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S. Pillay1;3, Dr. A. J. Smit2, Dr D. Robertson-Andersson1;3
1UKZN
2UWC
3MACE Lab
Introduction
Main Aim
The aim of this study was to investigate the level and extent of N
pollution to the south coast of KZN
Objectives
The specific objectives were:
 (1) To determine if each estuary chosen for this study is eutrophic and
comparisons made with the current known health status
 (2) To determine the effect of season on nitrogen pollution in rocky
shores during the closed and open phase of the estuary
 (3) To determine if the level of nitrogen pollution changes with
increasing distance away from the estuary.
Hypotheses
It was hypothesised that :
 (1) There is a difference in N pollution among the three
sites (Hibberdene, Margate and Port Edward).
 (2) Rocky shore habitats are supplemented by
nutrients from estuarine sources
Study design
Choosing estuaries
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.
Table 1. Ranking of esturine state based on functionng and health of the system (adapted from Forbes & Demetriades
(2008))
Mhlungwa
(Hibberdene)
Kongweni
(Margate)
Mtamvuna
(Port Edward)
Study sites
Figure 1. Map of sites chosen for study
HibberdeneHibberdene
(Mhlungwa Estuary)
Margate
(Kongweni Estuary with WWTP)
Port Edward (Umtamvuna Estuary)
Hibberdene
(Mhlungwa Estuary)
Margate
(Kongweni Estuary with WWTP)
Port Edward (Umtamvuna Estuary)
Sampling
Mouth:
POM
DIN
δ15N (POM)
Chl a
100 m
200 m
1000 m
2000 m
δ15N of
Macroalgae
Figure 2. sampling plan for each site
600 m
Nutrient analysis
 Filtered samples were analysed for nitrate and
phosphate using SKALAR SAN ++ nutrient analyser
POM
 Filtrate collected on pre-combusted GFF filters were
used for POM
 Isotope analysis
Macroalgae
 Jania intermedia and Hypnea spicifera
www.mpcer.nau.eduTaken by: Shivanee Pillay
Statistical analyses
 Analysis of Covariance (ANCOVA).
 ANOVA
Results
Estuary
Figure 2 Level of nutrient pollution in each of the estuaries in Hibberdene (Mhlungwa),
Margate (Kongweni) and Port Edward (Umtamvuna)
Rocky Shores
Figure 5. 2 Level of nitrogen pollution distributed across stations in Hibberdene
(Mhlungwa), Margate (Kongweni) and Port Edward (Umtamvuna)
Overall outcomes and
recommendations
 Nitrogen pollution is evident among the sites concerned
 It is suggested that both the estuary and rocky shore
habitat be monitored to elucidate other factors not
considered here.
 The condition of sites chosen for this study clearly indicate
a need for mitigation of nutrient pollution in estuaries and
a greater need for development of WWTW along the coast
of KZN.
 A survey of the KZN coastline will give an indication of
those similarly impacted and in need of mitigation
Thank you
References Bannon RO, Roman CT (2008) Using stable isotopes to monitor anthropogenic nitrogen inputs to estuaries. Ecological Applications 18:22–30
 Burrows EM (1971) Assessment of pollution effects by the use of algae. Proceedings of the Royal Society 177:295-306
 Carter R, Bell J, Breetzke T (2007) Cumulative environmental effects of land-derived wastes discharged to sea off the KwaZulu-Natal coast. In:
5th Western Indian Ocean Marine Science Association Scientific Symposium; Science, Policy and Management pressures and responses in
the Western Indian Ocean region; Book of Abstracts
 Cohen RA, Fong P (2005) Experimental evidence supports the use of d15N content of the opportunistic green macroalga enteromorpha
intestinalis (chlorophyta) to determine nitogen sources to estuaries. Journal of Phycology 41:287-293
 Costanzo SD, O'Donohue MJ, Dennison WC, Lonergan NR, Thomas M (2001) A new appraoch for detecting and mapping sewage impacts.
Marine Pollution Bulletin 42:149-156
 Crowe TP, Thompson RC, Bray S, Hawkins SJ (2000) Impacts of anthropogenic stress on rocky intertidal communities. Journal of Aquatic
Ecosystem Stress and Recovery 7: 273-297
 Forbes AT, Demetriades NT (2008) Estuaries of Durban, KwaZulu-Natal, South Africa 2009 report.
