TEAMMUIR I
(Jacobson,2016)
GreenRoofCarbonSequestrationPotentialof
Dalhousie’sHalifaxCampuses
APRIL2016
CODYMACDONALD-ENVIRONMENTALENGINEERING
JASMINBURCHELL-ENVIRONMENTALSCIENCEANDPSYCHOLOGY
NICOLESCOTNEY-ECONOMICS
OLIVIAKUEBER-INTERNATIONALDEVELOPMENTSTUDIES
PITCHAKONPADUNGDETPASUTON-ENVIRONMENTALSCIENCE&BIOLOGY
SAMDELLAPINNA-COMMUNITYDESIGNANDSUSTAINABILITY
TEAMMUIRMENTOR:ADAMCHEESEMAN
ENVS3502CAMPUSASALIVINGLABWITHTARAHWRIGHT
TEAMMUIR II
EXECUTIVESUMMARY
This project aims to determine the carbon sequestration potential if extensive green roofs were
installed on viable buildings on Dalhousie University's Carleton, Sexton, and Studley campuses in Halifax
RegionalMunicipality. Reasons to undertake this project are the potential to offset Dalhousie University's
carbonemissionsandfulfilltheuniversity'sgoalsregardingsustainability.
Research methodology consisted of determining which Dalhousie University buildings were
consideredviableinsupportinggreenroofs,usingtheArcGIStodetermineroofsurfaceareas,selectingagreen
roof plant species that can thrive in Nova Scotia's climate, and the carbon sequestration potential of that
species.
Byusingroofsurfaceareavaluesinconjunctionwithcarbonsequestrationpotentialvalues,several
scenariosforthetotalamountofcarbonthatcouldbesequesteredwerelaidout.Thetotalcarbonsequestration
wascalculatedtobe11,843to370,773kgofcarbon,or43,393.44to13,585,348.56kgofcarbondioxide.It
was estimated that Dalhousie University’s carbon emissions could be decreased by 7.00% through the
implementationofgreenrooftechnology.Thisreductionisroughlyequivalenttoremoving2,166mid-sizecars
fromtheroad.
The implementation of green roofs still decreases the total greenhouse gas emissions released by
Dalhousie.Althoughfindingsdidnot indicatea largemitigationofDalhousieUniversity’scarbonemissions,
green roofs may still be used as a method to reduce greenhouse gas emissions. For this reason, it is
recommended that Dalhousie University consider the implementation of green roofs, or other sustainable
techniques. This will provide opportunities for additional research while still continuously reducing
environmentalimpacts.
TEAMMUIR III
TABLEOFCONTENTS
1INTRODUCTION...............................................................................................................................................................1
1.1BACKGROUNDANDRATIONALE.......................................................................................................................................31.1.1TYPESOFGREENROOFS.............................................................................................................................................31.1.2GREENROOFBENEFITS...............................................................................................................................................31.1.3RELEVANTWORKCONDUCTED.....................................................................................................................................41.1.4THEDALHOUSIECAMPUS............................................................................................................................................51.1.5POLICIESONGREENROOFSINHALIFAX.........................................................................................................................6
2RESEARCHMETHODS.......................................................................................................................................................8
2.1METHODSOVERVIEW...................................................................................................................................................82.2DATACOLLECTION........................................................................................................................................................92.2.1LITERATUREREVIEW..................................................................................................................................................92.2.2ARCGIS.................................................................................................................................................................102.3DATAANALYSIS..........................................................................................................................................................112.3.1CALCULATIONS........................................................................................................................................................112.3.2ARCGIS.................................................................................................................................................................112.4DELIMITATIONSANDLIMITATIONS.................................................................................................................................122.4.1DELIMITATIONS.......................................................................................................................................................132.4.2LIMITATIONS..........................................................................................................................................................13
3RESULTS .................................................................................................................................................................14
3.1VIABLEBUILDINGS&TOTALROOFAREA........................................................................................................................143.2PLANTSPECIES&CARBONSEQUESTRATION....................................................................................................................153.3SCENARIOS................................................................................................................................................................16
4DISCUSSION.................................................................................................................................................................17
5CONCLUSION................................................................................................................................................................18
5.1RECOMMENDATIONS...................................................................................................................................................18
6ACKNOWLEDGEMENTS....................................................................................................................................................20
7REFERENCES.................................................................................................................................................................21
TEAMMUIR IV
LISTOFTABLES
Table1:SummaryofDataCollectionMethods..................................................................................................................................9
Table2:Summaryofliteraturesearchmethods............................................................................................................................10
Table3:SummaryofCarbonSequestrationPotentialScenariosAnalyzed.......................................................................11
Table4:CompliedDelimitationsandLimitations.........................................................................................................................12
Table5:ViableHalifaxCampusBuildings.........................................................................................................................................14
Table6:ScenarioCalculations...............................................................................................................................................................16
LISTOFFIGURESFigure1:ContextMap...................................................................................................................................................................................2
APPENDICES
AppendixA-GISSTEPS
AppendixB-CARBONSEQUESTRATIONCAREQUIVALENCYCALCULATIONS
AppendixC-OriginalProposal
TEAMMUIR 1
1 INTRODUCTION
Although it iswildly controversial among the public, there is substantial scientific consensus that
humanactivitycontributestoclimatechange(Boer,2014).Whileitisdifficulttopredicttheeffectsofclimate
change,itwilllikelyhaveadverseimpactsonecosystems(Döll&Zhang,2010)andsociety(Field,Barros,&
IntergovernmentalPanelonClimateChange,2014).Humanactivitycontributestoclimatechangebecausewe
getourenergyfromburningsubstancesthatemitgreenhousegases.DalhousieUniversityemitted97,393,000
tonnes(CO2equivalent)ofgreenhousegasesintheacademicyearof2013-2014(OfficeofSustainability,2014).
Toimprovetheirpractices,DalhousieUniversityistakingstepstomitigateandreducetheircarbonfootprint
(OfficeofSustainability,2014).DalhousiehasjoineduniversitiesacrossCanadainsigninga“ClimateChange
StatementofAction”acommitmenttoreducinggreenhousegasemissions(Pottle&Reagan,2012).Inlightof
this,ourresearchprojectinvestigatesthefeasibilityofaprojectthatwouldoffsetcarbonemissions.Thisoffset
wouldbeachievedthroughcarbonsequestration,aprocessbywhichatmosphericcarbonisremovedfromthe
atmosphere and stored in another form (liquid or solid). Specifically, the project will focus on carbon
sequestrationbyplants; throughphotosynthesis,plantsremovecarbondioxidefromtheair,andstore it in
theirtissuesassugar.
ThisprojectfocusesonthecampusesofDalhousieUniversitylocatedinHalifaxRegionalMunicipality,
NovaScotia,whicharetheCarlton,Sexton,andStudleycampuses.Partofthereasoningbehindthisstudyarea
isthatitisdifficulttosequestercarbonthroughplantsonanurbancampuswithmanyroadsandbuildings.An
innovative solution to this is the use of green roofs; a roof of a building that is covered with vegetation.
Dalhousie University already has some green roofs installed such as theMona Campbell building and the
LeMarchantPlacebuilding.Thisproject’sresearchexploredthepotentialforgreenroofsonexistingHalifax
campusbuildings.
Thisproject’sresearchaimstodeterminethecarbonsequestrationpotentialof installingextensive
green roofs on viable buildings pre-dating 2016 on Dalhousie University’s Halifax campuses. Extensive is
defined inSection1.1.1,andtheclassificationofwhatconstitutesaviablebuilding issetout inSection3.1.
Figure1,locatedbelow,providesacontextmapoftheDalhousieUniversitybuildingsconsideredinthisproject.
TEAMMUIR 2
Figure 1: A context map of the Dalhousie University buildings considered in this project,locatedinHalifaxRegionalMunicipality,NovaScotia
TEAMMUIR 3
1.1 BACKGROUNDANDRATIONALE1.1.1 TypesofGreenRoofs
Greenroofs,alsoknownasvegetativeroofs,canbedescribedaslayersoflivingvegetationontopofa
conventional roof (Miller, 2008). Modern green roofs can be classified as intensive or extensive systems,
dependingontheplantmaterialusedandtheintendedusagefortheroofarea(Getter&Rowe,2006).
Intensivegreenroofsaredesignedtobesimilartolandscapingfoundatnaturalgroundlevel,andare
thereforemuchheavierastheyhostalargerdiversityofplantspeciesanddeeply-rootedplants(Getter&Rowe,
2006). Theweight of vegetation anddeeper substrate requires costlier andmore complex buildingdesign
structurestosupportthistypeofroof(CreditValleyConservation,2008).Theyareoftenintendedforpublic
accessandthereforerequireregularmaintenance.
Extensive green roofs, on the other hand, are much smaller in depth and more lightweight than
intensive green roofs. These characteristics narrow the range of plant species they can support to herbs,
grasses, mosses, and sedum (Getter & Rowe, 2006). Extensive green roofs requireminimal maintenance
comparedtointensivegreenroofs,astheyarenotintendedforpublicaccess(Getter&Rowe,2006).Rather,
extensivegreenroofsareoftenusedtosatisfyengineeringandperformancegoalsofthebuilding(Miller,2008).
Duetothenatureofthisproject’sresearch,focushasbeennarrowedtosolelyextensivegreenroofs.
Reasoningforthisisthattheyarelesscostlyandrequirelessstructuralsupportthanintensivegreenroofs,
allowingthemtobemorefeasiblyimplementedonexistingbuildingsonDalhousieUniversity’sHalifaxcampus.
1.1.2 GreenRoofBenefits
Environmental
Therearenumerousenvironmentalbenefitsthatresultfromtheimplementationofagreenroof.The
installation of a green roof essentially offers a replacement for the vegetated footprint destroyed by the
construction of the building. Benefits of this vegetation include the management of storm water runoff.
Vegetationaidsindecreasingthevolumeofstormwaterrunoffbyabsorbingtheprecipitationandreducing
infiltration into groundwater,which results in a reduction of flooding and less stress onmunicipal sewer
systems(Getter&Rowe,2006).Greenroofsmayretain70to90percent(%)ofprecipitationduringsummer
months,and25 to40% inwintermonths (GHRC,2014). Additionally, thequalityof stormwater runoff is
improvedwiththeinstallationofagreenroof,asimpervioussurfacescollectpollutants,includingoil,heavy
metals, salts, pesticides and animal wastes. These contaminants may wash in to streams and waterways,
resultinginanegativeeffectonbothecosystemsandhumanhealth(Getter&Rowe,2006).
TEAMMUIR 4
Replacingconventionalrooftopswithagreenroofalsoresultsinmitigationofwhatisknownasthe
urbanheatislandeffect.Thisistheoccurrenceofwarmtemperaturesinurbanareasduetothelargeamount
ofbuiltsurfaceswhichabsorbheatandradiateitbackintheeveninghours(Getter&Rowe,2006).Nightair
temperatures therefore remainhigh in built-up areas. Theurbanheat islandoccurs as a result of reduced
vegetation and increased impervious surfaces, combinedwith the heat-absorbing properties of structures,
whichinturncreateshighertemperaturesinsideandoutsidethebuilding(Getter&Rowe,2006).Greenroofs
aidinthereductionoftheurbanheatislandthroughtheprocessofevapotranspiration,inwhichmoistureis
abletore-entertheatmosphereandthereforecoolcities(GHRC,2014).
