Difference between revisions of "Eutrophication in coastal environments"
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| − | '''[[Eutrophication]]''' is the enrichment of water as a result of an increase in nutrients, which can have a negative impact on the marine and coastal environment. The negative effects of [[eutrophication]] on marine [[ | + | '''[[Eutrophication]]''' is the enrichment of water as a result of an increase in nutrients, which can have a negative impact on the marine and coastal environment. The negative effects of [[eutrophication]] on marine [[ecosystem]]s includes: algal blooms, increased growth of macroalgae, increased sedimentation and oxygen consumption, oxygen depletion in the bottom water and sometimes the death of [[benthic]] animals and fish. Coastal European areas in particular the Baltic Sea provides an indication as to the negative affects that [[eutrophication]] can have including: the presence of blue-green algae which is potentially harmful to humans as well as the presence of large mats of drifting algae that get deposited along the shorelines and decay. In order to reduce the negative effects of [[eutrophication]] nutrient inputs need to be reduced and an integrated management strategy needs to be employed. |
==Eutrophication in coastal environments== | ==Eutrophication in coastal environments== | ||
| − | [[Eutrophication]] involves the enrichment of water by excess [[ | + | [[Eutrophication]] involves the enrichment of water by excess [[nutrient]]s. It can cause serious problems in the coastal zone through disturbance of ecological balances and fisheries, and through interference with recreational activities and quality of life. [[Eutrophication]] is the result of an [[anthropogenic|anthropogenically]] induced alteration of the global nitrogen cycle, and just like [[climate change]], should be regarded as a "global change". [[Eutrophication]] is usually treated scientifically and in terms of management as a local and regional phenomenon. Coastal regions throughout the world and Europe are affected by [[eutrophication]]. |
==What is eutrophication about?== | ==What is eutrophication about?== | ||
[[image:Baltic.jpg|thumb|right|Fig. 1. Cyanobacteria bloom, Western Baltic, 1997]] | [[image:Baltic.jpg|thumb|right|Fig. 1. Cyanobacteria bloom, Western Baltic, 1997]] | ||
| − | *It’s about '''increased productivity''' (conversion of light and carbon dioxide into living organic matter – a process that is limited by ''[[nitrogen]]'' and/or ''[[phosphorus]]'') and unacceptable ecological effects as [[algal | + | *It’s about '''increased productivity''' (conversion of light and carbon dioxide into living organic matter – a process that is limited by ''[[nitrogen]]'' and/or ''[[phosphorus]]'') and unacceptable ecological effects as [[algal bloom]]s and oxygen depletion, kills off benthic animals and fish |
*It’s caused by '''increased inputs''' of [[nutrients]] from point sources, activities in the upstream catchment (''e.g.'' losses from agriculture) and atmospheric deposition. | *It’s caused by '''increased inputs''' of [[nutrients]] from point sources, activities in the upstream catchment (''e.g.'' losses from agriculture) and atmospheric deposition. | ||
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But is “''[[eutrophication]]''” good? | But is “''[[eutrophication]]''” good? | ||
*In general: NO … it is actually ”bad” … | *In general: NO … it is actually ”bad” … | ||
| − | *Too many [[ | + | *Too many [[nutrient]]s in the wrong places may cause problems and result in changes in structure, function and stability of the marine [[ecosystem]]s. |
*[[Eutrophication]] is ”too much of a good thing” | *[[Eutrophication]] is ”too much of a good thing” | ||
==Effects of Eutrophication== | ==Effects of Eutrophication== | ||
