Lake Washington. |
Contrastingly, a great deal of longer-term research demonstrates that once a threshold is crossed, a 'tipping point', which pushes the system into the low biodiversity, turbid state, there are many factors which prevent recovery to clear water (Kumagai and Vincent, 2003). Occasionally this is due to an insufficient reduction in nutrient levels, i.e. failure to stop agricultural run-off or sewage from reaching the water body.
However, usually systems appear to recover in tests such as those above, but additional factors later cause a move back to turbid water, even without the addition of more nutrients by humans. For example, leaving piscivorous fish in a recovering water body can cause (smaller) planktivorous fish populations to remain low, leading to decreased predation of algae and returning algal blooms (Kumagai and Vincent, 2003). Fish such as pike (often introduced into lakes by humans) also have to be removed for efficient recovery, as these disturb sediments, increasing turbidity and releasing stored nutrients, making it more difficult for plant communities to recover (Kumagai and Vincent, 2003).
Additionally, Sondergaard et al., 1996, demonstrated that grazing waterfowl (such as swans) can prevent lakes recovering after eutrophication. Birds were found to suppress the regrowth of plants in these lakes (required for the return from a turbid water state), negatively impacting water quality; many hypertrophic areas therefore also require enclosures protecting them from grazing. Gulati, 1995, notes that many lakes have returned to a turbid state as recovery has only focused on reducing the amount of nutrients entering the water; biomanipulation such as the above is generally found to be necessary if water bodies are to improve after eutrophication. A classic case of this is the Norfolk Broads (such as Barton Broad), which has suffered chronic eutrophication, and required huge amounts of additional aid in the form of biomanipulation to even recover small areas.
Because so many factors are involved in water body recovery, truly reversing eutrophication becomes basically unfeasible - these all need to be continually maintained, and how can we act on all these issues with limited monetary resources?
hi
ReplyDeletei was just reading your post and you suggest that removing piscivorous can reduce turbidity of freshwater systems. however could leaving the piscivorous fish in the water, or in fact increasing their population size also help reduce the impacts of eutrophication? this could increase predation on the planktivorous and consequently the reduce predation on zooplankton, this would then lead to higher populations of these algal grazers such as snails, reducing the algal blooms which are characteristic of eutrophic lakes.
thanks
Georgina
Hi,
DeleteWhat I wrote was very much generalised, and eutrophication is a topic that in reality cannot often be handled in a generalised manner. Removal of piscivorous fish can be extremely important in lake recovery if these fish prey on smaller fish that then eat the phytoplankton of algal blooms.
However, if these smaller fish in fact prey on the zooplankton (which in turn eat the phytoplankton), then increasing the number of larger fish which prey on these could aid recovery as you say.
As I said, it very much depends on the specifics of the system in which the experiment is carried out - another reason why system recovery following eutrophication is extremely difficult and resource-intensive.
Thanks for the comment,
Harriet