169.

Apgar JM, Allen W, Albert J, et al. (2017) Getting beneath the surface in program planning,

monitoring and evaluation: Learning from use of participatory action research and theory

of change in the CGIAR Research Program on Aquatic Agricultural Systems. Action

Research 15(1): 15–34. DOI: 10.1177/1476750316673879.

Arriola KRJ, Ellis A, Webb-Girard A, et al. (2020) Designing integrated interventions to improve

nutrition and WASH behaviors in Kenya. Pilot and Feasibility Studies. DOI:

10.1186/s40814-020-0555-x.

Atherstone C (2014) Joint CGIAR meeting on aflatoxins. Nairobi.

Baker, D., Speedy, A., Hambrey J (2014) Report of the CGIAR Research Program on Livestock

and Fish Commissioned External Evaluation of the Program’s Value Chain Approach.

Nairobi.

Baker J, Sanghvi T, Hajeebhoy N, et al. (2013) Using an evidence-based approach to design

large-scale programs to improve infant and young child feeding. Food and nutrition

bulletin. DOI: 10.1177/15648265130343s202.

Béné C, Riba A and Wilson D (2020) Impacts of resilience interventions – Evidence from a

quasi-experimental assessment in Niger. International Journal of Disaster Risk Reduction.

DOI: 10.1016/j.ijdrr.2019.101390.

Canales, C., Manson, N., Jones B (2017) Mzima Cow Strategy & Theory of Change – Translating

from Genetic Research in Africa to Adoption and Social Value: Workshop Report. Nairobi.

Catholic Relief Services (2017) Theory of Change, Metrics and Learning Agenda.

Child, K., Kidoido, M., Kanyuuru C (2015) Using the Theories of Change approach to monitor,

evaluate and learn in the CGIAR research program on Livestock and Fish. Nairobi.

Clarkson G, Garforth C, Dorward P, et al. (2018) Can the TV makeover format of edutainment

lead to widespread changes in farmer behaviour and influence innovation systems?

Shamba Shape Up in Kenya. Land Use Policy 76. Oxford: Elsevier Ltd: 338–351. DOI:

10.1016/j.landusepol.2018.05.011.

Cole DC, Levin C, Loechl C, et al. (2016) Planning an integrated agriculture and health program

and designing its evaluation: experience from Western Kenya. Evaluation and Program

Planning 56. Oxford: Elsevier Ltd: 11–22. DOI: 10.1016/j.evalprogplan.2016.03.001.

Darisi, T., Watt H (2018) Envisioning a Circular Food Economy Theory of Change for Smart

Cities. Guelph, Canada.

Douthwaite, B., Kamp, K., Longley, C., Kruijssen F., Puskur, R., Chiuta, T., Apgar, M., Dugan P

(2013) Using theory of change to achieve impact in AAS. Penang, Malaysia.

273

Douthwaite B (2019) Outcome Evaluation of the work of the CGIAR Research Program on Land,

Water and Ecosystems (WLE) on soil and water management in Ethiopia. Ethiopia.

Douthwaite B and Hoffecker E (2017) Towards a complexity-aware theory of change for

participatory research programs working within agricultural innovation systems.

Agricultural Systems 155: 88–102. DOI: 10.1016/j.agsy.2017.04.002.

Douthwaite B, Mur R, Audouin S, et al. (2017) Agricultural research for development to

intervene effectively in complex systems and the implications for research organizations.

KIT Working Paper Series - Sustainable Economic Development. Amsterdam: Koninklijk

Instituut voor de Tropen (KIT) (Royal Tropical Institute, RTI). Available at:

http://213ou636sh0ptphd141fqei1-wpengine.netdna-ssl.com/sed/wp-

content/uploads/sites/2/2017/09/KIT-working-papers-2017-12.pdf.

Douthwaite Boru, Mayne J, McDougall C, et al. (2017) Evaluating complex interventions: A

theory-driven realist-informed approach. Evaluation 23(3): 294–311. DOI:

10.1177/1356389017714382.

Farrier A, Dooris M and Morley A (2019) Catalysing change? A critical exploration of the

impacts of a community food initiative on people, place and prosperity. LANDSCAPE

AND URBAN PLANNING 192. DOI: 10.1016/j.landurbplan.2019.103663.

Floate H, Durham J and Marks GC (2019) Moving on from logical frameworks to find the

‘missing middle’ in international development programmes. Journal of Development

Effectiveness 11(1). Abingdon: Routledge: 89–103. DOI: 10.1080/19439342.2018.1551921.

Howland F (2019) Individual capacity baseline report. Hanoi.

Johnson, N., Douthwaite, B., Mayne J (2019) Using Theory of Change in Agricultural Research

for Food and Nutrition Security. Rome.

Johnson N, Mayne J, Grace D, et al. (2015) How will training traders contribute to improved

food safety in informal markets for meat and milk? A theory of change analysis. IFPRI -

Discussion Papers. Washington: International Food Policy Research Institute. Available at:

http://www.ifpri.org/cdmref/p15738coll2/id/129293/filename/129504.pdf.

Johnson N, Atherstone C and Grace D (2015) The potential of farm-level technologies and

practices to contribute to reducing consumer exposure to aflatoxins: a theory of change

analysis. IFPRI - Discussion Papers. Washington: International Food Policy Research

Institute. Available at:

http://www.ifpri.org/cdmref/p15738coll2/id/129294/filename/129505.pdf.

Johnson N, Guedenet H and Saltzman A (2015) What will it take for biofortification to have

impact on the ground? Theories of change for three crop-country combinations. IFPRI -

Discussion Papers. Washington: International Food Policy Research Institute. Available at:

http://www.ifpri.org/sites/default/files/publications/ifpridp01427.pdf.

Kidoido, M., Korir L (2013) Report of the Tanzania Dairy Value Chain Impact Pathways

Workshop, Dar-es-Salaam, Tanzania, 7-8 May 2013. Nairobi.

Leavy, J., Boydell, E., McDowell, S., Sladkova B (2018) Resilience results BRACED final

evaluation. Washington.

274

Levay A V, Chapman GE, Seed B, et al. (2019) District-level implementation of British

Columbia’s school food and beverage sales policy: a realist evaluation exploring

intervention mechanisms in urban and rural contexts. Canadian Journal of Public Health

110(1). Cham: Springer International Publishing AG: 21–30. DOI: 10.17269/s41997-018-

0159-x.

LIFT (2016) Monitoring and Evaluation for Accountability and Learning (MEAL) Framework.