| − | The different processes and effects of coastal [[eutrophication]] are well documented<ref>Cloern, J. (2001) Our evolving conceptual model of the coastal eutrophication problem. Mar. Ecol. Prog. Ser., 210, 223–253.[ISI]</ref> <ref>Conley, D. J., Markager, S., Andersen, J. et al. (2002) Coastal eutrophication and the Danish National Aquatic Monitoring and Assessment Program. Estuaries, 25, 706–719.[Medline]</ref> <ref>Rönnberg, C. and Bonsdorff, E. (2004) Baltic Sea eutrophication: area-specific ecological consequences. Hydrobiologia, 514, 227–241.[CrossRef][ISI]</ref> and it has been considered as one of the biggest threats to marine [[ | + | The different processes and effects of coastal [[eutrophication]] are well documented<ref>Cloern, J. (2001) Our evolving conceptual model of the coastal eutrophication problem. Mar. Ecol. Prog. Ser., 210, 223–253.[ISI]</ref> <ref>Conley, D. J., Markager, S., Andersen, J. et al. (2002) Coastal eutrophication and the Danish National Aquatic Monitoring and Assessment Program. Estuaries, 25, 706–719.[Medline]</ref> <ref>Rönnberg, C. and Bonsdorff, E. (2004) Baltic Sea eutrophication: area-specific ecological consequences. Hydrobiologia, 514, 227–241.[CrossRef][ISI]</ref> and it has been considered as one of the biggest threats to marine [[ecosystem]] health for decades<ref>Ryther and Dunstan, 1971</ref> <ref>Nixon, S. W. (1995) Coastal marine eutrophication: a definition, social causes, and future concerns. Ophelia, 41, 199–219.[ISI]</ref> <ref>Bachmann, R. W., Cloern, J. E., Heckey, R. E. et al. (eds) (2006) Eutrophication of freshwater and marine ecosystems. Limnol. Oceanogr., 51 (1, part 2), 351–800.</ref>. |
[[Image:eutrophicationflow.jpg|600px|thumb|centre|Fig. 3. Eutrophication flow diagram. Source: HELCOM, 2006 <ref name="HELCOM">HELCOM, (2006) Andersen, J (DHI) and Pawlak, J (MEC), Nutrients and Eutrophication in the Baltic Sea – Effects, Causes, Solutions. Baltic Sea Parliamentary Conference.[http://sea.helcom.fi/dps/docs/documents/Monitoring%20and%20Assessment%20Group%20(MONAS)/EUTRO-PRO/EUTRO-PRO%203,%202006/BSPC%20Nutrients%20and%20Eutrophication%20in%20the%20BS.pdf]</ref> | [[Image:eutrophicationflow.jpg|600px|thumb|centre|Fig. 3. Eutrophication flow diagram. Source: HELCOM, 2006 <ref name="HELCOM">HELCOM, (2006) Andersen, J (DHI) and Pawlak, J (MEC), Nutrients and Eutrophication in the Baltic Sea – Effects, Causes, Solutions. Baltic Sea Parliamentary Conference.[http://sea.helcom.fi/dps/docs/documents/Monitoring%20and%20Assessment%20Group%20(MONAS)/EUTRO-PRO/EUTRO-PRO%203,%202006/BSPC%20Nutrients%20and%20Eutrophication%20in%20the%20BS.pdf]</ref> | ||
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| − | Effects of [[eutrophication]] on marine [[ | + | Effects of [[eutrophication]] on marine [[ecosystem]]s are well known<ref name="HELCOM"/>: |
| − | *algal | + | *[[algal bloom]]s resulting in green water |
*reduced depth distribution of submerged aquatic vegetation | *reduced depth distribution of submerged aquatic vegetation | ||
*increased growth of nuisance macroalgae | *increased growth of nuisance macroalgae | ||
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===General effects=== | ===General effects=== | ||
| − | Major effects of [[eutrophication]] include structure and function changes in the entire marine [[ | + | Major effects of [[eutrophication]] include structure and function changes in the entire marine [[ecosystem]] and a reduction in stability. The following are responses to increased nutrient inputs<ref name="HELCOM"/>: |
#Corresponding increase in nutrient concentrations | #Corresponding increase in nutrient concentrations | ||
#Change in ratio between dissolved [[nitrogen]] and [[phosphorus]] in the water: ''DIN:DIP'' ratio. Optimal is 16:1 – called the ''[[Redfield ratio]]''. Significantly lower ratio causes potential [[nitrogen]] limitation; while a higher ratio leads to [[phosphorus]] limitation of [[phytoplankton]] [[primary production]]. | #Change in ratio between dissolved [[nitrogen]] and [[phosphorus]] in the water: ''DIN:DIP'' ratio. Optimal is 16:1 – called the ''[[Redfield ratio]]''. Significantly lower ratio causes potential [[nitrogen]] limitation; while a higher ratio leads to [[phosphorus]] limitation of [[phytoplankton]] [[primary production]]. | ||
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''[[Primary production]]'' is usually limited by availability of light and nutrients. | ''[[Primary production]]'' is usually limited by availability of light and nutrients. | ||
| − | Nutrient enrichment increase [[phytoplankton]] [[primary production]], which increases biomass, which decreases light penetration through water column. Light penetration is measured by [[Secchi depth]] - a decreased [[Secchi depth]] can reduce colonization depth of macroalgae and [[ | + | Nutrient enrichment increase [[phytoplankton]] [[primary production]], which increases biomass, which decreases light penetration through water column. Light penetration is measured by [[Secchi depth]] - a decreased [[Secchi depth]] can reduce colonization depth of macroalgae and [[seagrass]]es. |