Economic
Roofstransferthegreatestheatlossfrombuildingsinthewinterandthehottesttemperaturesinto
buildingsinthesummer(GRHC,2014).Greenroofsofferasolutiontohighenergybillsbyhelpingtomaintain
internal building temperatures, reducing energy consumption and CO2 emissions (Castleton et al., 2010).
Indoortemperatureshavebeenshowntobe3-4°Clowerunderagreenroofwhenoutdoortemperaturesare
between 25 to 30 °C, while every 0.5 degrees decrease in internal building air temperature may reduce
electricityuseforairconditioningupto8percent(Getter&Rowe,2006).Buildingownershavetheopportunity
tosavemoneyonrenovatingout-datedstormwaterinfrastructureandtopowercoolingandheatingsystems
(Getter&Rowe,2006).Additionally,greenroofshavethepotentialtoout-liveconventionalrooftops,whichis
along-termcostsavingbenefit(GRHC,2014).
1.1.3 RelevantWorkConducted
In2006,agroupofstudentsenrolledinthecourseEnvironmentalProblemSolvingII(ENVS3502)
conducted an analysis to determine the feasibility of a Rainwater Collection system (RWCS) at Dalhousie
University. The foremost objective of their researchwas to examine an alternative sustainable solution to
reduce water consumption on campus. In the course of their data generation, the team chose interactive
techniques such as interviews and surveys to obtain crucial information and recommendations from
professionals“intheareasofwaterresourcemanagement,geology,engineering,plumbing,urbanplanningand
economics”(Abdual,Arsenault,Bachiu,Garrey,MacGillivray,&Uloth,2006).Otherproceduresundertookby
theteamincludeanextensiveresearchonthefunctioningofRWCSandwaterusageatDalhousieUniversity.
Subsequent to the compilation of the gathered information, their analysis has indicated the area between
UniversityofKing’sCollegeandLifeSciencesCentreasthemostfeasiblelocationforaninstallationofRWCS
(Abdulaletal.,2006).InspiteofthefactthattheirresearchstudywaspredominantlyonRWCS,theirarticle
doescontaindiscussionthatrelatestogreenroofs.Hence,reviewingtheirresearchstudycouldbebeneficial
becausebothRWCSandgreenroofsarecategorizedassustainabledevelopmentdesigns.
TEAMMUIR 5
In2009,afeasibilityanalysisofagreenroofontheLifeScienceCenterwasconductedbyagroupof
students enrolled in the same university course. They conducted a cost-benefit analysis of the economic,
environmentalandsocialimpactsofgreenroofs.Theyfoundthatthoughtheenvironmentalbenefitsofgreen
roofsoutweightheenvironmentalcosts,economiccostscaninitiallybehighandsocialbenefitsaredifficultto
quantify.AlimitationoftheirstudywasalackofinformationregardingLifeScienceCenter’sstructureandroof
capacity(Blocketal.,2009).Lastly,theteamconcludedthattheirprojectwouldbebeneficialtoanyonehas
similarinteresttotransformDalhousieUniversityintoamoreenvironmentallyfriendlycampus.Thisreport
gavealotofinformationonthecostsandbenefitsofgreenroofs,butwasrestrictedinscopetotheLifeScience
Centreandwaslimitedintheinformationtheycouldobtainaboutthebuilding’sstructure.Ourstudywilluse
avarietyofmethodstogetasmuchinformationaspossibleaboutcampusbuildingstructure,sothatphysical
feasibilityofgreenroofinstallationcanbeestablishedintheliterature.
In2015,anothergroupofstudentsconductedastudythatexaminedgreenroofsasapossiblestrategy
tomitigatetherisksofstormwateronStudleycampus.Thegoaloftheirstudywasto“addressthecurrent
issues with storm water management on Studley campus and apply a sustainable solution to mitigate
associatedenvironmentaldamages”(Cranstone,Hu,Laing,Watling&Zhang,2015).Theirreportacknowledged
theinstallationofagreenroofasanaffordableandhighlyeffectivewaytoimprovestormwatermanagement
andreducetheamountofwaterreachingsewers.ThroughtheuseofArcGIS,theprojectdefinedthetotalviable
surfaceareaofbuildingsonStudleycampusandestimatedtheinstallationcosttotheUniversity(Cranstoneet
al.,2015).Althoughthisstudywassimilarinthesensethatitfocusedonthepotentialofinstallationofgreen
roofsforDalhousie’sStudleycampus,theprojectonlyconcentratedontheeffectsthatgreenroofswouldhave
onthereductionofstormwateroncampus.
Incontrasttotheseprojects,ourprojectwillcontributetotheinformationonprojectedbenefitsof
greenroofinstallationonDalhousieUniversitycampusbyaddinginformationregardingcarbonsequestration
potential.Inaddition,ourstudywillapproximatelyquantifytheamountofcarbonsequesteredthroughgreen
roofinstallation.ThiswillgivetheOfficeofSustainabilitynumberstoworkwithastheyprojecttheircarbon
footprintinthefuture.
1.1.4 TheDalhousieCampus
TheDalhousie institutionhas threemajorcampuses located indowntownHalifax.Thesecampuses
include Sexton campus, Studley campus and Carlton campus. These three campuses combined consist of
approximately76buildings,manyofwhichhavethepotentialforthedevelopmentofagreenroof.Auniversity
campusisacomplexsystemduetothevariousprocessesthatarerequiredfornormaloperation.University
campuses can be associatedwith a large number of carbon emissions, some ofwhich are associatedwith
TEAMMUIR 6
transportation,electricity,heating,studentlaboratoriesandpilotscaleplants.Infact,campussustainabilityis
becomingan increasingconcerndue to theenvironmental impactsof theactivitiesconductedatuniversity
campuses (Alshuwaikhat & Abubakar, 2008). Therefore, education institutions are beginning to integrate
sustainablepracticesintoregularoperationbyimplementingsustainabilityintocurriculum,andevengoingas
faras signing international chartersanddeclarations (Nejati,2013).The implementationofgreenroofson
Dalhousiecampusbuildingsisanopportunitytoimprovethesustainabilityofthecampus.
Dalhousiehas implementedgreenroofsonsomeoftheirbuildings inanattempttopromotegreen
buildingthroughtheirsustainablebuildingpolicy.ThebuildingscontaininggreenroofsonDalhousieCampus
include the Mona Campbell, LeMarchant Place and Wallace McCain buildings. The green roofs on these
buildingsvaryinscale,andtheultimategoalofthesegreenroofsisnotnecessarilycarbonsequestration.For
example,whiletheMonaCampbellbuildinghasvegetativegreenrooftohelpfilterairpollutants,someofthe
otherobjectivesforimplementationincludereducingstormwaterrunoffandmitigatingtheurbanheatisland
effect.ThegreenroofoftheWallaceMcCainbuildingisaccessible,makingitanintensivegreenroofavailable
forpublicuse.Finally,theLeMarchantPlacegreenroofhasbothvegetationandsolarhotwatercollectorsto
help improvethesustainability.Therefore,agreenroofcanimprovesustainability inanumberofdifferent
ways.Theimplementationofafullscaleextensivegreenroofcomposedentirelyofvegetationmayprovean
effectivemannerofimprovingcampussustainabilitythoughcarbonsequestration.
1.1.5 PoliciesonGreenRoofsinHalifax
TheinstallationofgreenroofsacrosstheHalifaxcampuseswouldalignwithDalhousieUniversity’s
Sustainability Policy. This policy indicates that Dalhousie University focuses on sustainability goals,which
includesupportingphysicalsystemsthatenhancesustainabilityanddecreaseairemissions(Dalhousie,2009).
Agreenroof isaphysicalsystemthatnotonlyenhancessustainability,buthaspotential fordecreasingair
emissions through carbon sequestration. The policy also indicates that new and existing policies will be
developedtoachievethesesustainabilitygoals(Dalhousie2009).Thus,in2011,DalhousieUniversityapproved
asustainablebuildingpolicytoreduceenvironmentalimpactsandrepresentleadershipinsustainablebuilding
practices.Thepolicyindicatesthatanynewbuildinggreaterthan10,000squarefeetwillbedesignedtoachieve
Leadership in Energy and Environmental Design (LEED) gold certification, at aminimum. The policy also
indicatesthatanysmallerrenovationsandretrofitswillbeconsideredforsustainablebuilding,andtheconcept
ofLEEDforexistingbuildingswillbeexplored(Dalhousie,2011).TheLEEDGreenBuildingRatingSystemis
designedtobenchmarkhighperformancegreenbuildings.
AlthoughgreenroofsarenotmandatoryforLEEDcertification,thereareseveralratingpointsthatcan
beobtainedfrombenefitsassociatedwithgreenroofs.TheLEEDGoldcertificationrequiresqualificationfor
TEAMMUIR 7
atleast60ofthe110availableratingpoints,andtheimplementationofgreenroofscanhelpachievethisgoal
(CanadaGreenBuildingCouncil,2009).Becauseofthis,ourprojectassumesthatmostbuildingsconstructed
onDalhousieUniversityHalifaxcampusesinthefuturewillhavegreenroofs.Thus,ourprojectexploresthe
somewhatneglectedpossibilityofgreenroofsonexistingDalhousieUniversityHalifaxcampusbuildings.
Althoughgreenroofsprovideuniqueopportunities forsustainablebuilding, therearecurrentlyno
regulationsorby-lawsthatrequiretheirimplementationwithinHalifax.However,itisworthnotingthatthis
maynotbethecaseinthefuture.Infact,Torontoimplementedagreenroofby-lawin2009whichrequiredthe
installationofgreenroofsforlargeinstitutionalandindustrialbuildings(CityofToronto,2013).Installationof
green roofs may help compliance with any future policy or regulation amendments in Halifax Regional
Municipality.
TEAMMUIR 8
2 RESEARCHMETHODS
Todeterminewhichbuildingswereviable,aliteraturereviewofpaststudentprojectsonthesubject
ofgreenroofsatDalhousieUniversitywasconducted.Literaturereviewwasalsoconductedtodeterminethe
carbonsequestrationpotentialofgreenroofs:FirstbyidentifyingplantspeciesnativetoNovaScotiathatcould
thrive on green roofs, then by discovering the quantitative carbon sequestration potential of these native
plants.While these literature reviews took place, the surface area of viable buildingswas identified using
ArcGIS.Withthequantitiesofcarbonsequestrationandroofsurfacearea,calculationsweredonetodetermine
thepotentialforcarbonsequestrationonDalhousieUniversity’sHalifaxcampuses.
2.1 METHODSOVERVIEW
Theresearchperformedwasdeductiveandquantitativeinnature.Theliteratureresearchperformed
inthebackgroundstudyindicatesthatanextensivegreenroofisabletosequestercarbonfromtheatmosphere.
ThismeansitisreasonabletoexpectthattheDalhousieUniversityHalifaxcampuseswouldbeabletosequester
carbonifextensivegreenroofswereinstalled.Thequantitativedatacollectedallowedfortheestimationofthe
amountofcarbonsequestrationpossible,ifextensivegreenroofswereinstalled.
