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Advanced
knowledge
Eutrophication
The
phenomenon of eutrophication is particularly associated with lakes
and slow-flowing waters. It is widely, and erroneously, believed
that pollution by plant nutrients and organic matter actually causes
eutrophication. It is more accurate to say that pollution accelerates
what is probably a natural process. To understand the causes and
consequences of eutrophication requires some knowledge of the special
characteristics of lakes.
In
temperate latitudes, most lakes were formed by glaciation. Moving
glaciers gouged out hollows in the earth, and when the ice retreated
these hollows became filled with water from the melting ice. Such
lakes are not. Therefore, geologically ancient phenomena. In modern
times, substantial man-made lakes have become common in many parts
of the world. A lake is a body of water which is very slow-moving.
Some lakes have rivers flowing into or out of them. Even those which
do not, however, are not static; water moves slowly into or out
of the lake via the ground. Because the water moves only very slowly;
some physical and chemical processes occur in lakes which do not
occur in moving waters. Of particular importance are stratification,
and temporal variations in chemical quality of the water.
Stratification
occurs because the lake water is heated by the sun at the surface.
Because warm water is less dense than cooler water, and water is
a poor conductor of heat, during the warmer months of the year an
upper layer of warm water, the epilimnion, becomes established and
sharply delineated from a lower layer of cooler, denser water, the
hypolimnion. Between them is a very narrow zone, the thermocline,
within which the water temperature drops very sharply with only
a slight increase in water depth. Little or no vertical mixing can
take place, the like being effectively divided horizontally into
two distinct layers separated by tile thermocline. Obviously, stratification
cannot occur in very shallow lakes.
Photosynthesis
can only occur in shallow water, where light can penetrate. At the
lake margins, emergent plants and rooted aquatic macrophytes occur,
but as tile depth of the water increases, primary production is
possible only by phyoplankton in the surface waters, within the
epilimnion. During the winter, phyoplankton growth is restricted
by low temperatures and low light intensity. In spring and summer
Increasing temperatures and light intensity stimulate phyoplankton
growth, leading to an increase in population density and the depiction
of nutrients In the water of the epilimnion. Plant growth and reproduction
slow down, and as the plant cells senesce and die, they 1 sink into
the hypolimnion and eventually to the bottom of the lake, where
they begin to decompose. The inorganic nutrients which are the products
of decomposition remain in the hypolimnion, however, as the stratification
prevents vertical mixing of the water and upwards diffusion is slow.
As the autumn approaches, reduced temperatures, light intensity
and limited nutrients accelerate the decline of the phytoplankton
population. In the winter, the epilimnion cools and becomes more
dense. Its water sinks, displacing the hypolimnion which is now
warmer and lighter than the epilimnion. The lake waters become thoroughly
mixed, and nutrients from the hypolimnion are brought to the surface,
bringing about conditions suitable for the start of the next annual
cycle.
Underlying
these annual cycles is a progressive change in the physical and
chemical characteristics of the lake. At its formation, the lake
contains few plant nutrients or dissolved minerals of any kind,
and a negligible quantity of organic matter. With the passage of
time, dissolved minerals including plant nutrients enter the lake
from surface runoff and groundwater infiltration, at a rate which
depends largely upon the climate and the geology of the surrounding
area. As the nutrient levels rise, a flora and fauna becomes established
and develops, contributing an increased content of organic matter
in the lake. Organic matter is also gradually accumulated from outside
the lake, progressively building up a layer of sediment on the lake
bottom. Airborne dust also fills into the take, and the take begins
slowly to fill up, 'the rate at which this happens varies from the
barely detectable up to a few millimetres per year. The gradual
deposition of material oil the floor of the lake basin causes the
like to shrink, new land being formed at its edges. This new land
is colonised by terrestrial plants, and in some lakes it is possible,
by walking away from tile lake's edge, to see clearly the various
stages of development of the terrestrial flora, a classic example
of ecological succession. In areas where these processes have occurred,
for various reasons, at different rates in different lakes, it is
possible to see contemporaneously all the stages of a lake's development
from nutrient-poor, sparsely-populated lakes of low productivity,
through various stages of nutrient enrichment to swamp or marsh
and eventually dry land.
The
term eutrophication is applied to the process whereby the nutrient
levels of lakes increase from oligotrophic (nutrient poor) to eutrophic
(nutrient rich). It appears to be a natural process, although some
authors have argued that it is not inevitable or intrinsically unidirectional.
Since its basic cause is, however, the accumulation of plant nutrients
and organic matter in the lake basin, clearly anthropogenic influences
will accelerate it. The transition from oligotrophic to eutrophic
is accompanied by qualitative and quantitative changes in the biota.
Since plant growth is commonly limited by nutrient levels, a gradual
increase in nutrient levels would be expected to lead to successional
changes in the plant community.
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