Maru Y, Sparrow A, Stirzaker R, et al. (2018) Integrated agricultural research for development

(IAR4D) from a theory of change perspective. Agricultural Systems 165. Oxford: Elsevier

Ltd: 310–320. DOI: 10.1016/j.agsy.2016.09.012.

Maye D, Enticott G and Naylor R (2019) Theories of Change in Rural Policy Evaluation.

Sociologia Ruralis. DOI: 10.1111/soru.12269.

Mayer AM, Ndolo R and Keylock J (2018) Operational factors in the integration of nutrition

into agriculture and livelihoods programmes in Zimbabwe. Field Exchange - Emergency

Nutrition Network ENN (No.57). Oxford: Emergency Nutrition Network (ENN): 31–34.

Available at: https://www.ennonline.net/fex/57/operationalfactorsnutzimbabwe.

Mayne, J., Stern, E., Douthwaite B (2013) AAS Practice Brief: Evaluating natural resource

management programs. Penang, Malaysia.

Mayne J and Johnson N (2015) Using theories of change in the CGIAR Research Program on

Agriculture for Nutrition and Health. Evaluation 21(4): 407–428. DOI:

10.1177/1356389015605198.

McDonald B (2011) Managing water and land at the interface between fresh and saline

environments An impact evaluation. Colombo, Sri Lanka.

MDF (2017) Evaluation of GAIN Programme Driving Nutrition Impact in Food Security. Ede, the

Netherlands.

Merrey, D.J., Swaans, K., Borgne EL (2013) Lessons from the Nile Basin Development Challenge

Program: An Institutional History. Colombo, Sri Lanka.

Michelini L, Grieco C, Ciulli F, et al. (2020) Uncovering the impact of food sharing platform

business models: a theory of change approach. BRITISH FOOD JOURNAL 122(5). DOI:

10.1108/BFJ-06-2019-0422.

Nair S (2016) Addressing environmental degradation and rural poverty through climate

change adaptation: an evaluation of social learning in drought-affected districts of

southern India. CCAFS Working Paper. Frederiksberg: CGIAR Research Program on

Climate Change, Agriculture and Food Security. Available at:

https://cgspace.cgiar.org/rest/bitstreams/80444/retrieve.

Nimpagaritse M, Korachais C and Meessen B (2020) Effects in spite of tough constraints - A

theory of change based investigation of contextual and implementation factors affecting

the results of a performance based financing scheme extended to malnutrition in

Burundi. PLoS ONE. DOI: 10.1371/journal.pone.0226376.

Obodai J, Adjei POW, Hamenoo SVQ, et al. (2018) Towards household food security in Ghana:

assessment of Ghana’s expanded forest plantation programme in Asante Akim South

275

District. GeoJournal 83(2). Amsterdam: Springer: 365–380. DOI: 10.1007/s10708-017-

9776-9.

Ohly H, Crossland N, Dykes F, et al. (2019) A realist qualitative study to explore how low-

income pregnant women use Healthy Start food vouchers. Maternal and Child Nutrition.

DOI: 10.1111/mcn.12632.

Omore, A., Twine, E., Githinji, J., Kanyuuru, C., Kidoido M (2016) Maziwa Zaidi Theory of

Change: Context and ‘start point’. Nairobi.

Omore A, Kidoido M, Twine E, et al. (2019) Using “theory of change” to improve agricultural

research: recent experience from Tanzania. Development in Practice 29(7): 898–911. DOI:

10.1080/09614524.2019.1641182.

Pound, B., Tolera, A., Matsaert H (2015) Report of the internally-commissioned external review

of the Africa RISING project in the Ethiopian Highlands. Nairobi.

Pradel, W., Cole, D.C., Prain G (2013) Mixing methods for rich and meaningful insight:

Evaluating changes in an agricultural intervention in the Central Andes.

Roundtable on Sustainable Biomaterials (2014) RSB’s Theory of Change.

Schuetz T, Förch W, Thornton P, et al. (2017) Pathway to Impact: Supporting and Evaluating

Enabling Environments for Research for Development. In: Evaluating Climate Change

Action for Sustainable Development. DOI: 10.1007/978-3-319-43702-6_4.

Sustain Ontario (2012) Theory of Change Charting a Path to Healthy Food and Farming

Systems. Ottawa, Canada.

Thornton PK, Schuetz T, Förch W, et al. (2017) Responding to global change: A theory of

change approach to making agricultural research for development outcome-based.

Agricultural Systems 152: 145–153. DOI: 10.1016/j.agsy.2017.01.005.

Ton G, Vellema S and Ge L (2014) The Triviality of Measuring Ultimate Outcomes:

Acknowledging the Span of Direct Influence. IDS BULLETIN-INSTITUTE OF DEVELOPMENT

STUDIES 45(6, SI): 37–48. DOI: 10.1111/1759-5436.12111.

Vellema S, Maru YT, Ekong J, et al. (2017) Do theories of change enable innovation platforms

and partnerships to navigate towards impact? KIT Working Paper Series - Sustainable

Economic Development. Amsterdam: Koninklijk Instituut voor de Tropen (KIT) (Royal

Tropical Institute, RTI). Available at: https://213ou636sh0ptphd141fqei1-

wpengine.netdna-ssl.com/sed/wp-

content/uploads/sites/2/2015/06/KIT45_opmaak_WPS_13-2017_v2.pdf.

Vogel I (2012) Review of the use of ‘Theory of Change’ in international development. UK.

Wesley AS, De Plaen R, Michaux KD, et al. (2019) Integrating nutrition outcomes into

agriculture development for impact at scale: Highlights from the Canadian International

Food Security Research Fund. Maternal and Child Nutrition. DOI: 10.1111/mcn.12812.

WFP (2018) An Impact Evaluation of WFP Malnutrition Interventions in Niger. Rome, Italy.

276

Appendix 17: Coding process to analyze Theory of Change (ToC) and Realist Evaluation (RE)

studies.

277

Appendix 18. Number of publications focusing on food-related Theory of Change and Realist

Evaluation studies (note: review cut off 10 March 2020).

0

2

4

6

8

10

12

14

16

18

20

2011 2012 2013 2014 2015 2016 2017 2018 2019

Nu

mb

er o

f p

ub

lica

tio

ns

Year

Published literature Grey literature

278

Appendix 19: Codebook to identify problems as defined by Theory of Change and Realist

Evaluation studies (2nd level).

Question /

code

Description Example

Complexity The food security issue, program, and/or system (in which a program is

situated in) is complex.

Food security

issue is

complex

Describes how food security

multidimensional problem with

multiple causes.

“Malnutrition is a multidimensional

problem that requires multisectoral

interventions” (Wesley et al. 2019).