| − | Responses to nutrient enrichment ([[pelagic]] [[ | + | Responses to nutrient enrichment ([[pelagic]] [[ecosystem]]s) involve a gradual change towards<ref name="HELCOM"/>: |
#Increased [[plankton|planktonic]] [[primary production]] compared to benthic production | #Increased [[plankton|planktonic]] [[primary production]] compared to benthic production | ||
#Dominance of microbial food webs over linear [[plankton|planktonic]] food chains | #Dominance of microbial food webs over linear [[plankton|planktonic]] food chains | ||
#Dominance of non-siliceous [[phytoplankton]] species over diatom species | #Dominance of non-siliceous [[phytoplankton]] species over diatom species | ||
| − | #Dominance of gelatinous [[zooplankton]] (jellyfish) over [[crustacea | + | #Dominance of gelatinous [[zooplankton]] (jellyfish) over [[crustacea]]n [[zooplankton]] |
Finally, [[eutrophication]] issues<ref name="HELCOM"/> are often divided into three groups: | Finally, [[eutrophication]] issues<ref name="HELCOM"/> are often divided into three groups: | ||
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#increased growth of filamentous and short lived nuisance macroalgae at the cost of long lived species can lead to a change in structure of macroalgae communities with reduced diversity. | #increased growth of filamentous and short lived nuisance macroalgae at the cost of long lived species can lead to a change in structure of macroalgae communities with reduced diversity. | ||
Additionally, | Additionally, | ||
| − | *[[ | + | *[[Seagrass]] meadows and perennial macroalgae are important nursery areas for coastal fish populations. |
*Short-lived (annual) nuisance macroalgae are favoured by large nutrient inputs. | *Short-lived (annual) nuisance macroalgae are favoured by large nutrient inputs. | ||
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*Lethally low oxygen concentrations depend on the species. Fish and crustaceans have higher oxygen requirements; other speices have lower requirements. | *Lethally low oxygen concentrations depend on the species. Fish and crustaceans have higher oxygen requirements; other speices have lower requirements. | ||
*[[hypoxia|Hypoxic]] and anoxic (no oxygen) conditions may results in formation and release of hydrogen sulphide (H<sub>2</sub>S), which is lethal to organisms. | *[[hypoxia|Hypoxic]] and anoxic (no oxygen) conditions may results in formation and release of hydrogen sulphide (H<sub>2</sub>S), which is lethal to organisms. | ||
| − | *Anoxic periods cause the release of phophorus from sediments - dissolved inorganic phosphorus (DIP), and ammonium is released under [[hypoxia|hypoxic]] conditions. DIP and ammonium in water column can enhance [[algal | + | *Anoxic periods cause the release of phophorus from sediments - dissolved inorganic phosphorus (DIP), and ammonium is released under [[hypoxia|hypoxic]] conditions. DIP and ammonium in water column can enhance [[algal bloom]]s. |
*The predicted effect of global warming is to increase [[hypoxia]] with increased temperature. A 4 degree temperature increase is projected to results in a doubling of [[hypoxia]] in some parts of North Sea. | *The predicted effect of global warming is to increase [[hypoxia]] with increased temperature. A 4 degree temperature increase is projected to results in a doubling of [[hypoxia]] in some parts of North Sea. | ||
*An example of the effect: Eelgrass responds to low oxygen concentrations, and dies off under these conditions (often in combination with high temperatures) | *An example of the effect: Eelgrass responds to low oxygen concentrations, and dies off under these conditions (often in combination with high temperatures) | ||
| Line 112: | Line 112: | ||
