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MAP Technical Reports Series No. 106 UNEP

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- 23 -<br />

conditions, the geochemical dynamics, which also include the flow of nitrogen and phosphorus,<br />

are regulated by natural processes that depend on the specific geological, orographic,<br />

sedimentological, geochemical, climatic and biotic environment in which these processes take<br />

place. Thermic and hydrological conditions are of primary importance. However, historically all<br />

these factors have been seriously affected or changed by man to various degree. A majority of<br />

present-day landscapes, even of some where man's influence is not immediately apparent (e.g.,<br />

the Mediterranean macchia), are to be classified under the category of anthropogenically<br />

transformed landscapes, in which natural expanses remain as disjunct pockets only.<br />

A breakdown into land use categories, and their implied relationship to pollution and<br />

nutrient sources, is given in Figures 2 and 3. This breakdown has been kept as complete as<br />

possible as a reminder, although in reality every situation differs from each other, and<br />

accordingly must be evaluated and assessed separately.<br />

Besides the still natural landscapes, which are listed for completeness but will not be<br />

treated further, the main anthropogenically transformed land use categories of interest in the<br />

context of eutrophication are:<br />

- Urban Settlements and Communications Areas<br />

- Farm Lands<br />

- Industrial Areas<br />

Urban Development. With the rapid expansion of population centres that began in the last<br />

century in developed countries, and now involves also developing countries, new technologies<br />

and facilities have been introduced. Of greatest hygienic and environmental consequences was<br />

the almost general introduction in developed countries of water supply and water disposal<br />

systems, i.e., sewers that often were discharged directly to rivers and/or lakes and other<br />

stagnant waters. With the improvement of centralized treatment facilities and secondary<br />

treatment during this century, some of the worst pollution effects resulting from the discharge<br />

of untreated sewage to waterways have been alleviated. Still, secondary treated urban sewage<br />

contains substantial amounts of phosphorus and nitrogen, which became the main cause of<br />

eutrophication at the turn of the century. With the introduction of household and industrial<br />

detergents containing polyphosphates after World War II the problem was further aggravated.<br />

Following the adoption of tertiary sewage treatment and due to a substantial reduction of<br />

polyphosphates in household detergents in some countries further development of the problem<br />

has been halted or slowed down in recent decades. Still, secondary and in particular tertiary<br />

treatment of urban sewage is not general, specially in countries bordering the Mediterranean.<br />

Accordingly, urban sewage remains a major source responsible for the continuing eutrophication<br />

of fresh and marine waters.<br />

Further to direct discharges of insufficiently treated sewage, run-offs from urban streets<br />

and highways, and connected areas continue to cause concern, in particular in situations of<br />

combined sewer systems that receive both urban sewage and urban run-offs. This causes<br />

difficulties of effective treatment in conditions of storm-run-offs because of excessive sewage<br />

dilution that reduces and endangers the correct biodynamic functioning of treatment plants.<br />

Farming. The relative role of various farming practices regarding their effects on<br />

eutrophication, instead, depends largely on whether farming is extensive or intensive. Extensive<br />

farming may have a low impact on eutrophication, even if animal stock raising is involved. As<br />

long as the uptake capacity of soils remains high, extensive farmlands may act

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