Site development in the coastal region differs ... · Green Growth Guidelines: Chapter 3-2...
Transcript of Site development in the coastal region differs ... · Green Growth Guidelines: Chapter 3-2...
Green Growth Guidelines:Chapter3-2 Stormwater Management
Sitedevelopmentinthecoastalregiondifferscomparativelytodevelopmentin
Georgia’sPiedmontarea,wheresitedevelopmentinvolvesmovingvastquantitiesoffill
materialtoflattenhillyterrainforbuilding.Inthecoastalregion,sitesaregenerallyflat
tomildlysloping.Basedonthis,developersinthisareaseekenoughchangeinelevation
topreventthesitefromflooding.Thisisoftenaccomplishedbydiggingpondsto
providealowpointtoreceivestormwater,andusingthefillgenerated(fromthecreation
ofthepond)toelevatebuildingpads.Uplandsoilsinthisregiontendtobesandyand
havehighinfiltrationrates.InthePiedmont,uplandsoilsgenerallyhavehighclay
contentandcharacteristicallylowinfiltrationrates.Thesedifferencesdriveachangein
emphasisinrecommendedLIDpracticesforthecoastalarea.
However,manyissuesaffectingdevelopmentactivityarequitesimilar.Land
developmentinbothregionsinvolvesremovingforestedcanopyandreplacingitwith
imperviouscoversuchasroads,parkinglotsandrooftops.Chapter2discussedthe
importanceofretainingasmuchoftheforestedcanopywithinadevelopmentaspossible,
aswellasreplacingthecanopythatislostwithnewplantings.Whenanareaofforestis
convertedtopavement,theareagenerateseighttimesmorevolumeofrunoffbasedonthe
lossofcoverfactoralone.AccordingtotheEPA,goingfromgrassedareastopavement
generatesatleasttwicetherunoff.Thisrunoffreachesthereceivingstreamsinmuchless
timethanfromforestedareas.
Hydrologistsoftenrefertoahydrographwhendeterminingthepeakflowofa
stormevent.Developmentactivitychangesthispeakflowbyincreasingthevolumeof,
andspeedatwhichrainfallbecomesrunoff.Thehydrographillustratesthechanges
inpeakflowforpre-developmentandpost-developmentconditionsincoastalGeorgia.
(Figure3.1.c)
Figure 3.1c Hydrograph Representing Pre-and Post-development Conditions
Image Courtesy of: State.ga.us
Green Growth Guidelines:Stormwater Management Chapter3-1
low imPAct develoPment And stormwAter mAnAgement
3.1 Introduction
ThisChapterdiscussesthemanagementofstormwateratitssourcebyretaining
wateron-siteratherthandisposingofitaswaste.Thisiscommonlyknownaslow
impactdevelopment(LID)andreferstoagroupofengineeringtechniquesusedtomimic
naturaldrainagesystems.LIDtechniquesmanagerainfallwithpassive,non-structural
practicesthatpromotegroundwaterinfiltrationorevaporationatorneartherainfallsite.
ThisChapteradaptstechniquesfromtheGeorgiaStormwaterManualandothersources.
(Figures3.1.aand3.1.b)
Figure 3.1a Conventional Approach: Manage Stormwater
with Centralized Regional Facility
Image Courtesy of: PGDER
Figure 3.1b Decentralized Approach: Manage Stormwater at source with LID Techniques
Image Courtesy of: PGDER
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Changesalsooccurinthequalityoftherunoff.Rainfalllandingonimpervious
areaspicksuppollutantsandmovesthemtoreceivingstreamsandotherwaterbodies.
Dissolvedoxygen(DO)inthewaterisreducedinurbanrunoff,sometimestolevels
fataltofishandotheraquaticlife.Intheprocess,rainfalltemperaturesareelevatedas
thewatermovesacrosshotsurfaces.Thesechangestowaterqualityarereferredtoas
“non-pointsourcepollution”andare“theleadingsourceofwaterqualitydegradationin
Georgia”(GeorgiaStormwaterManagementManual,2001).(Figure3.1.d)
Receivingstreamsaresignificantlyaffectedbythequantityandqualityof
stormwaterrunoff.Runoffleavingthesiteathighervelocityandingreaterquantity
scoursthestreambedandcreateschangestothechannelprofile,erodingthestream
banksanddrasticallychangingaquatichabitat(seeChapter4).Withanadditional
pollutantload,lowerdissolvedoxygen,andelevatedwatertemperatures,habitat
degradationisamplified.Also,sincemorewaterrunsoffthesitesooner,thereisless
waterslowlypercolatingthroughthesystemtosupportbaseflowsinthestream,creating
anotherchallengeforaquaticspecies.