The purpose of the research was to determine the carbon sequestration potential from installing
extensive green roofs on viable buildings (as defined in Section 3.1) in the Dalhousie University Halifax
campuses.Therefore,therewasquantitativedatacollectedbasedonDalhousieUniversitybuildinginformation
andcarbonsequestrationpotentialsofextensivegreenroofs.Themajorgoalwastocollectbuildingsurface
area(measuredinmetressquared{m2}),andcarbonsequestrationpotentialofplants(measuredinkilograms
of carbon dioxide per squaremetre {kg CO2/m2}) to determine the total amount of carbon (measured in
kilogramsofcarbondioxide{kgCO2}) thatcouldbesequestered.The typesofdatabeingcollectedand the
methodsofcollectionhavebeenbrieflysummarizedinTable1.
BuildinginformationwascollectedbyfirstdeterminingthenumberofDalhousieUniversitybuildings
whicharecapableofsupportinganextensivegreenroof.Criteriaforvalidroofsweretoberelativelyflatand
toappearcapableofsupportingagreenroof.Theseviablebuildingswerethenusedtodeterminethetotal
surfaceareaavailable forextensivegreenroof installation.Carbonsequestrationpotential informationwas
collectedbasedonexistingextensivegreenroofsandvaryingvegetationspecies.Vegetationspeciesfocused
onvegetationthatisabletoacclimatetotheHalifaxclimate.ThemethodsofdatacollectionincludedArcGIS
analysis,andliteraturereview.Interviewsweretobeconductedonlyiftheliteraturesreviewandgeographic
information system (GIS) analysis were unable to provide sufficient information; however this was
TEAMMUIR 9
unnecessaryastheinformationwasreadilyavailable.Themajorityofthedatacollectionwasassociatedwith
literatureresearch.
Table1:SummaryofDataCollectionMethods
Information DatatobeCollected MethodofCollection
Building
Information
BuildingscapableofsupportingagreenroofwithinHalifax
Campuses
LiteratureReview
Totalsurfaceareaofviablegreenroofspace ArcGISSoftware
Carbon
Sequestration
Potential
Determinationofoptimalplantspeciesforgreenroofsat
DalhousieUniversity,HalifaxNovaScotia
LiteratureReview
Carbonsequestrationpotentialofspecificplantspecies LiteratureReview
TotalcarbonsequestrationpotentialofHalifaxCampuses DataAnalysis
2.2 DATACOLLECTION2.2.1 LiteratureReview
Theresearchprojectdidnotinvolveanyformofsampling,andthereforealiteraturesearchwasone
ofthechosenmethodsfordatacollection.Itwasdeterminedthatthiswouldbethemostreliableandefficient
methodtocollectdata.Thisisbecausethemajorityofrelevantcarbonsequestrationinformationwasreadily
availableinliterature.Thisalsominimizedthetimeassociatedwithresearchbyavoidingtheschedulingand
developmentofinterviews.
Firstly, a list of all buildings on Dalhousie’s Halifax campuses was obtained from their website
(DalhousieUniversity,n.d.).To findoutwhichbuildingswereviable foragreenroof, literaturereviewwas
conductedanalyzingpreviousstudiesperformedongreenroofs.Thefirsttaskwasreviewingpreviousprojects
conductedatDalhousieUniversitythatareassociatedwithgreenroofs.Thisinformationwasobtainedfrom
Dalhousie online libraries and previous ENVS 3502 projects. These studies were able to provide some
informationonbuildingscapableofsupportingagreenroof.However,theinformationofbuildingsuitability
wasinsufficient,andfurtheranalysiswasperformedusingothersources.Thesesourcesincludedmunicipality
by-lawsrelatedtogreenroofs,andbestpracticesforgreenroofs.Basedonthis,criteriawereformedtoassess
abuilding’sabilitytoholdagreenroof:theslopeoftheroof is lessthan10°,andtheroof isnotonasmall
residential-style building. If a building fit these criteria, it was considered viable. Dalhousie University
infrastructureinformationwasanalyzedusingArcGIS.
Finally,literaturereviewwasperformedtodeterminepotentialplantspeciesforimplementationon
thegreenroof.Thisinvolvedresearchingcharacteristicsofdifferentplantsincludingtopicsonnativelocation,
TEAMMUIR 10
carboncontent,carbonsequestrationpotential,etc.Differentspeciesareabletosequesterdifferentquantities
ofcarbon,basedontheirgrowingcapacity.Thissectionoftheliteraturereviewfirstdeterminedspeciesthat
wereabletoacclimatetoHalifax’sclimate.Then,thespeciescommonlyusedongreenroofswiththisclimate
werefound.ThespecieswithpotentialuseforextensivegreenroofsinHalifaxwerethenfurtheranalyzedfor
theirspecificcarbonsequestrationrates.Asummaryof thedatabasesandkeywordsused in this literature
reviewcanbeseeninTable2.
Table2:Summaryofliteraturesearchmethods
Research DatabasesSearched KeyWords
Nativegreenroof
species
ProQuest
WebofScience
GreenRoof
Sedum
Sedumcarbon
sequestrationrates
Agricola,BiologicalandAgriculturalIndex
EnvironmentalSciencesandPollutionManagement
CarbonSequestration
[SpeciesName]
CarbonContent
Sedum
2.2.2 ArcGIS
ArcGIS,acomputerprogramprovidedbyEsriwithpermissionfromDalhousieUniversity,wasusedto
calculatethetotalsurfaceareaofviablegreenroofspaceonDalhousieUniversity’sHalifaxcampusbuildings.
Theuseofthisresearchtoolwasquantitativeinnature.
To use ArcGIS as a research tool, data was required. Specifically, data on building footprints
(representingthespacebuildingstakeupwithintheirlots,providinganapproximatesizeoftheirroofs)within
DalhousieUniversity’sCarlton,Sexton,andStudleycampuseswasneeded.Dataforbuildingswasbeobtained
throughtheuseofDalhousieUniversityGISCentre’sin-housedata,specificallytheHalifaxMunicipality2012
CorporateDataset.PermissiontousethisdataisgrantedtoDalhousieUniversityfaculty,staff,andstudents
(Dalhousie University, 2015a); thus, the SUST 3502 students undertaking this project had access to these
datasets. In the cases that thesedatasetsdonotprovide sufficientbuildingdata, the shapefiles (a file type
containing geographic data aswell as other information)were createdmanually inArcGISusing the same
projectionastheDalhousieUniversityGISCentre’sdataset.
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2.3 DATAANALYSIS2.3.1 Calculations
The carbon sequestration potential (measured in kg CO2) of extensive green roofs on Dalhousie
UniversitycampuswascalculatedbyusingthesurfaceareasimulatedfromArcGISandthevaluesobtained
fromplantspecies literaturereview.Thespecificcarbonsequestrationvalue(measured inkgC/m2)of the
plantspecieswasmultipliedbythetotalsurfacearea(measuredinm2)ofthegreenroofs.However,thevalues
foundintheliteraturereferredtotheweightofonlythecarbonatomsthemselves,sothishadtobeconverted
tokgofCO2throughstoichiometry.Thecarbonsequestrationpotentialofthesedumspecieswasanalyzedto
determineboththeminimumandthemaximumsequestrationratefoundintheliterature.Thecalculations
consideredminimum roof coverageof 50%andmaximum roof coverageof 100%.A carbon sequestration
potentialwascalculatedforfourdifferentscenarios.Thecalculationsperformedtoanalyzethesefourdifferent
scenarioshavebeensummarizedinTable3.
Table3:SummaryofCarbonSequestrationPotentialScenariosAnalyzed
Scenario SpecificCarbonSequestration
Rate
Roofcoverage
MinimumSequestrationPotential Minimumsequestrationrate 50%
LowsequestrationPotential Minimumsequestrationrate 100%
HighSequestrationPotential MaximumSequestrationrate 50%
MaximumSequestrationPotential MaximumSequestrationrate 100%
Calculations were also performed to illustrate both the quantity of carbon dioxide produced by
DalhousieUniversity,andthecarbonsequesteredbyextensivegreenroofs.Theamountofcarbonproducedby
Dalhousie University was compared to the weight of a blue whale. The amount of carbon that would be
sequesteredasaresultofgreenroofinstallationwascomparedtothecarbonemissionsofvariouspassenger
vehicles.Theamountofcarbonsequesteredhasbeenrelatedtotheequivalentemissionreductionthatwould
beseenfromremovingthevehiclesfromtheroad.Theanalysiswasperformedforsmall,medium,largeand
hybrid cars for a varyingvariousannual traveldistances.This comparisonwasperformed to illustrate the
impactsofcarbonsequestrationatalevelthatisunderstandablebythegeneralpublic.
2.3.2 ArcGIS
ArcGISwas used to calculate the total surface area of roof space inmetres squared on Dalhousie
University’s threeHalifax campuses. In theproject’sdata analysis stage, this informationwas thenused in
conjunctionwithcriteriaidentifyingwhichroofswereconsideredviablefortheinstallationofgreenroofsand
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data regarding carbon sequestration potential to determine the total amount of carbon that may be
sequestered. An overview process taken in ArcGIS is described below; see Appendix A for a detailed
transcriptionofthestepstakentoobtainbuildingroofareaestimates.
Withtheappropriatedatagathered,ArcGISwasusedto isolatebuildingsonDalhousieUniversity’s
Carleton, Sexton, andStudley campuses.The shapefilesof thosebuildingswere selectedandexportedasa
separatelayer.Theareaofeachbuildingshapefilewasthencalculatedinthatnewlayer’sAttributeTableand
exportedinaformatviewableatalatertimeinMicrosoftExcel.Roofareawasestimatedbycalculatingthearea
ofthebuildingfootprints,whichprovidedanapproximatesizeoftheirroofs.
AmajorbenefitofusingArcGISasaresearchtoolisthatoncetheappropriatedata(shapefiles)are
gathered, theprogramcanbeusedtoalmost instantlycalculaterequiredareavalueswithonlysmalleffort
exertedbytheuser.ArcGIScanalsothenbeusedtocreatemapstoaidwiththerepresentationsofresearch
findingsinwrittenreportsorpresentations.