Within Europe, regional seas such as the Baltic and Mediterranean Seas are currently adversely affected by [[eutrophication]], with [[climate change]] expected to intensify these adverse impacts. As well as monitoring fresh water impacts on coastal areas, it will be important to monitor impacts between seas such as the Mediterranean and Black Seas. For example, the Black Sea is strongly eutrophic, and enters the Mediterranean Sea at the North Aegean near the borders of Greece and Turkey. | Within Europe, regional seas such as the Baltic and Mediterranean Seas are currently adversely affected by [[eutrophication]], with [[climate change]] expected to intensify these adverse impacts. As well as monitoring fresh water impacts on coastal areas, it will be important to monitor impacts between seas such as the Mediterranean and Black Seas. For example, the Black Sea is strongly eutrophic, and enters the Mediterranean Sea at the North Aegean near the borders of Greece and Turkey. | ||
| − | [[Eutrophication]] seriously affects the Baltic sea marine environment, resulting in [[algal | + | [[Eutrophication]] seriously affects the Baltic sea marine environment, resulting in [[algal bloom]]s, reduced water clarity, oxygen reduction and death of bottom animals. The causes behind this are well known<ref name="HELCOM"/>: discharges, losses and emissions of nitrogen and phosphorus to the aquatic environment. Reductions of discharges from municipal wastewater treatment plants and industries have been the focus for many years as have losses and emissions of nitrogen compounds from agriculture and traffic. |
More global approaches were considered in meetings such as the [http://eutro2006.dhi.dk/ International Symposium on Research and Management of Eutrophication in Coastal Ecosystems] from June 20 to 23, 2006 in Nyborg, Denmark. This meeting included a keynote speaker, a working seminar, produced some outcomes,and led to the creation of an European group to address the issue of [[climate change]] and [[eutrophication]]. | More global approaches were considered in meetings such as the [http://eutro2006.dhi.dk/ International Symposium on Research and Management of Eutrophication in Coastal Ecosystems] from June 20 to 23, 2006 in Nyborg, Denmark. This meeting included a keynote speaker, a working seminar, produced some outcomes,and led to the creation of an European group to address the issue of [[climate change]] and [[eutrophication]]. | ||
| Line 137: | Line 137: | ||
====Aspects of Eutrophication problem in the Baltic sea<ref name="HELCOM"/>==== | ====Aspects of Eutrophication problem in the Baltic sea<ref name="HELCOM"/>==== | ||
| − | *Excessive [[phytoplankton]] blooms are a major problem – especially of blue-green algae. There are commonly summertime [[algal | + | *Excessive [[phytoplankton]] blooms are a major problem – especially of blue-green algae. There are commonly summertime [[algal bloom]]s in most parts of Gulf of Finland, Gulf of Riga, the Baltic Proper and south-western parts of Baltic Sea |
Problems caused: | Problems caused: | ||
*bathing people can hardly see their feet | *bathing people can hardly see their feet | ||
Revision as of 13:38, 21 September 2008
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Waiting for author to confirm changes
Eutrophication is the enrichment of water as a result of an increase in nutrients, which can have a negative impact on the marine and coastal environment. The negative effects of eutrophication on marine ecosystems includes: algal blooms, increased growth of macroalgae, increased sedimentation and oxygen consumption, oxygen depletion in the bottom water and sometimes the death of benthic animals and fish. Coastal European areas in particular the Baltic Sea provides an indication as to the negative affects that eutrophication can have including: the presence of blue-green algae which is potentially harmful to humans as well as the presence of large mats of drifting algae that get deposited along the shorelines and decay. In order to reduce the negative effects of eutrophication nutrient inputs need to be reduced and an integrated management strategy needs to be employed.
Contents
Eutrophication in coastal environments
Eutrophication involves the enrichment of water by excess nutrients. It can cause serious problems in the coastal zone through disturbance of ecological balances and fisheries, and through interference with recreational activities and quality of life. Eutrophication is the result of an anthropogenically induced alteration of the global nitrogen cycle, and just like climate change, should be regarded as a "global change". Eutrophication is usually treated scientifically and in terms of management as a local and regional phenomenon. Coastal regions throughout the world and Europe are affected by eutrophication.