Withalloftheseimpactsinmind,lowimpactdevelopmentstrivestoachievea
naturalhydrologicalsystemthatcanmaintainandevenreducepre-developmentrunoff
rates.Secondarygoalsinclude:
uWaterqualityimprovement,
uRechargeoflocalgroundwateraquifer,
uStreamprotection,
uWetlandpreservation,
Figure 3.1d Algal Bloom in Lake Caused by Increased Levels of Nitrogen and Phosphorus from
Non-Point Source Pollution
Green Growth Guidelines:Chapter3-4 Stormwater Management
uWildlifehabitatcreation,
uReducedurban“heatisland”effects,
uImprovedairquality,and
uEnhancedcommunityaestheticalappearance.
GreenGrowthGuidelines(usingLIDprinciples)balancesdevelopmentwith
inherentnaturalsitefeatureswhileenhancinglotyields,reducingdevelopmentcosts,and
encouragingdevelopmentandeconomicgrowth.
Theseguidelinesseektoeliminate,minimize,and
mitigatetherootcausesofdevelopment-generated
impactsatthesourcebyintegratingstormwater
managementmeasuresthatmakethedevelopment’s
landscapemoreecologicallyandhydrologically
functional.(Figure3.1.e)
3.2 Natural Processes for Stormwater Management
Naturalprocessesthatremovepollutantsfromstormwaterrunoffinclude:
(Figure3.2.a)
u Infiltrationandfiltration,
uSedimentation,
uDetentionandretention,and
u Interactionofstormwater
withvegetation.
Figure 3.1e Healthy Wetland Habitat
Photo Courtesy of: Chere Peterson
Figure 3.2a The Water Cycle
Photo Courtesy of: John Evans, USGS
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3.2.1InfiltrationandFiltration
Infiltration,water’sentryintodry,unsaturatedsoil,isthemostnaturaland
directwaytohandlestormwaterincoastalGeorgia.Itallowsrainwatertoquicklyenter
groundwaterbeforeaccumulatingapollutantload.Inarainfallevent,thisunsaturated
areaisashrinkingzonebetweenrain-soakedsoilatthesurfaceandthegroundwater
saturatedsoilatthewatertable.Wherewatertablesareparticularlyhigh,asisthecase
inthecoastalregion,thisunsaturatedgapisoftenmeasuredinafewfeetoreveninches.
(Figure3.2.1.a)
Stormwatertendstopoolonthesurface,ordependingongrade,becomes
runoff.Standingwaterorsheetflowcaninfiltratesoil,saturatingitfromthetopdown.
Soiltypeandcompactiondeterminethespeedatwhichthewaterpercolatesormoves
downwardthroughthesoil.Thereby,soiltypesaffecttheinfiltrationprocess.Infiltration
isdependentonthepresenceofawell-drainedsoilcapableofacceptingwaterand
facilitatingitsentry.Soilswithlargeparticlesizes(sandsandgravels)havegreater
infiltrationrates.Certainclaysandorganicsoils(muchsmallerparticlesize)canalso
playmajorrolesinchemicalactivitiesthatremoveorimmobilizepollutants.Assessing
thesoils,topography,andhydrologyduringsitefingerprinting(seeChapter1)isessential
tofindingsuitableareasforinfiltrationaswellaspreventingordiscouragingitin
unsuitableareas.
Infiltrationismosteffectiveinareaswithhighergroundelevations.However,
lowerelevationscanbeusedforinfiltrationiftheypossesssufficientdepthtothewater
Figure 3.2.1a Illustration of Infiltration Process
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tableandadequatesoilpercolationrates.Infiltrationcanonlybeusedinareaswhere
runoffisrelativelyfreeofpollutants(chemicals,harmfulbacteria)thatcanleachinto
andcontaminategroundwater.Greatcaremustbetakentoensurethatthewatertableis
protected.