2.4 DELIMITATIONSANDLIMITATIONSSeveral delimitations (constraints set by the researchers) and limitations (constraints beyond the
researchers’control)werepresentinthisproject.Theyareasfollows:
Table4:CompliedDelimitationsandLimitations
Delimitations Description
Detailofroofcriteria RoofcriteriawereonlyestimationsofwhichDalhousieUniversity
buildingswouldbeconsideredviableandmaynotbeinfalliblycorrect
Itmaybepossibletoinstallgreenroofsonbuildingsnotincludedin
thisproject’scriteria
Estimationsofroofcoverage Roofcoveragewasestimatedwithgeneralisedscenarios,howeveron
acase-by-casebasis,buildingsmaysupportsmallerareasofgreen
roof
Costconsiderations Thisprojectdidnotfocusonthefinancialimplicationsofinstalling
greenroofs
Costmaybeadeterminingfactorinwhetherornotgreenroofswere
tobeinstalledonDalhousieUniversitybuildings
Limitations Description
Time Thisproject’sfocuswasnarrowedgiventheamountoftimeavailable
foritscompletion
TEAMMUIR 13
Givenmoretime,financialimplicationscouldhavebeenconsidered,
andmoreinformationcouldhavebeengatheredontheviabilityof
buildingstosupportgreenroofs
Literatureavailable–Carbon
sequestrationpotential
Onlytwousableresourceswerefoundtobeavailableregarding
carbonsequestrationpotential
Givenalargedifferenceinthecarbonsequestrationnumbers,more
documentationcouldhavepotentiallymeantmoreaccurateproject
results
Literatureavailable–Carbon
sequestrationpredictions
Theliteratureavailablewaslackingdetailastohowmuchcarbon
couldbesequesteredbeyondthefirstyearofimplementation
Availabilityofcarbonsequestrationinformationoverseveralyears
wouldhaveallowedthisproject’sresultstogiveabetterideaofgreen
roofeffectiveness
2.4.1 Delimitations
Adelimitationinourstudywasthebuildingsweeliminatedfromthestudybasedoncertaincriteria
suchasminimumroofarea(averysmallroofmaynotbeworthrenovating)ortypeofroof(buildingswithflat,
broadroofswillbefavouredoverbuildingswithpitchedroofs).Nootherinformationcouldbefoundonthe
architectureofDalhousieroofsandtheirabilitytosupportagreenroofinthetimeallotted.
2.4.2 Limitations
AlimitationtothisprojectwasthedetailinwhichthepotentialcarbonsequestrationofHalifaxcampus
buildingswascalculated.Thesecalculationswerelimitedaccordingtowhatdataisavailableintheliterature.
Datawasalsolimitedduetowhichgreenroofplantspecieshadcarbonsequestrationdata.
TEAMMUIR 14
3 RESULTS3.1 VIABLEBUILDINGS&TOTALROOFAREA
Weidentifiedtwenty-twobuildingsasviabletoberetrofittedwithgreenroofsbasedonthecriteria
weadoptedtoassessviability.Mostly largeacademicbuildingsweredeemedviableastheytendedtohave
large, flat roofs.By and large, small residential-style structureswere considerednot viable as theyusually
featuredslopedroofs.Thebuildingareasidentified,retrievedfromaMicrosoftExcelfileproducedusingdata
fromHalifaxMunicipality2012CorporateDataset,areasfollows:
Table5:ViableHalifaxCampusBuildings
BuildingName Area(squaremetres)
A,B,C,DBuildingcomplex&SextonLibrary 8853.94
BurbidgeBuilding 704.90
ChaseBuilding 797.30
ChemicalEngineering(FBuilding) 1236.80
ClinicalResearchCentre 3049.67
CollaborativeHealthEducationBuilding 1751.73
DalhousieArtsCentre 3652.88
DentistryBuilding 2848.31
G.H.MurrayBuilding(GBuilding) 730.43
GerardHall 573.75
GoldbergComputerScienceBuilding 191.42
HoweHall 5504.62
IndustrialEngineering(IBuilding) 380.56
KennethC.RoweManagementBuilding 2721.88
KillamLibrary 3386.56
LifeSciencesCentre 8271.71
LifeSciencesResearchInstitute 2831.74
MarionMcCainArtsandSocialSciences 3567.49
O'BrienHall(MBuilding) 557.21
RalphM.MedjuckBuilding(HBuilding) 1360.67
RisleyHall 2206.43
SirJamesDunnBuilding 2034.04
StudentUnionBuilding(SUB) 2598.65
TupperBuilding&KelloggLibrary 1400.24
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WeldonLawBuilding&LawLibrary 1951.63
Note:AsShapefilesofsomeDalhousieUniversitybuildingswerenotavailable,theareaoftheCollaborative
HealthEducationBuildinghasbeenestimatedbymanuallycreatingpolygonsinArcGISandcalculatingthe
areasfromthere.
3.2 PLANTSPECIES&CARBONSEQUESTRATION
Wefoundthatduetotheshallowgrowingmediaprofileofextensivegreenroofsthatrangefrom6
inchesorless,perennialplantssuchasforbs,sedum,moss,andgrassesarecommonlyselectedforcultivation
(GreenRoofTechnology,2016).Characteristicssharedamongthesespeciesarelowgrowthheight,afibrous
rootsystem,andminimalmaintenance.Inaddition,anyplantspeciesgrownongreenroofsmustalsobeable
tothriveunderintenseheat,cold,windanddrought.Asaresult,thesefactorsposedachallengeindetermining
suitablevegetationtypeforgreenroofs.
SomeoftheappropriateplantspeciesforHalifaxRegionalMunicipality’sclimatecompriseofgrasses,
shrubs,andmosses.PlantspecieswefoundthatgrowsuccessfullyongreenroofsinHalifax’sclimatewereBlue
Fescue (Festucaglauca),Chives (Alliumschoenoprasum),HairyGoldenrod(Solidagobicolor),Three-toothed
Cinquefoi(Potentillatridentata),Crowberry(Empetrumnigrum),PovertyOatGrass(Danthoniaspicata),Wavy
Hair-grass (Deschampsia flexuosa), Golden Root (Rhodiola rosea), Harebell (Campanula rotundifolia), and
SeasidePlantain(Plantagomaritima).Amongthisgreatvariationofnativeplantspecies,severalSedumspecies
such asSedumTernatum,SedumXenox, andSedumMatrona have been identified to possess a remarkable
capabilitytowithholdtheirresilienceandresistanceunderHalifax’shumidcontinentalclimate.Despitethe
differentappearanceswhichsetonespeciesfromoneanotherintheSedumgenus,allofthemshareseveral
things in common. All Sedum species are classified as succulent plants (United States Department of
Agriculture,n.d.),sotheyareabletostorewaterintheirthickleavesandrequireminimalsupplementalwater.
Incontrasttoothergreenroofplantspecies,Sedumcan“surviveandthriveonaslittleastworainspermonth”
(Vela,2014).Inaddition,paststudieshavealsoobservedthat“Sedumabsorbscarbondioxideandturnsitinto
malic acid,which is usedduring theday for photosynthesis. Thepores in the leaves only open at night to
minimizethelossofmoistureduringthehotanddryday”(Maja,2015).
The information we found for each species on carbon sequestration potential wasminimal. Most
searchesof“carbonsequestration”andaspeciesnamehadnoresults.Aboutfivepaperswerefoundonspecies
thatcouldgrowinNovaScotia,andtwoofthemincludedresultsonseveralSedumspecies.Thesepapersalso
hadthemostappropriateinformationforourproject,focusingspecificallyongreenroofsinclimatessimilarto
NovaScotiaclimate,andincludingabove-andbelow-groundsequestration.ThesetwopaperswerebyGetter,
Rowe,Robertson,Cregg,&Andresen(2009)andWhittinghill,Rowe,Schutzki,&Cregg(2014).Wittinghilletal.
TEAMMUIR 16
foundthatafteroneyear,manytypesofSedumgrowntogethersequestered5.87kgCarbon/m2.Getteretal.
foundthatonaveragethedifferenttypesofSedumsequestered0.375kgC/m2.Getteretal.explainedthattheir
higherresultcouldbeduetotheirstudyusingdeepersubstrate,irrigation,andgrowingthedifferenttypesof
Sedumtogether.
Severalresearchstudieshave indicatedthatspeciesrichnessdoes in fact intrinsicallyconnectwith
plantproductivity. For instance, it hasbeenobserved that suchphenomenon contributes to an increaseof
efficiency in assimilation of nutrients and solar energy, which then consecutively helps to yield a greater
productionofbiomass(UniversityofGotthenburg,2011).Furthermore,someresearchershavealsonotedthat
“plantspecieswithtallerheight,largerdiameter,andlargershootandrootbiomass”aremuchmoreeffective
atstoringcarboninplantbiomass(Andresenetal.,2009).Besides,itisalsoadvantageoustoincorporatenative
plantspeciestothegreenroofsastheyarebelievedtohaveevolvedaspartoftheregion’secosystem(Virginia
DepartmentofEducation,2013).
3.3 SCENARIOS
The two numbers we found for Sedum sequestration were very different. In addition, there was
insufficient informationonDalhousieUniversitycampusroofs, sowemadeassumptions inrelation toroof
area. These assumptions could be incorrect; however we accounted for this in the results with scenario
calculations.Weperformedcalculationsforfourdifferentscenariosusingthetwosequestrationresultsand
bothabestcaseandworstcasescenarioforusableroofarea.Thesecalculationsaresimplyalinearrelationship,
and therefore linear interpolationcanbeused todetermine thecarbonsequestrationofany roof coverage
percentagebetween50%and100%,fortherespectivespecificsequestrationrate.Inthebestcasescenario,
100%oftheroofareaweapprovedinourbuildingselectionwouldbeconvertedtogreenroofarea. Inthe
worstcasescenario,50%oftheroofareaweapprovedwouldbeconvertedtogreenroof.Forexample,ifsome
buildingswesaidcouldholdgreenroofsactuallycannot,orifsomebuildingscan’tfill100%oftheirroofwith
vegetation,the50%scenariowouldaccountforthis.Theresultsofthefourscenariocalculationsareshownin
Table6.
Table6:ScenarioCalculations
SpecificSequestrationRate
RoofCoverage TotalRoofSurfaceArea
Totalcarbon(C)sequestered
TotalCarbonDioxide(CO2)Sequestered
5.87kg/m2 100% 63,164m2 370,773kgC 13,585,348.56kgC0250% 31,582m2 185,386kgC 679,265.05kgC02
0.375kg/m2 100% 63,164m2 23,687kgC 86,790.54kgC0250% 31,582m2 11,843kgC 43,393.44kgC02
TEAMMUIR 17
4 DISCUSSION
Thegoalofthisprojectwasfindthecarbonsequestrationpotentialofinstallingextensivegreenroofs
onpre-existingbuildingsonDalhousieUniversity’sHalifaxcampuses.Accordingtoourcalculations,theanswer
tothisis11,843to370,773kgofcarboninthefirstyearofgreenroofinstallation.Thisresultsinamassof
43,393.44to13,585,348.56kgofcarbondioxidebeingremovedfromtheatmosphere.Afterthefirstyear,more
carbonwouldbesequesteredinthesoil,butnotquiteasmuchaswassequesteredinthefirstyear(Whittinghill
etal.,2014).Thisisaverywiderangeofresults,makingitdifficulttointerpret.Themainreasontherangewas
so large was the differing results of the literature review, suggesting that more research is needed to
understandcarbonsequestrationofplantsongreenroofs.
Taking themedian of our range (6,814,371 kg of carbon dioxide), installing green roofs on viable
DalhousieUniversitybuildingswouldsequesterenoughcarbontobetheequivalentoftakingapproximately
2,166mid-sizecarsofftheroadforoneyear*.Thefullrangeofcalculationsfordifferentvehiclescanbeseen
inAppendixB.Itisimportanttonotethattheseresultsonlyconsidercarbondioxidefromthecombustionof
fuel,notfortheentirelifecycleofthecar.Althoughthisresult issubstantial,DalhousieUniversity’scarbon
footprintismuchlarger,andthissequestrationonlyrepresents7.00%ofthetotalfootprint.Thisisalsobased
onagenerousassumptionthatthemediansequestrationrateisused.Dalhousiecurrentlyemitsgreenhouse
gassesatarateofaround97,393,000kgcarbondioxideequivalentsperyear(OfficeofSustainability,2014).
