CBD Guidelines on biodiversity
in EIA & SEA
Arend Kolhoff - NCEIA, Roel Slootweg - SevS,
Rob Verheem - NCEIA, Robert Höft - secretariat CBD
Objectives
In response to CBD decision VI/7:
(a) Prepare guidelines on incorporating biodiversity
considerations in EIA providing full consideration of
all stages of the EIA process:
(b) Compile lessons learned from existing experiences
with SEA;
(c) Prepare guidelines on incorporating biodiversity
considerations in SEA.
Intention: replacement of decision VI/7 by a new set of
documents
Process 1
Phase 1: September 2004
• Case studies solicited on Biodiv in SEA
• Expand EIA guidelines
• Analysis of cases & outline of SEA guidelines
• Internal review
• First daft SEA guidelines
Phase 2: December 2004
• External review: invited BD & SEA practitioners
• Comments received through BD & SEA lists IAIA
• CBD launches web-based case studies database
• CBD Focal points invited for Internet discussion
• IAIA Boston: discussion on review comments
Process 2: finalising & beyond..
• Second draft EIA & SEA guidelines
• Distribution through lists
• IAIA Prague: final discussion SEA guidelines
• Presentation at SBSTTA (side event)
• Submission to CBD Conference of Parties
beyond present project:
• Integration into REC SEA manual, OECD-DAC wg on SEA,World Bank toolkit on SEA, MA (through CBD), FAO forestryEIA manual.
• Further implementation of action programme BD in IA
• CBBIA as effective & visible mechanism to support in-country initiatives and exchange of experiences
Completing EIA Guidelines
• 2002 - Base document: CBD decision VI/7A
“Draft guidelines for incorporating biodiversity-related issues into
environmental impact assessment legislation and/or processes and in
strategic environmental assessment “
• 2003 – SBSTTA/9/INF/18: Report on ongoing work.
Based on a summary of IAIA contributions containing
51 references.
• 2004 - IAIA Principles & Practise Series: Biodiversity
in IA + CBBIA & workshop discussions at IAIA
Vancouver
Contributions on SEA
• CBBIA (6):
– India (2), Nepal, Pakistan, RSA, SEA Guidance
• Projectteam (4):
– Bolivia, Netherlands (3)
• Contributions through IAIA (7):
– Belgium, EU trade IA, RSA (2), UK (3)
• Draft publications SEA special of JEAPM (4):
– Nepal, Netherlands, Sweden & RSA
Sector distribution:
– spatial planning (3), flood protection (3), roads (2), minerals
(2), forestry (2), power, water supply, energy, irrigation,
agriculture.
Review
• Invited SEA experts (5):
– Czech Republic, Netherlands, Portugal, UK (2x)
• Invited Biodiv experts (7):
– India, Central America, RSA (2), Sweden, UK (2)
• List responses (4):
– Cameroon, Canada, Lebanon, UK
Overall structure
1. Introduction– Background on CBD articles and decisions
2. How to interpret biodiversity– Introduction to non-biodiversity audience on how to treat
biodiversity in impact assessment from a CBD point of view
3. EIA Guidelines + Annexes: – structured according to internationally accepted procedural
steps
4. SEA Guidelines + Annexes– Elaborate background on SEA and the role/relevance of
biodiversity in impact assessment
– Structure linked to characteristics of PPPs, relevant to biodiversity
Review and frustrations of the editor
• This section is wonderful!
• Not accessible to non-
biodiversity people
• A monumental effort. You
have earned my almost
limitless admiration and
respect by actually pulling
together something that
makes sense!!! -
• This approach is not helpful.
• For a non-biodiversity
specialist not too
complicated to understand.
• There are clearly some
areas which are not so well
developed as others.
Comments on structure & terminology
Duplication of text boxes and annexes in EIA & SEA guidelines:
• Question: integrated document / stand-alonechapters?
MA terminology: more rigorous and clear in use
But: ecosystem services concept not used and/orappreciated in many parts of the world ; more functional approach in ecological sense.
• Question: fully consistent with MA or dovetailing two perspectives? (what is the audience?)
Impact assessment or environmental assessment??
• Glossary with definitions: OK
Comments on 2: how to interpret BD
• Overwhelming amount of info, little focus - show relevance to
impact assessment.
• Questions: do we need chapter 2 ?
• More on positive planning approach (is this an internationally
known concept?)
No net loss:
• (i) preserving irreplaceable and (ii) substitute replaceable.
• Impossible principle: focus on compensation.
Precautionary principle:
• More information; stress importance for biodiv
• Impossible to work with: there is always uncertainty
Cummulative impacts: stress it’s importance for regular EIA. OK
3: EIA guidelines - points of departure
• Internationally accepted sequence of steps
• Guidelines should be used when a national IA system
is being revised – the only chance for change.
• Consequently, focus on how to get biodiversity into
the process, not on how to do a biodiversity inclusive
assessment study (not a technical manual).
• Screening and scoping most important aspect of an
EIA system to guarantee a biodiversity inclusive
process.
Comments 3: EIA guidelines
Changes to 2002 version: simplification of screening criteria; expansion on later stages; delete SEA sections.