Variousstormwatertechniquesuseinfiltrationtomanagestormwater.Infiltration
basinandtrenchesworkbetterinthecoastalplainthaninotherpartsofGeorgia.They
arelesssubjecttocloggingfromrunoffandhavehigherpercolationratesduetosandy
soils.Othertechniquesthatcombineinfiltrationwithvegetativefilteringinclude
bioretentionareas,enhancedswales,andraingardens.
3.2.2DetentionandRetention
Thesecondkeymethodofusingnaturalprocessestodelayrunoffisachieved
bytwosimilar,thoughintrinsicallydifferentprocesses:detentionandretention.These
processesmitigatethehydrologicandwaterqualityimpactsofstormwaterrunoff(due
toincreasedimperviousareaandincreasedrunoffvolume)bystoringandreleasing
stormwateratratessimilartoratesexistingpriortositedevelopment.Additionally,these
processescontroltherateofwaterflowthatreducesdownstreamchannelflooddamage
anderosion.(Figure3.2.2.a)
Whilethelinebetweendetentionandretentionmayblur,theoveralldifference
isclear.Detentionslowsthetimingofstormwaterrunofftolessenitsimpact,butdoes
notnecessarilyreducethequantityorimprovethequalityoftherunoffwater.Retention
simplyretainsanddisposesoftherunoffthroughnaturalhydrologicalprocesses.Since
Figure 3.2.2a Natural Detention in Wetlands
Photo Courtesy of: Tara Merrill
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manyhydrologicalprocessescanalsoremovepollutants,retentioncanalsoimprove
waterquality.Retentiondelaysthereleaseofrunoffbyincorporatingorenhancingthe
naturalhydrologicalactionsthatpurifyandredistributerainwater.
LIDtechniquesprimarilyuseretentionstrategies.Withtheexceptionofexcess
runoffflowthatmayberoutedaroundtheretentionsystem,runoffisnotreleasedtoa
channel,pipe,orwatercoursebutisessentiallydisposedofonsite.Aretentionsystem
focusesonthereleaseofrunoffthoughevapotranspiration(lossofwaterfromthesoil
byplantsviagasexchange)andinfiltration.Inmanyretentionpractices,mostnotably
infiltrationtrenches,thevoidspacesbetweenstonefillallowsforlocalizedmovementof
waterbelowthesoilsurface,eventuallyassistingthereturnofwatertothesoil.
Certainretentionpracticesplacemoreemphasisonstorageorimpoundmentthan
others.Adryretentionpondisagoodexample.(Figure3.2.2.b)Itisnormallyempty
andisfilledduringarainfallevent.Then,itdisposesofitsvolumethroughnatural
hydrologicalprocesses,includinggroundwaterrecharge,ratherthanbydirectdischarge
intoawatercourse.
Someretentionpracticesimpactwaterqualitymorethanothers.Forexample,in
amultiplecellpond,constructingsmallbermsinasequenceacrossthepondslowsrunoff
flow,promotessedimentremovalandallowsthestormwatertointeractwithvegetation
plantedonthebermsandalongthesides.Thiscombinationoftechniquesimproveswater
qualityinseveralways.Thefirstcellservesasasedimentforebayallowingsoilparticles
Figure 3.2.2b Dry Retention Pond
Photo Courtesy of: Dan Fischer
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todropoutofthewatercolumn.Thevegetationshadesthewatersurfaceandprovides
significantsurfaceareapromotingbiologicactivitythatservestocleanupthewater.
Detentionencompassesawiderangeoftechniquesincludingstorageinponds,
swales,andnaturalforestedwetlands.Thewaterthatentersadetentionsystemcanbe
processedforfurthertreatmentbutiseventuallyreleasedtoawatercourse.
Detentionmaycreatesomeimprovementstowaterquality.Forexample,simply
holdingthewaterforadayorsoinareservoirallowssomesedimentationandseparation
tooccur.Inlow-orno-flowconditions,particulatesnaturallydropoutofthewater
columnandsomesubstances,suchashydrocarbons,risetothetop.Somedetention
ponddesignsareintendedtohavemoreimpactonwaterqualityduringtheholding
period.Wetponds,forexample,permanentlyretainwaterandsupportvegetationthat
canassistinwaterqualitytreatment.Pondvolumeisprimarilyreducedbythereleaseto
awatercourse,ratherthanre-integrationintotheenvironment.Wetpondsaregenerally
excavatedtotheseasonalhighwatertable,creatinganadditionalhydrologicalinteraction.