This is roughlyequal to themassof537bluewhales,basedonabluewhalemassof181,437kg (National
Geographic, n.d.). The highest sequestration estimation would sequester carbon dioxide equivalent to the
weightofapproximately75bluewhales.ThisshowsthatinordertooffsetDalhousieUniversity’slargecarbon
footprint,manyothermethodsofcarbonreductionmayneedtobeimplemented.
Thisstudyfilledagapinexistingresearch;therewasnoresearchdoneoncarbonsequestrationofall
viableroofsontheHalifaxcampuses.However,thisresearchdidnotconsidertwootherthings:theamountof
carbon dioxide emittedwhen building a green roof, and the amount of carbon dioxide emissions avoided
throughbuildingenergysavingsfromgreenroofs.Byincorporatingthesetwovalues,futureresearchcould
findanoverallnetcarbonfootprintofgreenroofs.
*Basedonamid-sizecardrivingadistanceof12,000milesatafuelconsumptionrateof33milespergallonandacarbondioxideproductionrateof8.65kgCO2pergallonoffuel.
TEAMMUIR 18
5 CONCLUSION
The feasibility analysis indicated that the assessment of the carbon sequestration potential was
relatively small, sequestering only 7% of Dalhousie University’s total emissions. This is a highly variable
estimationduetothelackofprecisionassociatedwiththespecificcarbonsequestrationrates.Howeveritis
stillclearthatgreenroofswouldbeunabletooutbalancethetotalcarbondioxideemissions,evenifinstalled
onallviablebuildingsonDalhousie’sUniversityCampus.Fortunately,thisisstillasufficientamountofcarbon
dioxidesequestrationtoequateremoving2,166mid-sizecarsfromtheroad.Eventhoughthesequestration
resultsareverysmall,itwouldstillprovidesDalhousieUniversitywithasmallerglobalwarmingimpact.Itis
strongly believed that additional research is required in the hope to ensure a more sustainable and safe
environmentthroughthemeansofextensivegreenroofcarbonsequestration.
OurresearchexaminedexistingbuildingsonDalhousie’sHalifaxcampuses,ratherthanonesyettobe
built.Olderbuildingsdonothavegreenroofs,suggestingthattheoptionofgreeningoldbuildingshasnotbeen
looked into.Basedonourresults, itwouldbeworthwhile forDalhousie to implementgreenroofsonolder
buildingsinordertoreducethecarbonfootprintoftheUniversity.
In conclusion, green roofs are a valuable part of any initiative for improving the sustainability of
buildings on campus. For this reason, it is highly recommended that Dalhousie University consider the
implementationofadditionalgreenroofsorothersustainabletechniquestomitigateenvironmentalimpacts
andprovideadditionalopportunitiesforresearch.
5.1 RECOMMENDATIONS
Thepurposeof thisresearchprojectwas to focuson thecarbonsequestrationpotentialof installing
additionalgreenroofsonviablebuildingsonDalhousieUniversityHalifax’scampuses.Wekeptthescopeof
ourresearchrathernarrow.WeonlyexaminedthecarbonsequestrationpotentialofSedumplantsthatwere
cultivatedongreenroofs(duetoitsprevalentuseinNovaScotiaandtheavailabilityofresearch),andonly
considered green roof implementation for relatively flat rooftops (to maximize the likelihood of
implementationwithoutdelvingintoalargeamountofdetailregardingcosts).Thescopeofourprojectcould
bebroadenedbyexploringtheeffectivenessofmoreplantandrooftypes,andbyincludingbuildingsbeyond
DalhousieUniversity’scampusesontheHalifaxpeninsula.
Nevertheless,ithasbeenillustratedthatextensivegreenroofscanbesuccessfullyinstalledonuneven
surface rooftops, though installmentcostsareestimated tobemoderatelyhigher.Assuch, researchcanbe
broadened by incorporating factors that were not included. In this research, green roofs are simply a
TEAMMUIR 19
sustainable technique that may help pave the way for Dalhousie University to undertake sustainable
management.DalhousieUniversitycanalsoconsiderotherenvironmentallyfriendlyinitiativestoenhancethe
healthofthesurroundingenvironmentwhilereducingexpensesfromenergyuse.
Thisstudyfocusedonexistingandoldbuildingsratherthannewones.Itiscounter-intuitivetoattempt
toreducecarbonfootprintbybuildingLEEDcertifiedbuildings,becauseunlessthesebuildingsarecompletely
carbon-neutral, theywilladdtothecarbonfootprintoftheschool.Findinginnovativeandefficientwaysto
improveoldbuildingsiscrucialtoreducingDalhousie’sfootprint.Agreenroofisonestrategy,butitshouldbe
accompanied bymany others, such as changing old lights and plumbing fixtures, ormaking heatingmore
efficient.
TEAMMUIR 20
6 ACKNOWLEDGEMENTS
WewouldliketothankourwonderfulcourseinstructorDr.TarahWrightforhelpingusimproveourresearch strategies and allowingus to do this research in her course. Thank you toAdamCheeseman, theTeachingAssistantwhosesageadviceguidedusthroughtheprojectweekly.Aswell,beingDalhousiestudentshasallowedustoaccessinformationthatwouldotherwisebeprivatetous,sowearegratefulthatDalhousieallowedustodothisresearchinitsfullcapacity.
TEAMMUIR 21
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System:AFeasibilityStudyforDalhousieUniversity,1–19.Halifax,NS:DalhousieUniversity.Retrieved
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past-projects/2006.html
Alshuwaikhat,H.M.,&Abubakar,I.(2008).Anintegratedapproachtoachievingcampussustainability:
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sequestrationpotentialofextensivegreenroofs.EnvironmentalScience&Technology,43(19),7564–7570.
doi:10.1021/es901539x
Blok,K.,Hutt,J.,Inglis,S.,Saunders,L.,&Wainwright,H.(2015).GreeningNewHeights–AFeasibilityAnalysis
ofaGreenRoofontheLifeSciencesCenter,3–8.Retrievedfrom
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projects.html
Boer,K.(2014).Summarizingthegreenhouseeffect.SolarToday,28(5),12–13.
CanadaGreenBuildingCouncil(2009).LEEDCanadaforexistingbuildings:operationsandmaintenance2009.
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http://www.cagbc.org/cagbcdocs/LEED%20Canada%20EBOM%20rating%20system.pdf
Castleton,H.F.,Stovin,V.,Beck,S.B.M.,&Davison,J.B.(2010).Greenroofs;buildingenergysavingsandthe
potentialforretrofit.Energyandbuildings,42(10),1582-1591.
CityofToronto(2013).Torontomunicipalcode:Chapter492,greenroofs.Retrievedfrom
http://www.toronto.ca/legdocs/municode/1184_492.pdf
Cranstone,S.,Hu,S.,Laing,E.,Watling,D.,&Zhang,Z.(2015).Thegreeningofstormwater
management-MitigatingtherisksofstormwateronStudleycampusthroughtheinstallationofgreenroofs.
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3502---past-projects.html
CreditValleyConservation(2008).Lowimpactdevelopmentstormwatermanagementplanninganddesign
guide.Retrievedfromhttp://www.creditvalleyca.ca/wp-content/uploads/2012/02/lid-swm-guide-
chapter4-4.2-green-roofs.pdf
DalhousieUniversity(n.d.).BuildingDirectory.Retrievedfromhttp://www.dal.ca/campus-maps/building-
directory.html
DalhousieUniversity(2009).Sustainabilitypolicy.Retrievedfrom
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TEAMMUIR 22
repository/SustainabilityPolicy.pdf
DalhousieUniversity(2011).Dalhousiesustainablebuildingpolicy.Retrievedfrom
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TEAMMUIR 24
APPENDIXA-GISSTEPS
GISSteps
The following are the steps taken using ArcGIS using the Halifax Municipality 2012 Corporate Dataset to
calculatethetotalsurfaceareaofroofspaceinmetressquaredonDalhousieUniversity’sCarleton,Sexton,and
Studleycampuses.
Calculatingroofareafromexistingbuildingshapefiles
AfterdesiredDalhousieUniversitybuildingswereselectedmanuallyusingSelectbyAttributes,making the
buildingstheirownshapefileby:
SelectExportData
Export:SelectedFeatures
Outputfeatureclass:“DalBuildings.shp”
Dissolving“DalBuildings.shp”sothatatotalareamaybecalculated:
Inputfeatures:DalBuildings.shp
Outputfeatures:DalBuildings_dissolve.shp
Calculatingtheareaof“DalBuildings_dissolve.shp”:
OpenAttributeTable
AddField…
Name:Area_m2
Type:Double
OK
Rightclickthe“Area_m2”columninthe“DalBuildings_dissolve.shp”AttributeTable
CalculateGeometry…
Property:Area
Units:SquareMetres[m2]
OK
Exportingthe“DalBuildings_dissolve.shp”AttributeTabletoafileformatthatMicrosoftExcelcanread:
Export…
Outputtable:DalBuildings_TotalArea.csv
OK
CreatingnewDalhousieUniversitybuildingpolygons
Using ArcCatalog, created a new shapefile titled “New_DalBuildings.shp” with the Spatial Reference
“NAD_1983_CSRS_UTM_Zone_20N”(thesamecoordinatesystemastheHalifaxRegionalMData2012).
AddedittotheworkingArcGISfile.
TEAMMUIR 25
Usingbuilding lotsizes,adjacentbuildings,andGoogleMaps(2016)asreference,buildingpolygonswhere
drawn.
Addedanewfieldtitled“Names”tothe“New_DalBuildings.shp”AttributeTable
InEditToolbar,addedappropriatebuildingnamestothe“New_DalBuildings.shp”AttributeTable
CalculatingtheareaofnewDalhousieUniversitybuildingpolygons
Calculatingtheareaof“New_DalBuildings.shp”:
OpenAttributeTable
AddField…
Name:Area_m2
Type:Double
OK
Rightclickthe“Area_m2”columninthe“New_DalBuildings.shp”AttributeTable
CalculateGeometry…
Property:Area
Units:SquareMetres[m2]
OK
Exportingthe“New_DalBuildings.shp”AttributeTabletoafileformatthatMicrosoftExcelcanread:
Export…
Outputtable:NewDalBuildings_Area.csv
OK
TEAMMUIR 26
APPENDIXB-CARBONSEQUESTRATIONCAREQUIVALENCYCALCULATIONS
Miles/Gal AverageDistanceDriven(miles)
CarbonDioxideProduced(kgremoved)
CarsRemovedFromRoad(SmallSequestration)
CarsRemovedfromRoad(LargeSequestration)
CarsRemovedfromRoad(MedianSequestration)
SmallCar 37 6000 1403.31 31 9681 4856
9000 2104.97 21 6454 3238
12000 2806.63 16 4841 2428
MediumCar 33 6000 1573.41 28 8635 4331
9000 2360.12 19 5757 2888
12000 3146.82 14 4318 2166
LargeCar 24 6000 2163.44 21 6280 3150
9000 3245.16 14 4187 2100
12000 4326.88 11 3140 1575
Hybrid 50 6000 1038.45 42 13083 6563
9000 1557.68 28 8722 4375
12000 2076.90 21 6542 3282
Carbondioxideemissionsfromfuelcombustionwereestimatedfromfourdifferentinternetsources.Itwas
foundthatemissionratewas8.019kgCO2/Gal(AmericanForests,n.d.),8.91kgCO2/Gal(EIA,2015)8.89kg
CO2/Gal(USEPA,n.d.)and8.80kgCO2/Gal(USEPA,n.d.).Anaverageemissionrateof8.65kgCO2/Galwas
usedtoperformthecalculations.Itwasalsofoundthatthefuelefficiencyofasmallcar,mediumcarandlarge
car could be estimated at 24miles/Gal, 33miles/Gal and 37miles/Gal, respectfully (Carbon Independent,
2015).