What is eutrophication about?
- It’s about increased productivity (conversion of light and carbon dioxide into living organic matter – a process that is limited by nitrogen and/or phosphorus) and unacceptable ecological effects as algal blooms and oxygen depletion, kills off benthic animals and fish
- It’s caused by increased inputs of nutrients from point sources, activities in the upstream catchment (e.g. losses from agriculture) and atmospheric deposition.
What are we really talking about?
- Eutrophication
- “eu” = “well” or “good”
- “trope” = “nourishment”
But is “eutrophication” good?
- In general: NO … it is actually ”bad” …
- Too many nutrients in the wrong places may cause problems and result in changes in structure, function and stability of the marine ecosystems.
- Eutrophication is ”too much of a good thing”
Effects of Eutrophication
The different processes and effects of coastal eutrophication are well documented[1] [2] [3] and it has been considered as one of the biggest threats to marine ecosystem health for decades[4] [5] [6].
Effects of eutrophication on marine ecosystems are well known[7]:
- algal blooms resulting in green water
- reduced depth distribution of submerged aquatic vegetation
- increased growth of nuisance macroalgae
- increased sedimentation, increased oxygen consumption
- oxygen depletion in bottom water, and
- sometimes dead benthic animals and fish.
General effects
Major effects of eutrophication include structure and function changes in the entire marine ecosystem and a reduction in stability. The following are responses to increased nutrient inputs[7]:
- Corresponding increase in nutrient concentrations
- Change in ratio between dissolved nitrogen and phosphorus in the water: DIN:DIP ratio. Optimal is 16:1 – called the Redfield ratio. Significantly lower ratio causes potential nitrogen limitation; while a higher ratio leads to phosphorus limitation of phytoplankton primary production.
Primary production is usually limited by availability of light and nutrients.
Nutrient enrichment increase phytoplankton primary production, which increases biomass, which decreases light penetration through water column. Light penetration is measured by Secchi depth - a decreased Secchi depth can reduce colonization depth of macroalgae and seagrasses.
Responses to nutrient enrichment (pelagic ecosystems) involve a gradual change towards[7]:
- Increased planktonic primary production compared to benthic production
- Dominance of microbial food webs over linear planktonic food chains
- Dominance of non-siliceous phytoplankton species over diatom species
- Dominance of gelatinous zooplankton (jellyfish) over crustacean zooplankton
Finally, eutrophication issues[7] are often divided into three groups:
- Causative factors: inputs, elevated nutrient concentrations, Redfield ratio changes
- Direct effects: primary producers, namely phytoplankton and submerged aquatic vegetation
- Indirect effects (secondary effects): related to zooplankton, fish and ínvertebrate benthic fauna (animals living on seafloor).
Primary and Secondary Effects
Some important primary and secondary effects are discussed in the sections below.
Phytoplankton
Phytoplankton are at base of pelagic food webs in aquatic systems, have generation times from less that a few days, respond rapidly to nutrient concentration changes, and are often quantified in terms of:
- Primary production
- Biomass (chlorophyll-a concentration, or carbon biomass)
- Bloom frequency
Submerged aquatic vegetation
Submerged aquatic vegetation are affected by eutrophication through[7]:
- Reduced light penetration and shadowing effects from phytoplankton can reduce the depth distribution, biomass, composition and species diversity; and
- increased growth of filamentous and short lived nuisance macroalgae at the cost of long lived species can lead to a change in structure of macroalgae communities with reduced diversity.
Additionally,
- Seagrass meadows and perennial macroalgae are important nursery areas for coastal fish populations.
- Short-lived (annual) nuisance macroalgae are favoured by large nutrient inputs.
Oxygen depletion[7]
Oxygen depletion, or hypoxia, is a common effect of eutrophication in bottom waters. This effect may be episodic, occuring annually (most common in summer/autumn), persistent, or periodic in the coastal zone.
- Lethally low oxygen concentrations depend on the species. Fish and crustaceans have higher oxygen requirements; other speices have lower requirements.
- Hypoxic and anoxic (no oxygen) conditions may results in formation and release of hydrogen sulphide (H2S), which is lethal to organisms.
