Linking nitrogen pollution in estuaries to rocky shores: A stable isotope approach
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Transcript of Linking nitrogen pollution in estuaries to rocky shores: A stable isotope approach
S.Pillay1;3,Dr.A.J.Smit2,DrD.Robertson-Andersson1;3
1UKZN2UWC
3MACELab
Introduc)on
MainAimTheaimofthisstudywastoinvestigatethelevelandextentofNpollutiontothesouthcoastofKZN
Objec)vesThespecificobjectiveswere:
� (1)Todetermineifeachestuarychosenforthisstudyiseutrophicandcomparisonsmadewiththecurrentknownhealthstatus
� (2)Todeterminetheeffectofseasononnitrogenpollutioninrockyshoresduringtheclosedandopenphaseoftheestuary
� (3)Todetermineifthelevelofnitrogenpollutionchangeswithincreasingdistanceawayfromtheestuary.
HypothesesItwashypothesisedthat:� (1)ThereisadifferenceinNpollutionamongthethreesites(Hibberdene,MargateandPortEdward).
� (2)Rockyshorehabitatsaresupplementedbynutrientsfromestuarinesources
Studydesign
Choosingestuaries
Health state of estuary Description
Excellent Estuaries with high water quality, level of habitat integrity are high, high diversity and high provision of goods and services.
Good Estuaries with most of the core estuarine habitat and estuarine support habitats still present, good water quality, diversity of habitats and species and estuarine processes in place.
Fair Estuaries with core estuarine habitat intact, some estuarine support habitats, impacted water quality and some loss of diversity and key estuarine process in place.
Poor Estuaries with impacted core estuarine habitat. Substantially reduced or no estuarine support habitats, polluted water, substantial loss of diversity and/or abundance and key estuarine processes impaired.
Highly degraded Estuaries which have had major impacts on core estuarine habitats through infilling, canalisation and pollution, substantially reduced or no estuarine support habitats and major loss of key estuarine processes.
Table1.Rankingofesturinestatebasedonfunctionngandhealthofthesystem(adaptedfromForbes&Demetriades(2008))
Mhlungwa(Hibberdene)
Kongweni(Margate)
Mtamvuna(PortEdward)
Studysites
Figure 1. Map of sites chosen for study
HibberdeneHibberdene(MhlungwaEstuary)
Margate(KongweniEstuarywithWWTP)
PortEdward(UmtamvunaEstuary)
Hibberdene(MhlungwaEstuary)
Margate(KongweniEstuarywithWWTP)
PortEdward(UmtamvunaEstuary)
Sampling
Mouth:POMDINδ15N(POM)Chla
100m
200m
1000m
2000m
δ15NofMacroalgae
Figure 2. sampling plan for each site
600m
Nutrientanalysis� FilteredsampleswereanalysedfornitrateandphosphateusingSKALARSAN++nutrientanalyser
POM� Filtratecollectedonpre-combustedGFFfilterswereusedforPOM
� Isotopeanalysis
Macroalgae� JaniaintermediaandHypneaspicifera
www.mpcer.nau.eduTakenby:ShivaneePillay
Sta)s)calanalyses� AnalysisofCovariance(ANCOVA).� ANOVA
ResultsEstuary
Figure2LevelofnutrientpollutionineachoftheestuariesinHibberdene(Mhlungwa),Margate(Kongweni)andPortEdward(Umtamvuna)
RockyShores
Figure5.2LevelofnitrogenpollutiondistributedacrossstationsinHibberdene(Mhlungwa),Margate(Kongweni)andPortEdward(Umtamvuna)
Overalloutcomesandrecommenda)ons� Nitrogenpollutionisevidentamongthesitesconcerned� Itissuggestedthatboththeestuaryandrockyshorehabitatbemonitoredtoelucidateotherfactorsnotconsideredhere.
� TheconditionofsiteschosenforthisstudyclearlyindicateaneedformitigationofnutrientpollutioninestuariesandagreaterneedfordevelopmentofWWTWalongthecoastofKZN.
� AsurveyoftheKZNcoastlinewillgiveanindicationofthosesimilarlyimpactedandinneedofmitigation
Thankyou
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