Food security

program is

complex

Describes how pathways toward

food security are complex,

involving uncertainty, non-

linearity, emergence, multiple

interacting components,

multiple actors, multiple

feedback loops, and/or lengthy

time frames.

“… agricultural development is a complex

process with a “high degree of non-

linearity”, one that is “fundamentally a

social process in which people construct

solutions to their problems” by

opportunistically selecting only those

fragments of an innovation that meet

their particular needs” (CGIAR 2014).

Complex

systems

Describes how programs

intervene in complex systems,

contexts, and/or environments.

“Aquatic agricultural systems are

complex and evolving social-ecological

systems characterized by ongoing

change and unpredictability” (Apgar et

al. 2017).

Program

evaluation

Problems center around evaluation activities including the use of ToCs,

other theory-driven evaluation approaches, and/or experimental designs.

Problems also center around difficulties in evaluating certain food security

topics.

Limitations of

ToCs

ToCs miss detail and context;

ToCs do not account for

unexpected outcomes; ToCs do

not account for complexity.

“Program theory requires analyzing a

complex chain of causality, often not

adequately spelled out much less subject

to rigorous evaluation” (Cole et al. 2016).

Theory-driven

evaluations

Logic models oversimplify the

program, ignore complexity,

miss alternative pathways,

and/or present overly linear

pathways.

“… using only a logic model to articulate

a theory of change may result in

oversimplification of an intervention”

(Levay et al. 2018).

Experimental

designs

Many activities contribute to

food security outcomes making

it difficult to attribute change to

a specific program. Alternative

“Net effects, especially those related to

business performance and income, are

influenced by a wide range of

intervening factors… This makes it

279

approaches are needed. difficult to attribute effects to the actual

interventions and provides little

information on the effectiveness of

developmental activities” (Ton 2014).

Evaluating

food security

concepts

Describes evaluation challenges

specific to the food security

topic (e.g. nutrition, resilience,

capacity-building).

“Very little has been written so far on

impact evaluation of resilience

interventions” (Bene et al. 2020).

Program

planning

Problems center around the need of describing and/or explaining how the

program works.

Descriptive Need to describe and/or guide

the process of program planning

and/or learning.

“All research for development programs

wish to achieve impact, but

understanding how to plan for and

document this has been challenging.”

(Johnson et al. 2019).

Explanatory:

process

Describes the need to

understand and/or explain

program process and/or

mechanisms.

“… more evidence is needed to illustrate

the specific pathways by which elements

of process lead to the outcomes

specified—the how of social learning”

(Epp et al. 2019).

Explanatory:

outcomes

Describes the need to

understand and/or explain

program outcomes and/or

impact.

“Healthy Start is the UK government's

food voucher programme… It was

introduced in 2006, but the impact of the

programme on nutritional outcomes

remains understudied” (Ohly 2019).

280

Appendix 20: Codebook to identify how Theory of Change and Realist Evaluation studies are

responding to problems (3rd level).

Question /

code

Description Example

Purpose Describes the aim of the response to the problem.

Guiding the

program

Describes activities that guide

and/or understand change.

“To develop a ToC for improved nutrition

to understand the complex and varied

means through which nutritional

challenges can be addressed” (Wesley et

al. 2019).

Clarifying the

program

Describes activities that clarify a

program’s logic.

“The purpose of this paper is to

contribute a more nuanced

understanding of the theory of change

underlying this increasingly popular

public health intervention” (Levay et al.

2018).

Informing

evaluation

Describes activities that will

inform monitoring and

evaluation efforts.

“The theory of change devised in this

paper was articulated to form the basis

of a realist implementation evaluation of

the BC school food and beverage sales

Guidelines” (Levay et al. 2018).

Process Describes how responses were operationalized.

Researcher-led Describes how activities were led

by researchers.

“The proposed retrospective theory of

change was presented to various

stakeholders from the health sector to

ensure plausibility and their feedback

was incorporated where appropriate”

(Levay et al. 2018).

Participatory Describes how activities were

developed in a participatory

manner.

“Can start with a blank page or with a

straw impact pathway/theory of change

In a participatory manner, one can start

with a blank page and a facilitator who

proceeds to tease out the way

participants (stakeholders) imagine that

the intervention is to work and the

implicit assumptions behind their

thinking” (Mayne and Johnson 2015).

Prospective Describes how activities were

developed before/during the

“The project's theory of change was

developed with relevant stakeholders at

281

program implementation. the same time as the scenarios process

was undertaken, to help ensure high

relevance and the inclusion of the

partners likely to be necessary for

success” (Thornton et al. 2017).

Retrospective Describes how activities were

developed after the program

ended.

“IET developed without the use of an

articulated ToC. However, it was agreed

with the research project oversight group

that it would be valuable to undertake

the participatory development of a ToC

with local community members with

experience of and interest in IET” (Farrier

et al. 2019).

Outcome Describes the outcomes of

responses.

Single ToC Describes a single ToC. “Example of the theory-of-change for an

outpatient therapeutic feeding

programme” (Floate et al 2018).

Multiple ToCs Describes multiple ToCs (e.g.

one broad ToC and several

specific ToCs).

“In developing an approach to creating a

complexity-aware ToC, we also draw on

the idea that useful ToC should be

nested (Mayne, 2015) such that a

program or research system will have an

overarching ToC, describing its high-level

causal assumptions, under which more

detailed and grounded ToC is developed

for individual projects, or elements of

them” (Douthwaite and Hoffecker 2017).

If/then logic Logic reads: if the intervention

occurs successfully, then it will

lead to the desired result.

“After considering the diverse insights

from stakeholders, in conjunction with

the depiction of the programmatic

components in the logic model, broad

logical statements were developed to

theorize how the program was expected

to work (i.e. if-then statements)” (Levay

et al. 2018).

Backwards

mapping logic

Logic reads: for the change to

occur, these preconditions need

to be met.

“Using a backwards mapping approach

[27, 56, 57], positive actions, cognitive

processes, and behaviors needed to

achieve each of the priority behaviors

282

were mapped” (Arriola 2020).

Linear Describes uni-direction between

program activities and

outcomes.

“Our programme theory using the TOC

approach differs from the logical

framework by identifying additional

short- and medium-term outcomes

needed to create positive change”

(Floate et al. 2018).

Complex Describes emergence and/or

feedback loops between

program activities and

outcomes.

“These four parts should not be seen

only as a linear sequence of events.

There are important feedback and

cyclical elements within the ToC”

(Clarkson et al. 2018).

Factors

influencing

responses

Describes factors influencing responses.

Funder Describes the influence of

donors.

