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Organic pollutants                                                    167

                      BTEXs are among the most hazardous constituents of petrol and solvents. Except for
                   short-term hazards from concentrated spills, BTEX  compounds have been more frequently
                   associated with risk to human health than with risk to plants and animals. This is partly
                   due to the fact that plants and animals take up BTEX compounds in very small amounts
                   and BTEXs tend to volatilise relatively rapidly into the atmosphere rather than persisting
                   in surface waters and soils. However, BTEX compounds may pose a threat to drinking
                   water quality when they accumulate in groundwater. Short-term hazards of BTEX include
                   potential acute toxicity  to aquatic life in surface water and potential inhalation hazards.
                   Acute exposures to high levels of BTEX may cause irritation of the skin, eyes, and respiratory
                   tract, and depression of the central nervous system. Long-term potential hazards of BTEX
                   compounds include chronic inhalation and contamination of groundwater. Prolonged
                   exposure to BTEXs may cause changes in the liver and adverse effects on the kidneys, heart,
                   lungs, and the central nervous system. Benzene is the most dangerous and carcinogenic
                   to humans. Its chronic effects encompass the destruction of bone marrow, leading to
                   a reduction of red and white blood cells.  Workers exposed to high levels of benzene  in
                   occupational settings have been found to have an increased incidence of leukaemia. Toluene
                   may also adversely affect reproduction.
                      The acronym BTEX  suggests that benzene , toluene , ethylbenzene, and xylenes are
                   often found together at contaminated sites. The principal source of BTEX contamination
                   is the leakage of petrol from faulty underground storage tanks. Other sources of BTEX
                   contamination are releases from large bulk facilities, surface spills, and pipeline leaks. Once
                   released to the environment, BTEXs are liable to volatilisation , dissolution , adsorption , and
                   biodegradation . Although BTEXs can behave as a LNAPL, which means that the bulk of
                   the BTEX floats on water, it can also dissolve in water. Compared to the other components
                   in petrol, such as the aliphatic  components, BTEXs are very soluble in water. BTEXs can
                   be adsorbed by organic matter  in soil, but are not sorbed to soil particles as strongly as the
                   aliphatic components.  The bacterial flora naturally present in soil is capable of breaking
                   down BTEXs under aerobic  conditions (Brady  et al., 1998). Like the decomposition  of
                   the other mineral oil  components, the biodegradation rate depends on temperature and
                   the supply of oxygen  and nutrients. Toluene and – to some extent – xylene  can also be
                   biodegraded under anaerobic  conditions (Edwards et al., 1992). In anaerobic sediments, the
                   natural biodegradation is largely controlled by the amount of bioavailable Fe(III), which can
                   act as an electron acceptor. Typically, bioavailable Fe(III) constitutes between 10% and 30%
                   of the total amount of iron present in aquifer material (Manshoven et al., 2010).


                   9.4  POLYCYCLIC AROMATIC  HYDROCARBONS

                   Polycyclic aromatic  hydrocarbons (PAHs ) are a class of over 100 different, very stable
                   organic molecules that are made up of only carbon and hydrogen and contain two or more
                   connected benzene  rings (see examples in Figure 9.Ib). These molecules are formed during
                   the incomplete burning of coal, oil and gas, garbage, or other organic substances like
                   tobacco or charbroiled meat. PAHs are found in coal tar, crude oil, creosote, and roofing
                   tar. Some PAHs are manufactured and are used in medicines or to make dyes, plastics, and
                   pesticides . Pure PAHs usually exist as colourless, white, or pale yellow-green solids. PAHs are
                   commonly divided into two groups, depending upon their physical and chemical properties:
                   low-molecular-weight PAHs, containing three or fewer aromatic rings, and high-molecular-
                   weight PAHs, containing more than three aromatic rings. Most PAHs are semi-volatile and
                   the volatility generally increases with decreasing molecular weight. PAHs containing 6 or
                   more benzene rings are barely volatile. The US Environmental Protection Agency has defined
                   a subset of 16 PAHs that are most important from an environmental perspective. These 16










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