TEAMMUIR 27
APPENDIXC-TEAMMUIRPROPOSAL
PROPOSAL-FEEDBACK.DOCX DRAFT
GREEN ROOF CARBON SEQUESTRATION
POTENTIAL OF DALHOUSIE’S HALIFAX
CAMPUSES Preliminary Research Proposal
Preparedby:OliviaKueberNicoleScotney
CodyMacDonaldJasminBurchellHutPitchakonSamDellapinna
SubmittedtoDr.TarahWrightandAdamCheeseman
March3,2016
TEAMMUIR I
TABLEOFCONTENTS
1PROJECTDEFINITION.......................................................................................................................................................1
2BACKGROUNDANDRATIONALE..........................................................................................................................................2
2.1GREENROOFS.............................................................................................................................................................22.2GREENROOFBENEFITS..................................................................................................................................................22.3RELEVANTWORKCONDUCTED........................................................................................................................................32.3.1POLICIESONGREENROOFSINHALIFAX.........................................................................................................................4
3PROPOSEDRESEARCHMETHODS........................................................................................................................................5
3.1METHODSOVERVIEW...................................................................................................................................................53.2DATACOLLECTION........................................................................................................................................................63.2.1LITERATUREREVIEW..................................................................................................................................................63.2.2ARCGIS...................................................................................................................................................................63.3DATAANALYSIS............................................................................................................................................................63.3.1CALCULATIONS..........................................................................................................................................................63.3.2ARCGIS...................................................................................................................................................................73.4DELIMITATIONSANDLIMITATIONS...................................................................................................................................7
4SCHEDULEANDBUDGET...................................................................................................................................................8
4.1OVERALLSCHEDULE........................................................................................................ERROR!BOOKMARKNOTDEFINED.4.2BUDGET ERROR!BOOKMARKNOTDEFINED.
5DELIVERABLESANDCOMMUNICATIONPLAN.......................................................................................................................10
5.1COMMUNICATIONPLAN..................................................................................................ERROR!BOOKMARKNOTDEFINED.
6REFERENCES11
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LISTOFTABLES
Table3-1:SummaryofDataCollectionMethods.........................................................................................................5
Table41:TasksandMilestoneswithResponsibilities.................................................................................................8
LISTOFFIGURES
Figure1..........................................................................................................................................................................9
TEAMMUIR 1
1 PROJECTDEFINITION
Though it is wildly controversial among themasses, there is substantial scientific consensus thathumanactivitycreatesgreenhousegasemissionsthatcontributetoclimatechange(Boer,2014).Thoughitisdifficulttopredicttheeffectsofclimatechange,itwilllikelyhaveadverseimpactsonecosystems(Döll&Zhang,2010) and society (Easterling&Apps, 2005). Carbondioxide is amajor greenhouse gas of concern,whichhumansemitbyburningfossilfuelsforelectricity(“CarbonDioxideEmissions,”2016).DalhousieUniversityemittedover84,000tonnesofcarbondioxideintheacademicyearof2013-2014.Toimprovetheirpractices,DalhousieUniversity is taking steps tomitigate and reduce their carbon footprint (Office of Sustainability,2014).InlightoftheDalhousieOfficeofSustainability’sgoalofcarbonneutrality,ourresearchinvestigatesthefeasibility of a project that would offset carbon emissions. This offset would be achieved through carbonsequestration,aprocessbywhichatmosphericcarbonisremovedfromtheatmosphereandstoredinanotherform (liquid or solid). Specifically, our project will focus on carbon sequestration by plants: throughphotosynthesis,plantsremovecarbondioxidefromtheair,andstoreitintheirtissuesassugar.
TherearenotasmanyopportunitiesforplantcarbonsequestrationintheCityofHalifax(wherethelargerDalhousiecampusis)asthereareinruralareas.Aninnovativesolutiontothisisagreenroof;aroofofabuildingthatiscoveredwithvegetation.DalhousieUniversityalreadyhassomegreenroofsinstalledsuchastheMonaCampbellbuildingandsoon,theLeMarchantPlaceBuilding.OurresearchwillfindmorepotentialforgreenroofsonHalifaxcampus(i.e.theCarlton,Sexton,andStudleycampuses)buildings.
Ourresearchwilldeterminethecarbonsequestrationpotentialofinstallingextensivegreenroofsonviablebuildingspre-dating2016onDalhousieUniversity’sHalifaxcampuses.Extensiveisdefinedinpart2.1,andthedeterminationofwhatconstitutesaviablebuildingissetoutinsection3.
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2 BACKGROUNDANDRATIONALE
2.1 GREENROOFS
Green roofs are classified into two types, intensive and extensive. Intensive green roofs are oftenintendedforpublicaccessandconsistofgreatersoildepthsthanextensivegreenroofs.Intensivegreenroofsareabletohostalargerdiversityofplantspeciesanddeeply-rootedplantsduetotheirgreatersoildepths.Theyaremuchheavierinweightthanextensivegreenroofs,oftenrequiringmorecostlyandcomplexbuildingdesign structures to support them (Credit Valley Conservation [CVC] & Toronto and Region ConservationAuthority [TRCA], 2008). Intensive green roofs are often intended for public access and require regularmaintenance.
Extensive green roofs are much smaller in depth andmore lightweight than intensive green roofs.Althoughtheycansupportasmallerselectionofplantspecies,extensivegreenroofsrequirelessmaintenancethanintensivegreenroofsbecausetheyarenotintendedtobeseenbythepublic.Additionally,theyalsodonotrequirefertilizationandirrigationlikeintensivegreenroofs.
Ourresearchfocusesonextensivegreenroofsbecause,asnotedabove,intensivegreenroofsaremorecostly and require more structural stability. This means an extensive green roof is more feasible to beimplementedonDalhousieUniversityHalifaxcampusbuildings.
2.2 GREENROOFBENEFITS
Environmental
Fromanenvironmentalperspective,onebenefit is thatgreen roofsaid in themanagementof stormwater runoff. Stormwater is storedby the substrate and later takenupbyplants,where it returns to theatmospherethroughtranspirationandevaporation(GreenRoofsforHealthyCities[GRHC],2014).Inthisway,greenroofsdelaythetimeatwhichrunoffoccurs,thusdecreasingstressonsewersystems.Insummermonthsgreenroofsretain70-90%oftheprecipitationthatfallsonthem,whileinwintertheyretainbetween25-40%(GRHC,2014).
Vegetationonrooftopsalsoreduceswhatisknownasthe‘UrbanHeatIsland’effectbyabsorbinglightwhichwouldotherwisebeconvertedintoheatenergy.Throughtheprocessofevapo-transpiration,moistureisabletore-entertheatmosphereandcoolcitiesintheprocess(Draper,2002).Greenroofsalsoreducethedistributionofdustandparticulatematterthroughoutthecity,inadditiontosmog,whichcanplayaroleinthereductionofgreenhousegasemissionsaswellasadaptingurbancitiestoawarmerclimate(GRHC,2014).
Improvedairqualityisanotherenvironmentalbenefitofgreenroofs.Theplantsongreenroofsareabletocaptureairbornepollutantsandatmosphericdeposition,whilealsofilteringnoxiousgases(GRHC,2014).Bymoderating temperature,greenroofsmayalso reducedemandonpowerplants,potentiallydecreasing theamountofcarbondioxideandotherpollutantsbeingreleasedintotheair(GRHC,2014).
Economic
Roofs transfer the greatestheat loss frombuildings in thewinter and thehottest temperatures intobuildingsinthesummer(GRHC,2014).Increasedinsulationwhichgreenroofsprovideforbuildingsallowsforareduceddependenceonenergytomoderatethetemperatureofthebuilding.Indoortemperatureshavebeen
TEAMMUIR 3
showntobe3-4°Clowerunderagreenroofwhenoutdoortemperaturesarebetween25to30°C,andinthewinterheatlossisminimizedthroughaddedinsulationontheroof(Dunnett&Kingsbury,2004,33).Ownersthereforehavetheopportunitytosavemoneyontheclimatecontrolofthebuilding.Additionally,greenroofshavethepotentialtoout-liveconventionalrooftops,whichisalong-termcostsavingbenefit(GRHC,2014).
2.3 RELEVANTWORKCONDUCTED
In 2006, a group of students enrolled in the course Environmental Problem Solving II (ENVS3502)conducted an analysis to determine the feasibility of a Rainwater Collection system (RWCS) at DalhousieUniversity. The foremost objective of their researchwas to examine an alternative sustainable solution toreduce water consumption on campus. In the course of their data generation, the team chose interactivetechniques such as interviews and surveys to obtain any crucial information and recommendations fromprofessionals“intheareasofwaterresourcemanagement,geology,engineering,plumbing,urbanplanningandeconomics”(Abdulaletal.,2006).Otherproceduresundertookbytheteamincludeanextensiveresearchonthe functioning of RWCS and water usage at Dalhousie University. Subsequent to the compilation of thegathered information, their analysis has indicated the area between University of King’s College and LifeSciencesCentreasthemostfeasiblelocationforaninstallationofRWCS(Abdulaletal.,2006).InspiteofthefactthattheirresearchstudywaspredominantlyonRWCS,theirarticledoescontaindiscussionthatrelatestogreenroofs.Hence,reviewingtheirresearchstudycouldbebeneficialbecausebothRWCSandgreenroofsarecategorizedassustainabledevelopmentdesigns.
In2009,afeasibilityanalysisofagreenroofontheLifeScienceCenterwasconductedbyagroupofstudents enrolled in the same university course. They conducted a cost-benefit analysis of the economic,environmentalandsocialimpactsofgreenroofs.Theyfoundthatthoughtheenvironmentalbenefitsofgreenroovesoutweightheenvironmentalcosts,economiccostscaninitiallybehighandsocialbenefitsaredifficulttoquantify.AlimitationoftheirstudywasalackofinformationregardingLifeScienceCenter’sstructureandroofcapacity(Blocketal.,2009).Lastly,theteamconcludedthattheirprojectwouldbebeneficialtoanyonehas similar interest to transformDalhousie University into amore environmentally friendly campus. Thisreportgavealotofinformationonthecostsandbenefitsofgreenrooves,butwasrestrictedinscopetotheLifeScienceCentreandwaslimitedintheinformationtheycouldobtainaboutthebuilding’sstructure.Ourstudywilluseavarietyofmethodstogetasmuchinformationaspossibleaboutcampusbuildingstructure,sothatphysicalfeasibilityofgreenroofinstallationcanbeestablishedintheliterature.