“The standard donor proposal format

includes both a logical framework and

development of a TOC. We decide to

incorporate a realist approach into one

of the domains identified through our

TOC, to provide a more grounded theory

on our capacity building activities”

(Floate et al. 2018).

Resources Describes the influence of

resources.

“Development of ToC prior to launch of

an intervention does not happen in

practice due to resource constraints,

necessitating development of a

retrospective ToC” (Levay et al. 2018).

283

Appendix 21: Interview guide and Consolidated Framework for Implementation Research a

constructs used to explore the implementation and evaluation of the SafePORK program.

Interview question (Construct) Researchers Partners

Intervention characteristics

What components were you involved in and what were your

experiences? (Design quality and packaging)

x x

Did these components change over time and how have teams

stayed resilient to program changes? (Adaptability)

x

Would you consider the program to be complex or non-

complex? (Complexity)

x

What opportunities exist to scale the program after the program

ends? (Perceived scalability)

x

Process of implementation

What has been challenging and helpful in implementing each

component? (Reflecting and evaluating)

x

Did the implementation go according to plan? (Executing) x

How do you assess progress toward implementation goals?

(Planning)

x

Outer setting

What factors contributed to changes to program components?

(External policy and incentives)

x x

Have extreme weather events influenced the program? (Climate

change)

x x

Inner setting

Can you describe how teams worked together? (Compatibility) x

Individual characteristics

Do you think the intended results will be fully achieved?

(Knowledge and beliefs about the intervention)

x

Outcomes

Over the past few years, how did your

knowledge/attitudes/practice change? (Outcome)

x x

What influenced these changes? (Context) x x

How did the program contribute to this change? (Mechanism) x x a The Consolidated Framework for Implementation Research (CFIR) consists of 39 constructs divided across five

overarching domains found to influence the successful implementation of innovative programs. The domains assess

intervention characteristics, outer setting, inner setting, characteristics of individuals, and implementation process.

CFIR was selected because the multilevel factors identified by CFIR provide a promising starting point for exploring

how SafePORK is implemented and evaluated.

284

Appendix 22: Audit trail of decisions made and rationales behind them.

Decisions Rationale

We selected relevant constructs of CFIR and

adapted questions to our program evaluation

context.

Suggested by the CFIR guide (cfirguide.org).

Where appropriate, interviewees were probed

to describe factors that facilitated or impeded

the implementation of the program.

Suggested by the CFIR guide (cfirguide.org).

We added questions as appropriate for our

program. For example, under the outer

setting, we added a construct for climate

change.

Climate change increasingly impacts food

safety. For example, changes in temperature,

rainfall patterns, and increased frequency of

extreme weather events can influence food

safety by changing the population dynamics

of contaminating organisms (Mbow et al.,

2019).a

We added a sixth domain (Outcomes). to ask questions around intermediate

program outcomes, helping to validate the

program’s Theory of Change (objective three

of SafePORK). Constructs for this domain

were informed by realist evaluation, which

focuses on the relationship between program

outcomes, mechanisms, and context (Pawson,

2013).b Tracing implementation processes is

an important part of realist evaluation

because interviewees’ reasonings around

program implementation can help identify

key contextual differences in the

development of outcome patterns (Manzano,

2016).c

We added the construct “perceived

scalability”, an additional CFIR construct

proposed previously (Means et al., 2020).d

Program coordinators were also interested in

perspectives on scaling up the program.

The final interview guide for researchers was

conducted with SafePORK coordinators. After

piloting, the tool was found to be too

lengthy, and was subsequently shortened

from 18 questions to 14 questions.

Pre-test the tools but also provide rich

contextual information.

285

Midway through the interviews with program

participants, research assistants added the

question “On a scale of 1 to 10, how would

you rate the program”?

To facilitate probing on challenges. For

example, if interviewees responded 9/10, we

would ask: how could it be 10/10?

a Mbow, C., Rosenzweig, C., Barioni, L. G., Benton, T. G., Herrero, M., Krishnapillai, M., Liwenga, E., Pradhan, P., Rivera-

Ferre, M. G., Sapkota, T., Tubiello, F. N., & Xu, Y. (2019). Food Security. In P. Z. P.R. Shukla, J. Skea, E. Calvo Buendia, V.

Masson-Delmotte, H.-O. Pörtner, D.C. Roberts, J. P. P. R. Slade, S. Connors, R. van Diemen, M. Ferrat, E. Haughey, S.

Luz, S. Neogi, M. Pathak, J. Petzold, & J. M. P. Vyas, E. Huntley, K. Kissick, M. Belkacemi (Eds.), Climate Change and

Land: an IPCC special report on climate change, desertification, land degradation, sustainable land management, food

security, and greenhouse gas fluxes in terrestrial ecosystems. b Pawson, R. (2013). The Science of Evaluation: A Realist Manifesto. SAGE. c Manzano, A. (2016). The craft of interviewing in realist evaluation. Evaluation. 22(3): 342-360. d Means, A. R., Kemp, C. G., Gwayi-Chore, M. C., Gimbel, S., Soi, C., Sherr, K., Wagenaar, B. H., Wasserheit, J. N., &

Weiner, B. J. (2020). Evaluating and optimizing the consolidated framework for implementation research (CFIR) for use

in low- And middle-income countries: A systematic review. In Implementation Science. 15:17.

CFIR: Consolidated Framework for Implementation Research.

286

Appendix 23: Impacts of COVID-19 on data collection.

Initially, community visits for the qualitative study in Chapter 5 were planned toward the end of

March 2020 to coincide with the midterm review of the SafePORK program. However, COVID-19

cases in Vietnam surged, and the country suspended the entry of all foreigners on 22 March

2020 to limit the spread of the virus. While waiting to see how the COVID-19 pandemic would

evolve, I focused on the desk-based aspects of my research (e.g. Chapter 4).

By summer 2021, travel to Vietnam was still suspended. With the rapidly approaching

dissertation timelines, I considered whether research could be done at a distance. I wondered if

asking people to participate in research at this time – a year and a half into the pandemic – will

put them under any additional unnecessary stress. I consulted with my PhD committee, research

ethics board, and local partners, who provided support to conduct this study remotely. As such,

all interviews were conducted via Microsoft Teams or phone.

One initial concern I had was the limited control over the interviews with program participants,

which were conducted by the two SafePORK team members (Sinh and Trang). Because of time

zone differences between Canada and Vietnam, the limited existing rapport between myself and

program participants, and the anticipated challenges of myself being able to capture

Vietnamese speech fully over the phone, it made more sense for the SafePORK team to conduct

these interviews. To engage in this data collection process, I held sessions before, during, and

after interviews to plan for and reflect on the interviews. I also spent time listening to the audio

recordings and double-checking the Vietnamese transcripts.