 Gartner A, Lavery P, Smit AJ (2002) Use of δ15N signatures of different functional forms of macroalgae and filter feeders to reveal temporal
and spatial patterns in sewage dispersal. Marine Ecology Progress Series 235:63-73
 Gorman D, Russell BD, Connell SD (2009) Land-to-sea connectivity: linking human-derived terrestrial subsidies to subtidal habitat change
on open rocky coasts. Ecological Applications 19:1114–1126
 Islam MS, Tanaka M (2004) Impacts of pollution on coastal and marine ecosystems including coastal and marine fisheries and approach for
management: a review and synthesis. Marine Pollution Bulletin 48:624–649
 Littler MM, Littler DS (1980) The evolution of thallus form and survival strategies in benthic marine macroalgae: Field and laboratory tests of
a functional form. The American Naturalist 116:25-44
 Lombard DAT, Strauss MT, Harris DJ, Sink DK, Attwood DC, Hutchings DL (2004) Marine component. In: South African national spatial
biodiversity assessment 2004 technical report, Book 4. SANBI
 Nahman A, Rigby D (2008) Valuing blue flag status and estuarine water quality in Margate, South Africa. South African Journal of Economics
76:721-737
 Oviatt CA, Quinn JC, Maughan JT, Ellis T, Sullivan BK, Gearing JN, Gearing PJ, Hunt CD, Sampou PA, Latimer JS (1987) Fate and effects of
sewage sludge in the coastal marine environments: a mesocosm experiment. Marine Ecology Progress Series 41:187-203
 Peterson BJ, Fry B (1987) Stable Isotopes in Ecosystem Studies. Annual Review of Ecology and Systematics 18:293-320
 Sigman DM, Altabet MA, Michener R, McCorkle DC, Fry B, Holmes RM (1997) Natural abundance-level measurement of the nitrogen
isotopic composition of oceanic nitrate: an adaptation of the ammonia diffusion method. Marine Chemistry 57
 Smith SSA (1996) The effects of domestic sewage effluent on marine communities at Coifs Harbour, New South Wales, Australia. Marine
Pollution Bulletin 33:309-316
 Underwood AJ (2000) Experimental ecology of rocky intertidal habitats: what are we learning? Journal of Experimental Marine Biology and
Ecology 250:51-76
 Vitousek PM, Aber JD, Howarth RW, Likens GE, Matson PA, Schindler DW, Schlesinger WH, Tilman DG (1997) Human alteration of the
global nitrogen cycle: Sources and consequences. Ecological Applications 7:737-750

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Linking Nitrogen Pollution in Estuaries to Rocky Shores: A stable Isotope Approach

  • 1. S. Pillay1;3, Dr. A. J. Smit2, Dr D. Robertson-Andersson1;3 1UKZN 2UWC 3MACE Lab
  • 3. Main Aim The aim of this study was to investigate the level and extent of N pollution to the south coast of KZN
  • 4. Objectives The specific objectives were:  (1) To determine if each estuary chosen for this study is eutrophic and comparisons made with the current known health status  (2) To determine the effect of season on nitrogen pollution in rocky shores during the closed and open phase of the estuary  (3) To determine if the level of nitrogen pollution changes with increasing distance away from the estuary.
  • 5. Hypotheses It was hypothesised that :  (1) There is a difference in N pollution among the three sites (Hibberdene, Margate and Port Edward).  (2) Rocky shore habitats are supplemented by nutrients from estuarine sources
  • 7. 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. Table 1. Ranking of esturine state based on functionng and health of the system (adapted from Forbes & Demetriades (2008)) Mhlungwa (Hibberdene) Kongweni (Margate) Mtamvuna (Port Edward)
  • 8. Study sites Figure 1. Map of sites chosen for study HibberdeneHibberdene (Mhlungwa Estuary) Margate (Kongweni Estuary with WWTP) Port Edward (Umtamvuna Estuary)
  • 9. Hibberdene (Mhlungwa Estuary) Margate (Kongweni Estuary with WWTP) Port Edward (Umtamvuna Estuary)
  • 10. Sampling Mouth: POM DIN δ15N (POM) Chl a 100 m 200 m 1000 m 2000 m δ15N of Macroalgae Figure 2. sampling plan for each site 600 m
  • 11. Nutrient analysis  Filtered samples were analysed for nitrate and phosphate using SKALAR SAN ++ nutrient analyser POM  Filtrate collected on pre-combusted GFF filters were used for POM  Isotope analysis
  • 12. Macroalgae  Jania intermedia and Hypnea spicifera www.mpcer.nau.eduTaken by: Shivanee Pillay
  • 13. Statistical analyses  Analysis of Covariance (ANCOVA).  ANOVA
  • 14. Results Estuary Figure 2 Level of nutrient pollution in each of the estuaries in Hibberdene (Mhlungwa), Margate (Kongweni) and Port Edward (Umtamvuna)
  • 15. Rocky Shores Figure 5. 2 Level of nitrogen pollution distributed across stations in Hibberdene (Mhlungwa), Margate (Kongweni) and Port Edward (Umtamvuna)
  • 16. Overall outcomes and recommendations  Nitrogen pollution is evident among the sites concerned  It is suggested that both the estuary and rocky shore habitat be monitored to elucidate other factors not considered here.  The condition of sites chosen for this study clearly indicate a need for mitigation of nutrient pollution in estuaries and a greater need for development of WWTW along the coast of KZN.  A survey of the KZN coastline will give an indication of those similarly impacted and in need of mitigation
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