In2015,anothergroupofstudentsalsoconductedastudy,whichexaminedapossiblestrategythatcanhelptomitigatetherisksofstormwateronStudleycampusthroughtheinstallationofgreenroofs.Thegoaloftheirstudywasto“addressthecurrentissueswithstormwatermanagementonStudleycampusandapplyasustainable solution tomitigate associated environmental damages” (Cranstone et al., 2015). Their reportacknowledgedtheinstallationofagreenroofasanaffordableandhighlyeffectivewaytoimprovestormwatermanagementandreducetheamountofwaterreachingsewers.ThroughtheuseofGIS,theprojectdefinedthetotalviablesurfaceareaofbuildingsonStudleyCampusandestimatedtheinstallationcosttotheUniversity(Cranstone et al., 2015). Although this study was similar in the sense that it focused on the potential ofinstallationofgreenroofforDalhousie’sStudleycampus,theprojectonlyconcentratedontheeffectsthatgreenroofswouldhaveon the reductionof stormwateron campus. In contrast to theirproject, ourprojectwillcontributetotheinformationonprojectedbenefitsofgreenroofinstallationonDalhousiecampusbyaddinginformationregardingcarbonsequestrationpotential.
TEAMMUIR 4
In addition, our studywill approximately quantify the amount of carbon sequestered by green roofinstallation. This will give the Office of Sustainability numbers to work with as they project their carbonfootprintinthefuture.
2.3.1 PoliciesonGreenRoofsinHalifax
TheinstallationofgreenroofsacrosstheDalhousieHalifaxcampuseswouldalignwithDalhousie’sSustainability Policy. This policy indicates that Dalhousie focuses on sustainability goals, which includesupportingphysicalsystemsthatenhancesustainabilityanddecreaseairemissions(Dalhousie,2009).Agreenroofisaphysicalsystemthatnotonlyenhancessustainability,buthaspotentialfordecreasingairemissionsthroughcarbonsequestration.Thepolicyalso indicates thatnewandexistingpolicieswillbedeveloped toachieve these sustainability goals (Dalhousie 2009). Thus, in 2011, Dalhousie University approved asustainablebuildingpolicytoreduceenvironmentalimpactsandrepresentleadershipinsustainablebuildingpractices.Thepolicyindicatesthatanynewbuildinggreaterthan10,000sq.ftwillbedesignedtoachieveLEEDgoldcertification,ataminimum.Thepolicyalsoindicatesthatanysmallerrenovationsandretrofitswillbeconsideredforsustainablebuilding,andtheconceptofLEEDforexistingbuildingswillbeexplored(Dalhousie,2011).TheLeadershipinEnergyandEnvironmentalDesign(LEED)GreenBuildingRatingSystemisdesignedtobenchmarkhighperformancegreenbuildings.
AlthoughgreenroofsarenotmandatoryforLEEDcertification,thereareseveralratingpointsthatcanbeobtainedfrombenefitsassociatedwithgreenroofs.TheLEEDGoldcertificationrequiresqualificationforatleast60ofthe110availableratingpoints,andtheimplementationofgreenroofscanhelpachievethisgoal(CanadaGreenBuildingCouncil,2009).Becauseofthis,ourprojectassumesthatmostbuildingsconstructedonDalhousieHalifaxcampusesinthefuturewillhavegreenrooves.Thus,ourprojectexploresthesomewhatneglectedpossibilityofgreenroovesonexistingDalhousieHalifaxcampusbuildings.
Althoughgreenroofsprovideuniqueopportunities forsustainablebuilding, therearecurrentlynoregulationsorby-lawsthatrequiretheirimplementationwithinHalifax.However,itisworthnotingthatthismaynotbethecaseinthefuture.Infact,Torontoimplementedagreenroofby-lawin2009whichrequiredtheinstallationofgreenroofsforlargeinstitutionalandindustrialbuildings(CityofToronto,2013).InstallationofgreenroofsmayhelpcompliancewithanyfuturepolicyorregulationamendmentsintheHalifaxarea.
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3 PROPOSEDRESEARCHMETHODS
Todeterminewhichbuildingsareviable,wewillconductaliteraturereviewofpaststudentprojectsonthesubjectofgreenroofsatDalhousie,andifnecessarywillconductinterviewswithknowledgeablepersons.Todeterminethecarbonsequestrationpotential,wewillconductaliteraturereviewonplantspeciesnativetoNovaScotiathatcouldthriveonagreenroofandthecarbonsequestrationpotentialoftheseplants.Wewillattempttoquantifytheamountofcarbonthattheseplantscouldsequester.Wewillfindtheareaoftheroofsof viable buildings using Arc Geographic Information System (ArcGIS). With the quantities of carbonsequestrationandroofarea,wewillmakecalculationstodeterminethepotentialforcarbonsequestrationonDalhousie’sHalifaxCampuses.
3.1 METHODSOVERVIEW
The research being performed is deductive and quantitative in nature. The literature researchperformedinthebackgroundstudyindicatesthatanextensivegreenroofisabletosequestercarbonfromtheatmosphere.ThismeansitisreasonabletoexpectthattheDalhousieUniversityHalifaxcampuseswouldbeabletosequestercarbonifextensivegreenroofswereinstalled.Thequantitativedatacollectedwillallowfortheestimationoftheamountofcarbonsequestrationpossible,ifextensivegreenroofswereinstalled.
Thepurposeoftheresearchistodeterminethecarbonsequestrationpotentialfrominstallingextensivegreen roofs on viable buildings in the Dalhousie University Halifax campuses. Therefore, there will bequantitative data collected based on Dalhousie University building information and carbon sequestrationpotentials of extensive green roofs. The major goal is to collect building surface area (m2) and carbonsequestrationpotentials(gCO2/m2)todeterminethetotalamountofcarbon(gCO2)thatcouldbesequestered.The types of data being collected and themethods of collection have been briefly summarized in Table 1.BuildinginformationwillbecollectedbyfirstdeterminingthenumberofDalhousieUniversitybuildingswhicharecapableofsupportinganextensivegreenroof.Thisinformationwillthenbeusedtodeterminethetotalsurfaceareaavailableforextensivegreenroofinstallation.Carbonsequestrationpotentialinformationwillbecollectedbasedonexistingextensivegreenroofsandvaryingvegetationspecies.VegetationspecieswillfocusonvegetationthatisabletoacclimatetotheHalifaxclimate.ThemethodsofdatacollectionwillincludeArcGISanalysis,andliteraturereview.InterviewswillbeconductedonlyiftheliteraturereviewandGISanalysisisunabletoprovidesufficientinformation.Themajorityofthedatacollectionwillbeassociatedwithliteratureresearch.
Table3-1:SummaryofDataCollectionMethods
Information DatatobeCollected MethodofCollection
BuildingInformation
BuildingscapableofsupportingagreenroofwithinHalifaxCampus LiteratureReview
Interview
Totalsurfaceareaofviablegreenroofspace ArcGISSoftware
CarbonSequestrationPotential
DeterminationofoptimalplantspeciesforgreenroofsatDalhousie LiteratureReview
Carbonsequestrationpotentialofspecificplantspecies LiteratureReview
TotalcarbonsequestrationpotentialofHalifaxCampus DataAnalysis
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3.2 DATACOLLECTION
3.2.1 LiteratureReview
Theliteraturereviewwillbeperformedbyanalyzingpreviousstudiesperformedongreenroofs.ThefirsttaskwillbereviewingpreviousprojectsconductedatDalhousieUniversitythatareassociatedwithgreenroofs.ThiswillbedoneintheattempttodetermineifthereareanypreviousstudiesreferringtotheviabilityofgreenroofsonDalhousiecampusbuildings.Thesestudieswouldbeabletoprovidethebuildingscapableofsupporting a green roof. If this information is unavailable, then studies will be performed on DalhousieUniversityroofcharacteristicsthatarecapableofsustainingagreenroof.DalhousieUniversityinfrastructureinformationwillbeanalyzedusingArcGIS.Finally,literaturereviewwillbeperformedtodeterminepotentialplantspeciesforimplementationonthegreenroof.Thiswillinvolveresearchingcharacteristicsofdifferentplantssuchasnativelocation,carboncontent,carbonsequestrationpotential,etc.Differentspecieswillbeabletosequesterdifferentquantitiesofcarbon,basedontheirgrowingcapacity.Thetotalcarbonsequestrationwillbecalculatedfromvaluesusedfromliterature,basedonplantspeciesandextensivegreenroofdata.
AninterviewingprocesswillbeconsideredifthedesiredinformationregardingDalhousieUniversityinfrastructure isnotavailable.Thiswill involvenon-probabilisticcriterionsamplingthroughtheprocessofinterviewingpersonswiththeknowledgeongreenrooftechnologyandDalhousieUniversityHalifaxcampusinfrastructure. The interviewwill be conducted in the form of an exploratory consultation. The interviewprocesswillrequestinformationregardingwhichbuildingsarecapableofsupportingextensivegreenroofs.
3.2.2 ArcGIS
ArcGIS,acomputerprogramprovidedbyEsriwithpermissionfromDalhousieUniversity(DalhousieUniversity, 2015a),will beused to calculate the total surface areaof viable green roof spaceonDalhousieUniversity’sHalifaxcampusbuildings.Useofthisresearchtoolwillbequantitativeinnature.
TouseArcGISasaresearchtool,dataisrequired.Specifically,dataonbuildingfootprints(representingthespacebuildingstakeup,andthusthesizeoftheirroofs)withinDalhousieUniversity’sCarlton,Sexton,andStudleycampusesisneeded.DataforbuildingswillbeobtainedthroughtheuseofDalhousieUniversityGISCentre’sin-housedata.PermissiontousethisdataisgrantedtoDalhousieUniversityfaculty,staff,andstudents(DalhousieUniversity,2015b;DalhousieUniversity,2015c); thus, theSUST3502studentsundertaking thisprojectwillhaveaccesstothesedatasets.Inthecasethatthesedatasetsdonotprovidesufficientbuildingdata,theappropriateshapefileswillbecreatedmanuallyinArcGISusingsatelliteimagery(includedintheDalhousieUniversityGISCentre’sdatasets)asabasereference.
3.3 DATAANALYSIS
3.3.1 Calculations
ThecarbonsequestrationpotentialofextensivegreenroofsonDalhousiecampuswillbeanalyzedbyusing the surface area calculated from ArcGIS and the values obtained from green roof and plant species
TEAMMUIR 7
research.Thecarbonsequestrationpotentialofthevariousplantspecieswillbereviewedtodeterminetheoptimumsequestrationrate.Theoptimumvaluecanthenbemultipliedbythetotalavailablesurfaceareatodeterminethetotalcarbonsequestration.
3.3.2 ArcGIS
ArcGISwillbeusedtocalculatethetotalsurfaceareaofviablegreenroofspaceinmetressquared(m2)onDalhousieUniversity’sthreeHalifaxcampuses.Indataanalysis,thisinformationwillbeusedinconjunctionwithdataregardingcarbonsequestrationpotentialandwhichroofsarecapableofsupportinggreenroofstodeterminethetotalamountofcarbonthatmaybesequestered.