287

In the end, this concern was perhaps not significant as both Sinh and Trang have extensive

experience conducting surveys and interviews. When I asked Sinh and Trang about their

thoughts on how remote data collection went, they said “it depends”. Some participants were

open to chatting as the time was convenient for them. Others had children, customers, or

livestock in the background, which at times created interruptions in the interview process.

Importantly, Sinh and Trang said phone interviews were fine because they knew the

interviewees. If new researchers were to join in the conversation, Sinh and Trang would have had

to explain in-depth who the new researcher is to avoid skepticism.

288

Appendix 24: Presentation material for the SafePORK team.

29 November 2021

2

Retailers and slaughterhouse workers reported they adopted hygienic practices because of

SafePORK interactions, training, and equipment, as well as changing consumer perspectives (e.g. increased demand for safer food)

While retailers and slaughterhouse workers could not sell pork at a higher price, many reported improved business from higher number of customers, which is a key motivator

Retailers and slaughterhouse workers reported consumers feel more secure buying pork from them, given improved cleanliness of facilities and pork quality

Microbial sampling will be important for confirming improved pork quality

Local authorities are supportive of SafePORK interactions, trainings, and equipment, even

requesting activities to scale up ( e.g. focus on centralized slaughtering facilities)

Discussions are underway in certifying model slaughterhouses and branding Ban pork

SafePORK is well respected by food safety

actors, with slaughterhouse workers and retailers requested increased visits from the

SafePORK team to raise awareness of consumers that their facilities are clean

Local authorities also appreciated SafePORKinterventions and would like to see them

scaled up ( e.g. to centralized slaughtering facilities)

Delegating tasks for joint activities

Offering strategies for effective

multidisciplinary collaboration, especially as the program is nearing completion and

teams will be publishing findings together

Ongoing development of program theory is a promising strategy for thinking about hard

to anticipate food safety outcomes. Measuring outcomes along a program s change pathway on a real time basis provides indicator s of gradual

progress toward the long term food safety goal as well as identifies (and addresses) emerging issues as they arise.

The team noted adoption of practices was quicker in urban areas than rural areas, likely

because consumers there are more aware of food safety concerns, suggesting improving consumer awareness is important for moti vating actors

to adopt hygienic practices. Attuning to context helps identity elements to consider when interventions are scaled up or adapted to other settings.

Women and men, for example, face different challenges related

to their work, requiring tailored interventions to their circumstances. They are also not homogenous groups; for example, the approach to working

with slaughtermen may be different in privately run vs family run slaughterhouses. Paying attention to mechanisms and context behind

behavioural outcomes is important for identifying what interventions work for different food safety actors .

While not an explicit objective of SafePORK, asking questions about climate change can reveal important insights into

how food safety is impacted by climate change and identify areas where SafePORK may potentially intervene.

289

3

Because food security is a multi dimensional issue, multi sector

programs are often required to achieve food security goals. Such

programs mobilize health, agriculture, and other related sectors to

implement a package of components ( e.g. research, intervention,

policy), which targeting different levels of change.

The multiple programming components can interact with each

another along with wider food systems. While necessary, the

complexity arising from these interactions creates challenges when

evaluating, learning from, and replicating multi sector programs.

Guidelines exist to support the development of complex health

interventions, but there are comparatively few guidelines relevant

for food security. To address this gap, this study explores insights

into food security programming. We draw on the experiences of the

SafePORK food safety program in Vietnam as a case study.

Semi structured interviews with SafePORK

researchers (n=7)

Semi structured interviews with slaughterhouse

workers (n=10), retailers (n=9), local authorities (n=3), and market managers (n=1) from Hung

Yen (n=13), Nghe An (n=7), and Hoa Binhprovinces (n=3) ( ).

The following points should be kept in mind when interpreting

findings:

The primary purpose of the study

was to generate lessons for program evaluation, rather than

evaluate the program itself. While the study also generated

evaluation findings, it does not replace SafePORK research

and evaluation activities ( e.g. KAP pre and post test survey,

microbial sampling, Outcome Mapping).

Given familiarity of the interviewer with participants, it was

difficult to probe for thoughts from slaughterhouse workers

and retailers on how the program might be done better.

However, local authorities and the market manager were

very open in sharing ideas for program improvement.

Examining SafePORK from an implementation science and realist

evaluation perspective ( ), we explored questions of:

1. What outcomes have SafePORK achieved so far, and what

mechanisms triggered such outcomes?

2. What are the challenges and opportunities for implementation?

Steven conducted semi structured interviews with researchers,

while Sinh and Trang conducted interviews with program

participants. Thematic analysis was used to analyze findings.

Regular de briefing sessions were held to co develop themes.

We drew on the following data sources:

4

Understanding the implementation of food safety programs in Vietnam requires an understanding of Vietnamese food systems . Foo d safety is

one the most pressing issues among Vietnamese, often given more emphasis than education. A particular area of concern is pork the main

animal source food in Vietnamese diets which is often produced by smallholder farming systems and sold fresh in traditional we t markets. While

highly nutritious, fresh pork sold in these markets are highly susceptible to microbiological contamination, presenting healt h r isks.

Market based approaches to improving

the safety of pork in Vietnam

( SafePORK ) is a five year program

(2017 2022) aiming to reduce the burden

of foodborne disease in informal,

emerging, and niche markets through

designing, piloting, and evaluating food

safety interventions. SafePORK is

implemented in Hung Yen, Hoa Binh, and

Nghe An. In Hung Yen and Nghe An,

SafePORK is primarily focused on pork

handling practices within traditional

slaughterhouses and wet markets, two

critical points in the chain in which food

safety issues can have large

consequences. In Hoa Binh province,

SafePORK is strengthening the Ban pig

value chain by linking rural women and

men smallholder farmers to emerging

and niche markets. shows the

five core objectives of SafePORK and their

interrelations.

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5

Below is an overview of key activities and timelines of SafePORK alongside relevant external factors ( ). The context of ASF and COVID 19

is important for understanding how and why implementation shifted over time. At the time of the study (Aug Sept 2021), Vietnam was under

lockdown due to COVID 19. Despite delays created by COVID 19 (and ASF), nearly all researchers perceive SafePORK to be implement ed as

planned. Researchers reported reaching eight slaughterhouses (out of a target of 10) and 14 retailers (out of 24) in Hung Yen and Nghe An.

Regarding Ban value chain development in Hoa Binh, the team is working with local authorities and markets to build and promote branding and

market linkages. Risk communication is well under way, with hundreds of actors trained in food safety risk management. Researche rs believe they

will achieve their original objectives by the end of 2022.