Pondsthatincorporatepermanentpoolsofwateraredesignedtousethebiologicalaction
ofplantsandorganismstotrapandthentreatpollutants.
Forbothdetentionandretention,someformofimpoundmentisrequired.For
example,vegetationandforestfloororganicmatterinabufferzonemayprovide
sufficientchemicalorbiochemicalactiontotreatthewaterduringitsimpoundment.
Simpletemporarysurfacepoolingmayalsocontributetoretention.
3.2.3 Sedimentation
Thesettlingoutordepositionoferodedsoilsisreferredtoassedimentation.By
volume,sedimentmakesupthelargestpercentageofpollutantsenteringstreams,ponds
andlakes.Preventingerosionisthefirstandbestlineofdefenseagainstsedimentation.
Erosionbeginsinarainfalleventwhenwaterstrikesanexposedsoilsurfaceor
washesacrossitastherunoff,looseningsoilparticlesandsuspendingtheminthewater.
Sedimentationbeginswhenrunoffcarryingthisloadoferodedmaterialslows,allowing
particlestofallfromthewatercolumn,anddeposititonthestreambedorbank.
Sedimentationoccursgraduallywithheavierparticlessuchassanddropping
Green Growth Guidelines:Stormwater Management Chapter3-9
outfirstsincetheyrequirehigherflowvelocitytoremainsuspended.Thelighterthe
soilparticle,themoretimeitneedstodropoutofthewatercolumn.Asflowvelocities
continuetodecrease,thesmallest,lightestparticles(clay)settleoutintheslow-moving
areasofthewater.(Figure3.2.3)
Whilesoillossthrougherosioncansignificantlydamagethelandscape,its
depositionassedimentintostreamscanalsohavethefollowingadverseeffects:
u Increasedfloodingduetoreductionofchannelsizebysedimentdeposits,
uEventualchangeinthepathornatureofthestream,
uFilledsecondarychannels,cutofffromthemainstream,
uCloggedfloodcontroland/ortreatmentstructures,
uReducedfishspawningareasfromchangesinstreamcharacteristics,
uModifiedfishpopulations,ofteninfavoroflessdesirablespecies,
uReducedaquaticinsectcommunities,especiallythemorebeneficialspecies,asa
resultofsedimentation-inducedchanges,
u Impairmentordestructionofterrestrial(shore)habitatsbecausesedimentclogs
anexistingchannelandmakesthestreamspread,causinginundationofsensitive
wildlifehabitatalongthestreambank,
Figure 3.2.3 Extreme Sedimentation of River
Photo Courtesy of: The University of Florida Center for Aquatic and invasive Plants
Green Growth Guidelines:Chapter3-10 Stormwater Management
uReducedrecreationalopportunities,
uAdverseimpactoncommercialfisheries,
uReducedstreamnavigability,and
u Increasedcostsofkeepingharborsandmarinasusable.
InthestormwaterpracticesdiscussedlaterinthisChapterandinthebank
stabilizationtechniquesdiscussedinChapter4,thecaptureofsedimentson-sitebefore
reachingstreams,riversandotherwaterbodiesisemphasized.
3.2.4InteractionofStormwaterwithVegetation
Vegetationplaysanimportantroleinimprovingwaterquality.Whilesoil
microorganismsandsoil-basedchemicalreactionsremoveavarietyofnutrients,
pathogens,andheavymetals,vegetationassiststhisprocessinanumberofways:
(Figure3.2.4.a)
uSlowsrunoffflow,
uFilterslargeparticulates,
uProvidesconsiderableamountsofsurfaceareaonwhichpollutant-removing
microorganismsthrive,
uUseswaterfordirectmetabolicorstoragepurposes,
uDecomposesintoanorganicsoillayeractiveinneutralizingheavymetals,
uReleasesoxygenintothesoil,improvingwaterquality,and
uProvidesshadeforthewatersurface,reducingwatertemperature.
Figure 3.2.4a Buffered Stream Flowing Through Farmland
This buffer will slow nutrient loaded runoff before it reaches the stream.
Photo Courtesy of: Landstudies.com