• Early stages OK – more needed on later stages: how to measure significance, examples of impacts (= guidance on the actual work); draw from available guidance.
• Better defined protected areas for screening.
• Differentiate (i) setting screening criteria, and (ii) doing the screening. Focus is on (i) only. (Discussion)
• Scoping: cost of alternatives / mitigation?
• Better highlight service: maintenance of biodiversity.
• (Scoping interpreted differently by UK people??)
SEA guidelines: points of departure
& points for discussion
Overarching question: how to better address biodiversity in SEA
• SEA process is leading: no seperate biodiversity process
• No pre-defined SEA procedure (different from EIA guidelines);
• Ecosystem approach: focus on people-nature interactions and
stakeholder involvement
• Harmonising with Millenium Ecosystem Assessment: ecosystem
services translate biodiversity into values for society (present &
future) (consistent terminology in EIA and SEA guidelines)
• Level of detail at which biodiversity can be described depends
on characteristics of the PPP under study
• These characteristics provide structuring principle for guidelines
– not intended to prescribe the entire SEA process
SEA: contents
1. Introduction
2. SEA, a family of tools
3. Why biodiversity-inclusive SEA – what difference
does it make to decision making?
4. Biodiversity and SEA: different perspectives
5. Is SEA needed from biodiversity perspective?
Biodiversity-inclusive screening
6. Is biodiversity attention required in SEA?
Biodiversity-inclusive scoping
SEA: different perspectives
• Biodiversity part of the voiceless environment = western perspective
• Biodiversity for social and economic well-being = developing countries perspective
• Merging perspectives = opposing views are disappearing
• Time & space = planning & biodiv horizons differ
Comments:
• this section is wonderfull versus not helfull/simplistic
• reviewers with BD background are uneasy with this section
SEA situations:
relate to characteristics of the PPP
1. Geographical delineation possible:
– Area-related info allow for mapping of ecosystem services &stakeholders
2. Known interventions with concrete biophysical consequences:
– direct drivers of change show potential impacts; define sensitive
biodiversity.
3. Both geographical area and intervention known:
– impacts on aspects of biodiversity (composition, structure, key processes)
can be predicted
4. No concrete biophysical consequences or very large scale
– indirect drivers of change & modelling (MA); identify linkages between
indirect and direct drivers of change.
SEA situations: comments
• The situations may induce
less familiar users to think
that these are the 4 possible
situations that occur in
relation to SEA and
biodiversity, which is not
correct.
• The situations described are
rather artificial (in practice,
many PPPs may feature
their combinations); quite
difficult to use in the SEA
practice.
• Rather describe them
irrespective of the type of
PPP
SEA: guidelines stop at scoping?
• The single reference to
screening and scoping, the
first two typical activities of
an EIA process may lead
people to wait to see the
remaining stages!! Why not
talking about objectives,
understanding the problem,
etc.?
• Were are sections on
assessment, monitoring,
decision-making?
• The guidelines end very
abruptly - include other steps
• Does not address remaining
elements of SEA
The different approach used in the EIA guidance and in the SEA
guidance was noted and appreciated. It is important, for the
purpose of enhancing the different role of SEA in decision-making
that guidance will direct mind mapping in different ways.
SEA: general comments on contents
Better explore links with NBSAP’s
• Do NBSAPs provide the expected benefits? (it only
appeared in the UK cases)
When NOT to include biodiversity:
• extremely opposing views on the need for this box.
Do more with IAIA SEA Performance criteria?
Interesting reading but no guidance. Does not provide
clear principles for dealing with biodiversity (no net
loss, carying capacity, home ranges, etc.).
• Isn’t chapter 2 providing this?
Assessment framework needed in main text (figures
from annex).
4: SEA: style & structure
Length of text: too long.
• “Is SEA explanation needed” versus move “SEA/EIA tables to main text”
Use of cases: “reduce text by moving to annex”; “put in boxes”; “cases merit more elaboration”.
• Suggested: Put in boxes in main text
Style
• SEA chapter specialised/academic/theoretical language
• Interesting as it leads towards actual thinking on SEA as opposed to SEA born on EIA grounds and common readings.
2nd order
biophysical
change
(on soil, water, air,
flora, fauna)
2nd ordersocial change
Intervention
physical
social
Impacts
on ecosystem
services
Range of
influence in
space and time
social impacts
changes in economic,
social and ecological
values of services
Indirect drivers
of change
MA framework
Direct
Drivers
Indirect
Drivers
Ecosystem
Services
Human
Well-being
Direct Drivers of Change� Changes in land use � Species introduction or removal� Technology adaptation and use� External inputs (e.g., irrigation) � Resource consumption� Climate change� Natural physical and biological drivers (e.g., volcanoes)
Indirect Drivers of Change� Demographic� Economic (globalization, trade, market and policy framework)
� Sociopolitical (governance and institutional framework)
� Science and Technology� Cultural and Religious
Human Well-being and
Poverty Reduction� Basic material for a good life� Health� Good Social Relations� Security� Freedom of choice and action