Safe

PORK inte

rventions

Exte

rnal fa

cto

rs

6

291

7

When asked about the changes resulting from SafePORK, researchers

reported:

Researchers described how multidisciplinary collaborations

led to knowledge exchange. For example, economic researchers

learned about risk assessments whereas public health teams learned

from others about how to effectively engage with communities.

Researchers described how collaborations

created outputs or led to ideas that were stronger than if team

members worked within their own disciplines. Some reported if the

other team was not involved, they would not have been able to

implement activities and/or interventions.

SafePORK is fostering the development of new

relationships and partnerships. Researchers reported engaging with

different disciplines, often for the first time. Outside of regular team

meetings, SafePORK researchers found it valuable to connect on Zalo

and Facebook to provide real time updates on SafePORK and life.

Researchers described how

SafePORK activities led to changes outside the immediate program

team. For example, senior researchers described using SafePORK as a

case study in lectures, helping to equip the future workforce with

knowledge. Others described progress made in certifying model

small scale slaughterhouses or markets, thus supporting informal pork

production. In Hoa Binh, discussions are being facilitated to promote

branding and market linkages for Ban pork, as well as support

hygienic practices at slaughterhouses and markets.

Because when we discuss on an issue with other sector, they

bring with me more chance to rethink what I thought before,

bring for me more ideas. I also have more potential partners.

Our team members most of them are lecturers in their

discipline. SafePORK give them some idea and also some

chance to upgrade to know to improve the lecture.

And for doing training for the slaughterhouse, without the

HUPH team, we couldn't do this because they have the

experience and knowledge on this.

Now I learned a lot from the VNUA team and NIAS team about

how to work with local people. And I think if we can run

SafePORK again or scale up I think we can do other things to

approach people.

8

When asked about the ways in which their food safety

thinking / practice has changed, participants reported:

Shared outcomes among women and

men included the adoption of hygienic practices, resulting

in improved cleanliness of the working area.

Women described how meat is now

cleaner, more beautiful, and has less odor than before,

enabling them to sell more pork. One retailer in Hung Yen

shared she used to sell around sold 20 kg of pork per day,

but now she can sell 25 30 kg. Men also noticed their

business was better, as one slaughterhouse worker in Nghe

An explained, because customers see [slaughtering

practices] directly, it s clean, they like it, and they introduce

us other customers who buy more pork .

Both women and men

reported that consumers trust them more because of

improved cleanliness of facilities and quality of pork.

According to them, consumers feel more secure when they

buy and eat their pork.

SafePORK interactions have led to

structural changes. For example, discussions with market

managers have led to improved access to water at markets,

supporting retailers in keeping counters clean.

Both women and men said they know more

now and recalled key messages from the training sessions.

Importantly, change in knowledge was often not enough to lead to

change in practice. For many, mechanisms were related to achieved

outcomes ( e.g. changed practice because pork looked better).

, as one

explained: if I don t, I will lose customers. And while they often

cannot sell pork at a higher price, many noticed increased number of

customers, a motivator for continuing to apply hygienic practices.

For

men, convenience of proposed recommendations was highly valued.

They appreciated how equipment ( e.g. inox grid, boots) helped keep

the floor cleaned and relieved them of not worrying about

borrowing. For women, having access to water at the market was

important, which was not available before SafePORK: now that there's

water I'll wash my hands, wash the cutting board and clean seats, then

sell [pork] without the smell anymore.

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9

Better understanding of hygienic practices and how to communicate with food safety actors

Interactions with the team, studying project documents, and attending trainings contributed to these outcomes

Low level of knowledge of consumers about safe pork (especially in the highlands)

Low consumer willingness to pay higher prices for safer pork

Low level of knowledge of retailers/slaughterhouse workers about safe food handling practices

Limited funding for staff members to travel and carry out inspections

Climate change increases risk of pigs getting disease; farmers will use chemicals ( e.g. veterinary drugs, animal feed) to prevent pigs from getting sick,

which increases costs and affects food safety

More communication especially for consumers who have a large influence on other actors

Consumers should be encouraged to limit purchases from counters with limited hygiene

Training for producers to raise livestock that avoids risks from disease and price fluctuations

Expand the project in other communes to achieve larger impacts, as well as continuing trainings for consumers, retailers, and slaughterhouse workers

More visits from the SafePORK team to encourage maintenance of practices

Expand training to centralized slaughtering facilities to align with overall policy direction

Start training for veterinary staff around food safety management / disease detection

Traceability; cannot control quality of pork coming to the market from different sources

Hard to tell retailers what to do because it will bring him displeasure

Still notices hygienic issues ( e.g. cloths aren t washed, cutting boards aren t clean, bad smell); convenience of old habits is a barrier

Practices depend on the individual retailer (some are clean while others are messy)

Consumers don t notice change in practices because they are busy and buy meat fast

Lack of inspection being done, only he does it (not veterinary departments or authorities)

Climate change and hot weather increases appearance of flies

Would like to see more visits from the SafePORK team to inspect; visits should be sudden and unannounced

Consider adding a camera and inspecting food safety at the market from a distance

10

Finding time to get together is difficult. Often it seems the same

conversations are being held without any progress being made.

If key team members cannot make it to meetings, encourage

representative members to debrief with their team

Encourage young researchers to join these meetings as they

bring an important perspective and have more time

Share field visits in advance, while recognizing not all activities

can be prepared early

Joint activities without a clear lead/support leads to confusion on

who will do these activities. Also, after brainstorming next steps

during meetings, often next steps are not followed.

For joint activities, delegate tasks clearly, even if they are joint

Follow through on action items by tracking progress on their

achievement

Actors adopt hygienic practices when researchers come, but

quickly revert to old practices when researchers leave.

Continue regular visits to study sites as consumers think visits

from SafePORK team means the slaughterhouse/market is clean

As consumers increasingly recognize the value of safe food

handling, retailers and slaughterhouse workers have to adopt

practices

Adopting hygienic practices is challenging because they do not

yet provide incentives such as higher profit, certification, or

branding.

Explain how such practices improves the quality of pork and

facility cleanliness, which can attract customers

Explain that other participants adopting these practices have

seen increase in of customers

Participants say they have no time, but what they really mean

may be that they the need to keep pork dry (hence cannot clean

cutting boards often), there is too many customers (hence

cannot use disinfection), or need to process pigs quickly (thus

cannot clean knives).

Seek to understand what participants mean when they say they

have no time

Continue designing interventions that are convenient; continue

using nudges; continue seeking feedback regularly

Continue fostering an enabling environment (e.g. ensuring

access to clean water)

Local authorities prioritize investment projects rather than light

touch interventions.