- Anoxic periods cause the release of phophorus from sediments - dissolved inorganic phosphorus (DIP), and ammonium is released under hypoxic conditions. DIP and ammonium in water column can enhance algal blooms.
- The predicted effect of global warming is to increase hypoxia with increased temperature. A 4 degree temperature increase is projected to results in a doubling of hypoxia in some parts of North Sea.
- An example of the effect: Eelgrass responds to low oxygen concentrations, and dies off under these conditions (often in combination with high temperatures)
Invertebrate benthic fauna[7]
Invertebrate benthic fauna can cope with oxygen depletion to varying degrees (days – month). If O2 drops below zero and H2S is released all organisms are killed immediately. Mobile benthic invertebrates in sediment move to surface when O2 decreases - there are increased catches of fish and crustaceans during these times. It is difficult to predict when animals will return after eutrophication events. The area affected plays a factor: small areas are recolonised and re-established more quickly than larger areas.
Climate change
- Seas are important in element cycling – carbon and nitrogen cycle; phosphorus and silicate cycle
- Ocean still takes up more carbon than it releases – depositing some in sediments
Solutions
Nutrient inputs must be reduced to levels that do not put at risk target values for mitigation of eutrophication. Integrated management strategies should enable characterization of all pressures on water bodies in order to develop a coherent approach to deal with the pressures in a cost effective manner[7].
European Coastal Areas
Eutrophication is the result of an anthropogenically induced alteration of the global nitrogen cycle, and just like climate change, should be regarded as a "global change". Eutrophication is usually treated scientifically and for management as a local and regional phenomenon. Coastal regions throughout the world and Europe are affected by eutrophication.
Within Europe, regional seas such as the Baltic and Mediterranean Seas are currently adversely affected by eutrophication, with climate change expected to intensify these adverse impacts. As well as monitoring fresh water impacts on coastal areas, it will be important to monitor impacts between seas such as the Mediterranean and Black Seas. For example, the Black Sea is strongly eutrophic, and enters the Mediterranean Sea at the North Aegean near the borders of Greece and Turkey.
More global approaches were considered in meetings such as the International Symposium on Research and Management of Eutrophication in Coastal Ecosystems from June 20 to 23, 2006 in Nyborg, Denmark. This meeting included a keynote speaker, a working seminar, produced some outcomes,and led to the creation of an European group to address the issue of climate change and eutrophication.
The main source of nitrogen to European coastal waters is agricultural runoff discharged into the sea via rivers, identified as originating from sources of ammonia evaporation in animal husbandry and partly from fossil fuel combustion in traffic, industry and households[8]. For phosphorus the major sources are treated and untreated discharges to the sea from households and industry as well as soil erosion[8].
Within Europe, regional seas such as the Baltic and Mediterranean Seas are currently adversely affected by eutrophication, with climate change expected to intensify these adverse impacts. As well as monitoring fresh water impacts on coastal areas, it will be important to monitor impacts between seas such as the Mediterranean and Black Seas. For example, the Black Sea is strongly eutrophic, and enters the Mediterranean Sea at the North Aegean near the borders of Greece and Turkey.
Eutrophication seriously affects the Baltic sea marine environment, resulting in algal blooms, reduced water clarity, oxygen reduction and death of bottom animals. The causes behind this are well known[7]: discharges, losses and emissions of nitrogen and phosphorus to the aquatic environment. Reductions of discharges from municipal wastewater treatment plants and industries have been the focus for many years as have losses and emissions of nitrogen compounds from agriculture and traffic.
More global approaches were considered in meetings such as the International Symposium on Research and Management of Eutrophication in Coastal Ecosystems from June 20 to 23, 2006 in Nyborg, Denmark. This meeting included a keynote speaker, a working seminar, produced some outcomes,and led to the creation of an European group to address the issue of climate change and eutrophication.
Causes in Baltic Sea
Human-mediated nutrient enrichment[7] in the Baltic Sea can be caused by input of nutrients in form of:
- Direct inputs from point sources (sewage treatment plants, industries)
- Atmospheric deposition
- Riverine inputs (from activities in the catchment: eg point sources, agricultural losses, atmospheric deposition, natural background losses (natural erosion and leakage of nutrients from areas without much human activities) and stream, river and lake retention)
Waterborne: Agriculture forestry, scattered dwellings, municipanlities, industries, natural background losses.
