9.2.
Contamination of soils with inorganic
substances
When growing a variety of agricultural crops and harvesting the
yield, the main plant nutrients – nitrogen, phosphorus, potassium,
and microelements such as magnesium, iron, boron, etc., which
plants require in lesser quantities, are removed from the field. If
the content of these elements in the soil is not compensated, the soil
degrades and becomes unsuitable for crop production. Therefore, to
9. POLLUTION OF SOIL
197
maintain soil fertility and increase crop yields, natural and artificial
fertilizers in agriculture are extensively used.
Under intensive farming conditions mineral fertilizers ( super-
phosphate, potassium chloride, ammonium nitrate and others) are
widely applied, and the goal is to provide the necessary balanced
nutrient quantities for the agricultural crops. Due to economical
reasons, these fertilizers are usually as raw products, therefore
with each dose of fertilizer the soil could be polluted with certain
quantities of toxic metals and their compounds. For example, super-
phosphate contains metals such as arsenic, cadmium, chromium,
lead, vanadium, cobalt and others. These elements, along with
pesticide residues, accumulate in the soil over a long period of time
and contaminate it.
Soil pollution also consists of excessive mineral and organic
nitrogen and phosphorus amounts. Some of them are leached
from the soil into groundwater, wells and watercourses. However,
agricultural crops also are subject to the increased intake of nitrates,
for example, spinach, in which their quantity, depending on the
availability of nitrogen compounds in the soil, may vary between 1.4
to 3.5 g/kg. Increased phosphorus and nitrogen discharge into rivers
and lakes causes eutrophication. Furthermore, high concentra tions of
nitrates in drinking water and consumable plants can cause disease
in humans. During industrial processing, including conservation and
preservation, as well as consuming nitrate-rich vegetable products
into the human intestinal tract, nitrate ions NO
3
–
turn into nitrite ions
NO
2
–
. In the human body they interact with the haemoglobin in red
blood cells – erythrocytes, which ensure the oxygen transfer in the
organism. As a result, methaemoglobin is formed, which is incapable
to bind oxygen and causes serious illness – methemoglobinemia, a
disorder resulting in the oxygen starvation in the tissues of the body,
despite the fact that breathing is normal. In addition, it has been
established that nitrates in human intestinal tract can also turn into
nitrosamines, which are considered carcinogenic compounds.
A number of heavy metals that accumulate in the soil as a
result of fertilizer over-use are in the form of insoluble compounds,
which at the given conditions can not be consumed by plants and
microorganisms and, therefore, they are not biologically dangerous.
Such a set of sedentary chemical elements are chemical «time
bombs». Due to some changes in the external conditions (such as
human economic activities or climate change, increased soil acidity)
these compounds change into a soluble form and may pass into
ecological food chains with all the ensuing dangerous consequences.
It is to be recognized that one of the major factors of soil fertility
are organic fertilizers, whose misuse can locally cause high levels of
nitrogen pollution. This situation has been observed in many European
countries, including the Netherlands, Denmark and Germany.
198
ENVIRONMENT, POLLUTION, DEVELOPMENT: THE CASE OF UZBEKISTAN
A very serious environ mental problem today is the use of
sewage sludge as field fertilizer. Wastewater treatment plants in
the world every year accumulate thousands of tons of sludge, which
form huge piles at the treatment plants. Since sewage sludge is rich
in phosphorus and other plant nutrients, it was recommended to
address the sludge problem by using it as a fertilizer for growing
agricultural crops. However, the chemical analysis of sludge shows
that it also contains a lot of harmful chemicals – organic compounds
and heavy metals, which enter the sludge during the factory and
urban waste water treatment process. Thus, the harmful substances
which a man has tried to get rid of in wastewater treatment process,
and which are concentrated in one place, are dispersed again over a
wide area and injected into the soil from where they can be ingested
by plants or leach into groundwater. Many researchers have warned
against the dangers of such practice to environ ment.
Industrial pollution is caused by a variety of manufacturing
processes associated with processing of substances and materials,
power generation and fuel use in manufacturing processes. The
most important is the industrial pollution, which is ejected into
the atmo sphere from the factory chimneys. It consists of gases,
aerosols and dust particles, which in the air masses are carried
over long distances, during the precipitation formation processes
dissolve within the water droplets in the atmo sphere and eventually
settle or fall on vegetation or soil. The chemical composition of
industrial pollution is largely dependent on the substances used in
the production and technological processes. It is as diverse as the
industrial production, therefore in each particular case the industrial
pollution interaction with the environ ment is specific.
A very topical problem in the 20
th
century was sulfur-containing
industrial emission impact. Most industrial plants and heat-electric
generating plants used the coal as fuel, but in its combustion process
great quantities of sulfur dioxide SO
2
are released. This gas dissolves
in precipitation water to form acid rain, therefore much attention
was paid to research the ecological effects of soil acidification. It
has been found that the acid rain most of all affects plants and soil
microorganisms.
Since the the end of 1980s the production technology improve-
ment, introduction of filter systems and replacement of coal as a pri-
mary fuel with natural gas, sulfur-containing emissions are reduced
considerably. However, environ mental problems caused by acid rain
have not become less acute, because due to the rise in car ownership
and, consequently, the amount of car exhaust, nitrogen oxide emis-
sions in the world have increased significantly, which, dissolving in
atmo spheric precipitation water enter the soil in the form of ammo-
nium NH
4
+
and nitrate ions NO
3
–
.
Of all the industrial
enterprise types, the
most important in the
context of environmental
pollution are considered:
chemical complexes;
smelting companies;
mining companies;
building complexes;
heat‑electric
generating plants.
9. POLLUTION OF SOIL
199
Near the mines and smelting plants the soils are profusely
contaminated with heavy metals. Under severe pollution conditions
over a wide area around the metal smelting plants the so-called
industrial deserts develop, where almost no vegetation or animals are
found. An example of such a desert is the surroundings of the non-
ferrous metal production complex «Severonikel» built in the North of
Russia. Forest soil pollution with heavy metals has a negative impact
on soil microorganisms and fauna.
The persistent pollution, which could not be destroyed collapse
biologically, is of special significance. The term ‘heavy metals’
commonly denotes the metals, whose relative density is greater
than 5 g/cm
3
and thus about 70, or seven-eighths of all the known
metals are heavy metals. In the environ mental protection, according
to the use of metals in the economy and the severe danger of their
compounds, more attention is paid only to certain heavy metals
and non-metals, the effects of which may pose a threat to living
organisms, such as arsenic (As), mercury (Hg), cadmium (Cd),
selenium (Se), copper (Cu), zinc (Zn), chromium (Cr), nickel (Ni),
lead (Pb), tin (Sn), antimony (Sb), bismuth (Bi), cobalt (Co).
Heavy metals enter the atmo sphere as a result of a variety
of pollu tion sources, and with time as a result of the wet and the
dry deposition they land on the soil. It is estimated that in Europe
annually 130 g/ha of Ni, 500 g/ha of Zn, 20 g/ha of Pb, 75 g/ha
of C, 20 g/ha of Cr and 3.5 g/ha Cd land on the soil. Industrial
activity, energy production and motor transport impact result in
the increased concentrations of heavy metals in the upper soil layer
on a global scale, as the soil has very high metal sorption capacity.
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