Continue communicating to local authorities about the value of

building capacity and an enabling environment

Actors don t want to change because they don t know where

pork is coming from and where it is going. They also consider

food safety to be the responsibility of others ( e.g.

slaughterhouse workers think of retailers, and vice versa).

Select value chains with clear linkages

If not possible, continue communicating challenges with

achieving traceability and advocating for traceability

293

11

If SafePORK could be done differently:

During this activity,

key champions were identified who were supportive of SafePORK.

Risk communication can also help improve consumer awareness,

helping to improve uptake of interventions in markets and

slaughterhouses.

Preliminary findings

can be used as a risk communication tool to explain risks and

opportunities for mitigation. Findings should be presented to all

study communities. Presenting raw data is an opportunity to

collect more insights and strengthen survey findings..

Actors are likely more motivated to participate if they have a

financial stake.

Suggestions moving forward:

Consider a workshop at the beginning of collaboration with

researchers. Each researcher could share how they would address

the food safety problem using tools/approaches from their

discipline. Don t assume people have prior knowledge about

others disciplines. Provide guidance on how to work together.

Researchers suggested activities for the next phase

including adding food classes (for consumers) and developing

traceability of pork. While SafePORK pivoted activities well during

ASF and COVID 19, consider developing tools that protect food

safety and mitigate the impact of external events. For example,

researchers suggested developing an early warning system.

Engage with local authorities

earlier (e.g. local authorities, animal health Women s Union).

Budget for engagement. Continue regular visits to study sites,

which help actors maintain practice and improve consumer

awareness. Continue finding champions who will work with their

peers toward positive social change (e.g. Mr. An slaughterhouse).

12

294

13

When asked whether climate was a factor influencing

implementation, many researchers talked about the link

between heatwaves and increased microbial replication.

For slaughterhouse workers and retailers, transporting pork

can be challenging during heavy rainfalls.

Retailers talking about how heat and rain impacted pork

quality by making your meat worse, it is not fresh and

beautiful anymore

Because heat makes pork wet, retailers often use cardboard

to help absorb moisture

One local authority reported that farmers pigs would get

sick during climate variation and would often use

unnecessary substances to support pigs.

For women we interviewed, time is a scarce resource.

Retailers described cleaning only when there are no

customers: I cut it for this person first, and when no one has

come to buy, I bend down to wash quickly before someone

buys and I cut it again. Maintaining cleanliness is important

for retailers in keeping customers, not just their individual

retailer counters, but the entire market.

Women more often than men reported challenges with

climatic events ( e.g. heat reduces pork quality).

Men worried more about sourcing pigs not affected by ASF

and collecting pigs when is not too hot/cold out.

Continuously monitoring and adapting interventions in

response to implementation feedback and new emerging

conditions is critical for achieving behavioural change.

Ongoing development of program theory is a promising

strategy for thinking about potential outcomes

Measuring outcomes along a program s change pathway

provides indicators of gradual progress toward the long

term food safety goal, as well as identifies emerging issues

and opportunities for intervention adaptation

Because program components vary in complexity, different

tools are required to to assess and learn from components.

SafePORK interventions were strongly influenced by context.

The team noted adoption of practices was quicker in urban

areas than rural areas, likely because consumers there are

more aware of food safety concerns, suggesting improving

consumer awareness is important for motivating actors to

adopt hygienic practices.

Scale of pork production operations also influence

interventions; for example, more pigs are processed in Hung

Yen compared to Nghe An, often calling for slaughterhouse

interventions to be more sophisticated ( e.g. installing 2 grids

vs one grid in Hung Yen).

Attuning to context provides ideas for intervention design.

14

Were any of these findings surprising?

Do the four developed themes make sense? Should they be changed?

How can these findings be helpful for other food security researchers

and practitioners? In other words, what are the implications for food

safety program planning and evaluation?

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15

Interview guide used to explore the implementation and evaluation of the SafePORK program.

Questions were informed by:1) , an implementation science framework used to explore factors considered important for intervention success.

2) , an approach to evaluation used to explore how, why, and under what context program outcomes were achieved.

16

What components were you involved in and what were your

experiences? (Design quality and packaging)

x x

Did these components change over time and how have teams stayed

resilient to program changes? (Adaptability)

x

Would you consider the program to be complex or non complex?

(Complexity)

x

What opportunities exist to scale the program after the program

ends? (Perceived scalability)

x

What has been challenging and helpful in implementing each

component? (Reflecting and evaluating)

x

Did the implementation go according to plan? (Executing) x

How do you assess progress toward implementation goals?

(Planning)

x

What factors contributed to changes to program components?

(External policy and incentives)

x x

Have extreme weather events influenced the program? (Climate

change)

x x

Can you describe how teams worked together? (Compatibility) x

Do you think the intended results will be fully achieved? (Knowledge

and beliefs about the intervention)

x

Over the past few years, how did your knowledge/attitudes/practice

change? (Outcome)

x x

What influenced these changes? (Context) x x

How did the program contribute to this change? (Mechanism) x x

296

17

297

Appendix 25: Characteristics of program participant interviewees.

Province Role Gender Ethnic group

Hoa Binh Local authority Man Minority

Hoa Binh Slaughterhouse worker Man Minority

Hoa Binh Slaughterhouse worker Man Majority

Hung Yen Slaughterhouse worker Man Majority

Hung Yen Slaughterhouse worker Man Majority

Hung Yen Slaughterhouse worker Man Majority

Hung Yen Slaughterhouse worker Man Majority

Hung Yen Retailer Woman Majority

Hung Yen Retailer Woman Majority

Hung Yen Retailer Woman Majority

Hung Yen Retailer Woman Majority

Hung Yen Retailer Woman Majority

Hung Yen Retailer Woman Majority

Hung Yen Market manager Man Majority

Hung Yen Retailer Man Majority

Hung Yen Local authority Man Majority

Nghe An Slaughterhouse worker Man Majority

Nghe An Slaughterhouse worker Man Majority

Nghe An Slaughterhouse worker Man Majority

Nghe An Slaughterhouse worker Man Majority

Nghe An Local authority Woman Majority

Nghe An Retailer Man Majority

Nghe An Retailer Woman Majority

298

Appendix 26: Codebook to identify overarching themes from SafePORK implementation.

Code Description Supporting quotation

Developing and using program theory: describes the use of program theory in tracking

changes to program context, strategies, and outcomes.