Airborne: Nitrogen compounds emitted to atmosphere:
- Nitrogen oxides: road transportation, energy combustion, shipping
- Ammonia emissions: mostly from agriculture.
- Distant sources
The role of agriculture in nitrogen inputs: The main source of nitrogen inputs in Baltic Sea is agricultural discharge via rivers, deriving from:
- Soil cultivation
- Fertiliser use
- Use of manure
- Intensive and uncontrolled agriculture
Aspects of Eutrophication problem in the Baltic sea[7]
- Excessive phytoplankton blooms are a major problem – especially of blue-green algae. There are commonly summertime algal blooms in most parts of Gulf of Finland, Gulf of Riga, the Baltic Proper and south-western parts of Baltic Sea
Problems caused:
- bathing people can hardly see their feet
- blue-green algae potentially toxic to humans and animals
- large mats of drifting algae deposited along shores and decay
Baltic Sea Solutions
The following steps have been suggested[7]
- Establish overall goals and target values
- Implement relevant measures directly linked to fulfillment of these overall goals and targets
- Carry out monitoring
- Conduct assessments
- Evaluate whether the goals and targets have been fulfilled or not
Main drivers:
- European Directives (see links below)
- Decisions and recommendations adopted by HELCOM
- National action plans
EU Directives:
- EC Urban Waster Water Treatment Directive
- EC Nitrates Directive
- EU Water Framework Directive
- Marine Strategy Directive
See also
- Theme 4 - Pollution
- Water quality/pollution
External links
- Baltic Sea Parlimentary Conference
- BERNET: Baltic Eutrophication Regional Network
- BONUS for the future of the Baltic Sea
- European Environment Agency
- HELCOM
- HELCOM Indicator fact sheets:
- MARE Research program on Baltic Sea environmental issues
- National Environment Research Institute (DK) Aquatic page
- Nutrients and Eutrophication in Danish Marine Waters
- OSPAR For the protection of the marine environment of the north-east Atlantic
- The Water Forecast
- Wikipedia: Eutrophication article
- WWF Baltic Ecoregion Programme
References
- Nutrients and Eutrophication in the Baltic Sea - Effects, Causes, Solutions (HELCOM) - main reference for this article
- ↑ Cloern, J. (2001) Our evolving conceptual model of the coastal eutrophication problem. Mar. Ecol. Prog. Ser., 210, 223–253.[ISI]
- ↑ Conley, D. J., Markager, S., Andersen, J. et al. (2002) Coastal eutrophication and the Danish National Aquatic Monitoring and Assessment Program. Estuaries, 25, 706–719.[Medline]
- ↑ Rönnberg, C. and Bonsdorff, E. (2004) Baltic Sea eutrophication: area-specific ecological consequences. Hydrobiologia, 514, 227–241.[CrossRef][ISI]
- ↑ Ryther and Dunstan, 1971
- ↑ Nixon, S. W. (1995) Coastal marine eutrophication: a definition, social causes, and future concerns. Ophelia, 41, 199–219.[ISI]
- ↑ Bachmann, R. W., Cloern, J. E., Heckey, R. E. et al. (eds) (2006) Eutrophication of freshwater and marine ecosystems. Limnol. Oceanogr., 51 (1, part 2), 351–800.
- ↑ 7.00 7.01 7.02 7.03 7.04 7.05 7.06 7.07 7.08 7.09 7.10 7.11 7.12 7.13 HELCOM, (2006) Andersen, J (DHI) and Pawlak, J (MEC), Nutrients and Eutrophication in the Baltic Sea – Effects, Causes, Solutions. Baltic Sea Parliamentary Conference.[1]
- ↑ 8.0 8.1 Ærtebjerg, G. et al., Eutrophication in Europe’s Coastal Waters. Topic Report No 7/2001. European Environment Agency. [2]
Further Reading
The Biology and Ecology of Seagrasses (ed. Brant W. Touchette), 2007. Journal of Experimental Marine Biology and Ecology, Volume 350, Issues 1-2, Pages 1-260 (9 November 2007), . http://www.sciencedirect.com/science/journal/00220981
Please note that others may also have edited the contents of this article.
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