Once thedata identifyingwhichbuildingscouldsupportgreenroofs isgathered through literaturereview,inArcGIStheshapefilesofthosebuildingswillbeselectedandexportedasaseparatelayer.TheareaofeachbuildingshapefilecanthenbecalculatedinArcGISinmetressquaredandexportedinaformatthatmaybeviewedatalatertimeeitherinArcGISorMicrosoftExcel.
Inthisprocessanymajorrooffeatures(suchasventilationdevices)thatwouldnotsupportagreenroofmustbeacknowledged.Todealwiththis,shapefileswillbecreatedfortheserooffeatures,theirareaswillbecalculatedandexportedfromArcGIS,andthenthoseareaswillbesubtractedfromthebuildingareadatainMicrosoftExcel.Ifthisprocessdoesnotworkasexpected,analternativewayofdealingwiththeserooffeatureshasbeenidentified.Hereseparatebuildingshapefileswhichdonotincludetherooffeaturesmaybecreated,andtheirareascanthenbecalculatedandexported.
Amajorbenefit ofusingArcGISas a research tool is thatonce theappropriatedata (shapefiles) aregathered,theprogramalmostinstantlycalculatestheareavaluesrequiredbytheprojectwithonlysmalleffortexertedbytheuser.ArcGIScanalsothenbeusedtocreatemapstoaidwiththerepresentationsofresearchfindingsinwrittenreportsorpresentations.
3.4 DELIMITATIONSANDLIMITATIONS
Adelimitationinourstudyisthebuildingswewilleliminatefromthestudybasedoncertaincriteriasuchasminimumroofarea(averysmallroofmaynotbeworthrenovating)ortypeofroof(buildingswithflat,broadroofswillbefavouredoverbuildingswithpitchedroofs).Moreprecisecriteriawillbeestablishedthroughouttheresearchprocess.
Anotherdelimitationisanassumptionofwhichvegetationtypeswillbeplantedinordertoprovidecarbonsequestrationcalculations.Astandardsetofplantswillbeselectedforthecalculationsofcarbonsequestrationacrosseachofthethreecampuses,ratherthandeterminingadesiredsetofplantsforeachindividualbuilding.
A limitationtothisproject isthedetail inwhichthepotentialcarbonsequestrationofDalhousieUniversityHalifax campus buildings can be calculated. These calculations will be limited according to what data isavailableintheliterature.Datawillalsobelimitedtemporallydependingonwhattimerangethedatacovers,aswellasinscope,dependingonwhichgreenroofplantspecieshavecarbonsequestrationdata.
TEAMMUIR 8
4 SCHEDULEANDBUDGET
Team Muir’s research project schedule is summarized in a Gantt chart, presented as Figure 1. FurtherinformationontheproposedtasksandwhoisdesignatedtocompletethemisprovidedinTable4-1.Ourteammemberswillprocureallwork.Assuch,fundingisnotrequiredtocontinuewithourproposedresearch.
Table4-1:TasksandMilestoneswithResponsibilities
Week(Datesall2016) TasksandMilestones Responsibility
Week3(Jan24-30) ENVS3502groupsassigned --
Jan26-Worksheetcompleted Everyone
SecretFacebookgroupsetup Hut
Jan31-Feb6 Weeklymeeting-determinationofresearchmethods Everyone
Feb7-13 CreateproposaltemplateandGoogleDocumentFolder Nikki
ReviewofpotentialGISrequirementsandcapabilities Sam
Reviewofexisting/capacityofgreenroofspecies Hut
Considerstructuralandtechnicalrequirements Cody
Initiateliteraturereview OliviaandJasmin
Weeklymeeting-researchprojectdevelopment Everyone
SnowdayWorkSheet Everyone
Feb14-20(Studybreak) IndividualizedResearch Jasmin,Hut,Olivia
Finalizeresearchquestion LeadbySam,supportedbyteam
ReviewpastENVS3502proposals Everyone
Developmethods SamandCody
Groupmeetingtodelegatesectionsofproposalwriting Everyone
Feb21-27 Groupmeeting-tofinalizeourresearchquestionandproposalresponsibilities
Everyone
Weeklymeeting-finalizationofmethodssection Everyone
Feb28-March5 Groupmeeting-worktowardsproposal Everyone
ResearchproposaldueMarch3rd Everyone
March6-12 Reviewfeedbackonproposal Everyone
Determineifinterviewsarerequired CodyandSam
Literaturereview Olivia,JasminandHut
March13-19 Furtherdelineaterolesandresponsibilitiestocompleteourresearchproject
Everyone
March20-26 Brainstormingsessionforpresentation Everyone
March27-Apr2 InternalReviewPechaKuchaSlide Everyone
Draftresearchprojectdueforinternalreview Everyone
Apr3-9 PechaKuchaprepandpresentation Everyone
Apr10-16 FinalizeandsubmitfinalProject Everyone
TEAMMUIR 9
Figure1:TeamMuir'sResearchProjectDevelopmentSchedule
WeeklyMeeting
ProjectDefinition
LiteratureReview
ResearchMethods
WeeklyMeeting
CreateProposalTemplateandPreliminaryResearch
WeeklyMeeting
AdditionalGroupMeeting
WinterStudyBreak
DevelopListofPotentialInterviewees
AdditionalGroupMeeting- prepareresearchproposal
WeeklyMeeting
GroupMeeting- finalizeresearchproposal
WeeklyMeeting
ResearchProposalDue
PotentiallyInterviewGreenRoofExperts
WeeklyMeeting
BrainstormingSessionforPechaKuchaPresentation
WeeklyMeeting
DevelopPechaKuchaPresentationSlides
WeeklyMeeting- darftReseachProjectdue
InternalReviewPechaKuchaSlide
FinalProject- InternalReviewDraft
GroupPechaKucha
FinalResearchProjectSubmission
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5 COMMUNICATIONPLANANDDELIVERABLES
Thepurposeofthisprojectistoprovideanunderstandingofthecarbonsequestrationpotentialifgreenroofs were installed on viable Halifax campus buildings.We hope our project will be useful to DalhousieUniversity;specificallytheOfficeofSustainability,astheyconsiderhowtomeettheirgoalofcarbonneutrality.OurcommunicationobjectiveistoprovideclearanddefensibleresearchthatcanbeconsideredbytheOfficeofSustainability,ourprofessorDr.TarahWright,ourmentorAdamCheeseman,aswellascurrentandfutureENVS3502students.
Indevelopingourwork,ourteamwillcommunicatebythreemainmethods:
1. In-classgroupdiscussions(heldweekly)
2. SundayResearchGroupsessions(asrequired)
3. FacebookandGoogleDocs-ongoingdiscussionandsharingofinformationrelatedtoourresearch
Our major deliverable will be our final report that presents our project, outlines our methods andsummarizesourfindingsInaddition,ourgroupwilldevelopapresentationtobedeliveredonApril5,2016.
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6 REFERENCES
Abdulal,H.,Arsenault,L.,Bachiu,T.,Garrey,S.,MacGillivray,M.,&Uloth,D.(2006).RainwaterCollection
System:AFeasibilityStudyforDalhousieUniversity(pp.1–19).Halifax,NS:DalhousieUniversity.
Retrievedfromhttp://www.dal.ca/faculty/science/environmental-science-program/research/envs-
3502---past-projects/2006.html
Andresen,J.A.,Cregg,B.M.,Getter,K.L.,Robertson,G.P.&Rowe,D.B.(2009).Carbonsequestrationpotential
ofextensivegreenroofs.EnvironmentalScience&Technology,43(19),7564–7570.doi:
10.1021/es901539x
Blok,K.,Hutt,J.,Inglis,S.,Saunders,L.,&Wainwright,H.(2015).GreeningNewHeights–AFeasibilityAnalysis
ofaGreenRoofontheLifeSciencesCenter(pp.3–8).Halifax,NS:DalhousieUniversity.Retrievedfrom
http://www.dal.ca/faculty/science/environmental-science-program/research/envs-3502---past-
projects.html
Boer,K.(2014).SummarizingtheGreenhouseEffect.SolarToday,28(5),12–13.
CanadaGreenBuildingCouncil(2009).LEEDCanadaforexistingbuildings:operationsandmaintenance2009.
Retrievedfrom
http://www.cagbc.org/cagbcdocs/LEED%20Canada%20EBOM%20rating%20system.pdf
CityofToronto(2013).TorontoMunicipalCode.Chapter492,GreenRoofs.Retrievedfrom
http://www.toronto.ca/legdocs/municode/1184_492.pdf
Cranstone,S.,Hu,S.,Laing,E.,Watling,D.,&Zhang,Z.(2015).TheGreeningofStormwaterManagement-
MitigatingTheRisksofStormwateronStudleyCamousthroughtheInstallationofGreenRoofs(pp.2–
6).Halifax,NS:DalhousieUniversity.Retrievedfrom
http://www.dal.ca/faculty/science/environmental-science-program/research/envs-3502---past-
projects.html
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CreditValleyConservation.(2008).LowImpactDevelopmentStormwaterManagementPlanningandDesign
Guide.Retrievedfromhttp://www.creditvalleyca.ca/wp-content/uploads/2012/02/lid-swm-guide-
chapter4-4.2-green-roofs.pdf
DalhousieUniversity(2009).SustainabilityPolicy.Retrievedfrom
http://www.dal.ca/content/dam/dalhousie/pdf/university_secretariat/policy-
repository/SustainabilityPolicy.pdf
DalhousieUniversity(2011).DalhousieSustainableBuildingPolicy.Retrievedfrom
http://www.dal.ca/content/dam/dalhousie/pdf/university_secretariat/policy-
repository/SustainableBuildingPolicy.pdf
DalhousieUniversity(2015a).Libraries:ArcGIS(ArcInfolicense)forWindows.Retrievedfrom
https://software.library.dal.ca/index.php?page=2
DalhousieUniversity(2015b).Libraries:GISdatadownload.Retrievedfrom
https://arcgis.library.dal.ca/gisdata/gis/index.php
DalhousieUniversity(2015c).Libraries:GISinhousedata.Retrievedfrom:
http://libraries.dal.ca/locations_services/services/gis_centre/gis_inhouse_resources.html
Döll,P.,&Zhang,J.(2010).Impactofclimatechangeonfreshwaterecosystems:Aglobal-scaleanalysisof
ecologicallyrelevantriverflowalterations.HydrologyandEarthSystemSciences,14(5),783–799.doi:
10.5194/hess-14-783-2010
Draper,Dianna(2002).Ourenvironment:ACanadianperspective(2nded.).Scarborough:NelsonThomas
Learning.
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Evaluation Project Definition – 4.5/5 Background and Rationale – 4.5/5 Research Methods – 4/5 Schedule and Budget – 3.5/5 Deliverables and Communication Plan – 5/5 References and Appendices – 4/5 Organization, Specifications and Writing Style – 3.5/5 Total – 29/35 or 8.3/10
Key Next Steps – You need to consider our comments and add in
some updated references especially in background and
methods. No budget included. Really great proposal overall,
keep up the good work!