ASF impacts Describes impacts on ASF

on SafePORK activities

(e.g. inability to access the

field, slaughterhouse

workers more concerned

about sourcing healthy

pigs)

the district and also province did allow people

going in and out much in the slaughterhouse,

disrupting activities. There is a need to restrict

/ manage the number of people

Changing pig

production and

consumption

patterns

Describes changes to pig

deaths, consumer

demand, pork production,

and pork price

In Hung Yen during the swine fever time

because the price of pigs and price of pork

increase very significant. So, farmers try to raise

heavier pigs.

Responding to

ASF

Describes SafePORK

strategies to respond to

external factors (e.g.

practicing caution in

entering field sites,

shifting focus to other

actors along the pork

value chain)

you know, the ASF occur very strongly in

Vietnam, and it really affects our activity a lot,

because at that time we visit the SL, and from

SL to other SL, we can be the vector to bring

the virus to the pigs, so which mean we must

be very careful in our work

COVID-19

impacts

Describes changes

brought on by COVID-19,

such as inability to go to

the field, switching from

remote communications,

busyness of local

authorities in COVID-19

control

As long as COVID-19 is here, and we do not

control that, it is very difficult to reinforce what

we have done earlier in both Hung Yen and

Nghe An. Because you know the

slaughterhouse and retailer when you are in

contact with them it must be continuous

Push to

modernize

pork

production

Describes the

government’s push toward

large and centralized pork

production in order to

more carefully control

food safety issues

want to maintain and increase the influence in

centralized slaughtering facilities and raise

awareness for retailers and consumers.

Currently, interventions are only in small

slaughterhouses, while the district's and

province's orientation are toward concentrated

slaughtering points

299

Responding to

COVID-19

Describes responses to

COVID-19, particularly

leveraging existing

relationships and

maintaining contact with

food safety actors

remotely

However, because of COVID so we can

sometimes we couldn't go there, and we make

the phone call only… we would like them to

take some pics or videos of implementation

but some couldn’t because they don't have a

smartphone

Facility size Larger facilities tended to

have more difficulty with

adhering to

recommended practices

compared to smaller

facilities

you can imagine from 2 am to five am. They

have few hours to slaughter seven or eight

pigs. So they have to do it quick. Not like in

Nghe An they sometimes only have 1 pig.

Ownership

structure

Different approaches are

required to engage with

community members; for

example, for family-run

slaughterhouses, need to

work with the entire

family, whereas for owner-

run slaughterhouses,

primarily need to engage

with the owner who will

then delegate tasks to

workers

we have implemented the intervention in two

types of slaughterhouses. The first one is a very

private slaughterhouse which means that the

owner, they are not the worker, which means

that the owner, they just hire the workers. But

for other smaller scale SL, the owners are also

the workers, and they just use the labor from

their family. The way they operate is very

different. We also need to change the way we

approach them.

Government

priorities

Governments (district,

provincial, federal) now

prioritizing modern pork

production facilities

Slaughterhouses at the large scale can control

the food safety and hygiene. In smallholders

the government cannot control because they

don't have enough people to check those. So,

the trend of household-level slaughterhouse is

disappearing, gradually.

Private sector

priorities

Private sector are more

concerned about

economic profit over food

safety

the private sector they are more focused on

profit. They not always concern of improving

the facility. So that is what we see in Nghe An

and one market in Hung Yen as well

300

Location Rural areas are more

challenging to work in

compared to urban areas

due to lower consumer

awareness of food safety

if you can do that [have safe practices] in the

countryside, it's good already

Attuning to climate change: describes how climate change is impacting food safety,

how program participants are responding to climate change, and how SafePORK is

supporting climate change adaptation and environmental management.

Climate

impacts

Describes the impacts of

climate change, including

heat waves (making pigs

sick, encouraging

microbial replication in

pork products), heavy

rainfall (making

transportation of pork

challenging,

contaminating water,

delaying field visits), and

how climate change

impacts vary by region

(more-so in Hoa Binh and

Nghe An compared to

Hanoi and Hung Yen)

Climate change right now is a big problem. So

for example in Nghe An in the summer we

have to some days that are too hot. To keep

and maintain the quality of pork it is also hard

for them. Retailer do not have refrigerator to

keep the meat, meat is put on the table

Adaptation

strategies from

SafePORK

Perceptions on how

SafePORK activities and

recommendations directly

or indirectly helps

participants adapt to

climate change

So some small wet market also they operate

during the afternoon, between 4-7 pm. But

most of wet market operate early in the

morning. We encourage consumers to buy the

pork early morning and put in refrigerator. So

that in the evening they keep for cooking

Adaptation

strategies from

participants

Perceptions on how

participants are adapting

to climate change, such as

covering pork or using

water sprays to cool pigs

Sometimes if they have heavy or weather

difference in summer will have effect on pork

as well. And sellers, they have their own thing

of the cover by nylon or they put under cover

or box

Environmental

management

Describes food safety

actors’ concerns about the

environment (e.g. treating

When we do with slaughter or farm (with

PigRISK) do they have enough facility to treat

their waste to not affect sellers and community

301

waste and wastewater),

and SafePORK’s work

toward environmental

management (e.g.

discussions with market

managers and local

authorities)

around. Yeah. And recently we also talk with

local authority about how to keep the

environment of the market clean, the waste as

a market, clean every day, and how to treat

waste

Attuning to equity: Describes how SafePORK interventions are tailored to different

groups of people, what outcomes are achieved, and the context and mechanisms behind

the achievement of outcomes.

Tailoring

interventions

Describes intentional

design considerations for

different groups of people

we have some video for the retailer, but we are

thinking of making two different videos. One

by men retailer, one by women

Context Describes contextual

factors influencing the

adoption of safe practices,

including consumer

awareness and enabling

environment (e.g. water at

market)

Since the project has been discussed with the

market and commune management boards,

electricity and water have been provided.

Mechanisms Describes reasoning

behind adoption of

practices, including

changes in food safety

knowledge, concern for

food safety, consumer

perspectives, convenience

of practices, and provision

of training and equipment

I feel that not maintaining good hygiene will

affect the meat, and secondly, I’m also worried

about consumers' health when we clean and

provide better products, consumers will turn to

me more

Outcomes Described how SafePORK

research led to new

knowledge on food safety

or how outputs generated

were stronger together

compared to individually;

described changes to

enabling environment (e.g.

educating future

workforce, improvements

to slaughterhouse and

From my side, brought a lot of added value,

when working in different team or sector, I

learned to get more new ideas. Because when

we discuss on an issue with other sector, they

bring with me more chance to rethink what I

thought before, bring for me more ideas. I also

have more potential partners

302

market facilities,

promoting interest in Ban

pigs); described how

SafePORK led to changes

in food safety practice;

described how SafePORK

led to changes in

relationships


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