D10: Impact of Contaminants - Hydromod
D10: Impact of Contaminants - Hydromod
D10: Impact of Contaminants - Hydromod
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Integrated Water Resource Management for Important Deep European Lakes and their Catchment Areas<br />
EUROLAKES<br />
<strong>D10</strong>: <strong>Impact</strong> <strong>of</strong> <strong>Contaminants</strong><br />
FP5_Contract No.: EVK1-CT1999-00004<br />
Version: 4.0<br />
Date: 25/07/01<br />
File: <strong>D10</strong>-vers.4.0.doc<br />
Page 58 <strong>of</strong> 136<br />
9 LEVEL OF POLLUTION IN WATER AND SEDIMENT<br />
In the [ENVIRONMENTAL ATLAS BERLIN] it is said that there is a continual accumulation<br />
<strong>of</strong> pollutants in water bottom soils, such as heavy metals and chlorinated hydrocarbons.<br />
In the material cycle <strong>of</strong> waters sediments form a natural buffer and filter system. The<br />
waters are subject to strong variations <strong>of</strong> current, substance input, substance transport<br />
and sedimentation. In addition to the water sample analyses practised for years, sediment<br />
analyses is increasingly important in evaluating qualities <strong>of</strong> the total ecosystem <strong>of</strong><br />
a water body. In comparison to water analyses and independent <strong>of</strong> current inputs,<br />
sediment tests reflect the long term quality situation. For this reason, sediment tests are<br />
a better basis for fundamental comparisons with other flowing waters. The suspended<br />
and precipitate substances stored on the water bottom form a reservoir for many pollutants<br />
and trace substances <strong>of</strong> low solubility and low degree <strong>of</strong> degradability. According<br />
to their chemical persistence and the physical-chemical and biochemical characteristics<br />
the substances are conserved in sediments over longer periods <strong>of</strong> time. Even after<br />
sedimentation, portions <strong>of</strong> fixed substances can be remobilised and re-enter the material<br />
cycle <strong>of</strong> water. Analyses <strong>of</strong> sediment samples from different depths give a chronological<br />
record <strong>of</strong> inputs in waters and can also allow conclusions to be drawn regarding<br />
sources <strong>of</strong> contamination. Also mineral suspension and precipitation substances are<br />
able to store heavy metal ions on their outer surface and they can also be bound in<br />
water organisms. The heavy metals can be taken up by higher organisms through the<br />
food chain, or they sink to the bottom as sediment, depending on the flow velocity <strong>of</strong><br />
water. Various pesticides and PCB have the characteristic <strong>of</strong> being stored adsorptively<br />
on suspended matter or in plant organisms. After attaining into the sediment this substances<br />
and by ingestion <strong>of</strong> the organisms they reach the food chain. Eels have a high<br />
fat content and eat bottom organisms and bury themselves in sediment. That way, the<br />
intake <strong>of</strong> pesticides and PCB not only takes place through nutrients. They also ingest<br />
them through the skin and accumulate them in the body fat [ENVIRONMENTAL ATLAS<br />
BERLIN].<br />
9.1 TRANSPORT AND ACTION OF TRANSPORT IN WATER<br />
[FENT 1998] refers that several processes are responsible for the destiny <strong>of</strong> chemicals<br />
in water bodies, like disposition, dilution in the water, volatility in the atmosphere, sedimentation,<br />
abiotic chemical conversation (hydrolysis, photolysis, oxidative and reductive<br />
processes), biotic conversations(microbial reduction, metabolism) and bioaccumulation.<br />
He continues that chemicals having a high vapour pressure and a low water solubility<br />
are given to the atmosphere very fast. If substances have a low water solubility and a<br />
low vapour pressure they prefer to adhere at particles and sediment. Figure 9-1 shows<br />
the apply <strong>of</strong> contaminants to their volatility in a simplified version.