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Table 4 Concentrations of some compounds in lake Baikal water

Compound

Concentration

 

 

Pb (µg L 1)

0.110.75

Cd (µg L 1)

0.0158.50

Hg (µg L 1)

0.080.38

Sb (µg L 1)

0.110.31

U (µg L 1)

0.371.33

DDT (µg L 1)

0.0060.017

Oil products (mg L 1);

 

Northern Baikal

0.031.00

Southern Baikal

0.030.66

Outow of Angara

0.000.11

Source: After Grachev,[25] Silow & Orlov,[35] and Silow & Khodzher.[36]

are able to suppress phytoplankton under ice,[44] the rest of these substances are toxic for lake Baikal ecosystem components. Additionally, heavy metals and surfactants can be accumulated in trophic chains, concentrating in nal

Lake Baikal: Current Environmental Problems

consumers organisms (large shes, aquatic birds, seal, human beings).[2123]

Now, we observe the uctuations of different compounds concentrations in water (Table 4). These uctuations are the result of the income of allochthonous compounds as well as of self-purication processes in the background of other factors acting, as natural oil springs, natural oscillations of hydrochemical regime, geological, and hydrological processes. Here, we can swear for anthropogenic origin for DDT (dichlorodiphenyltrichloroethane) only.

SELF-PURIFICATION PROCESSES

It is very important to take into account the processes of self-purication of lake Baikal. Every organic molecule is a precious food for baikalian bacteria, which decompose any natural organic substance (including benz(a)pyrene and dioxins of natural origin) and cannot decompose arti- cial substances such as pesticides (e.g., DDT) and some surfactants. The decomposition of organic substances in Baikal

Table 5 Income of contaminants to the lake Baikal (103 t year 1) during 19992010

 

 

 

 

Source

 

 

 

 

 

 

 

Wastes and

 

 

 

 

 

 

 

washes from

 

 

 

 

 

 

 

settlements at

 

Atmospheric

Contaminant

 

BPPC

Navigation

Tourism

shores

Tributaries

precipitations

 

 

 

 

 

 

 

Mineralization

40.7+1

0.011+0.002

2+0.3

5.26+0.63

4304+763

413+47

Without

 

 

 

 

 

 

 

Sulfates

26+0.1

 

 

1.23+0.15

380+67

63.6+19

Mineral nitrogen

 

 

0.008+0.001

1.5+0.3

0.384+0.0461

3.3+1.1

17.9+3.8

Mineral

 

 

0.003+0.0005

0.3+0.08

0.106+0.013

0.46+0.17

0.7+0.1

phosphorus

 

 

 

 

 

 

 

Heavy metals

 

 

 

 

0.017+0.002

0.43+0.36

0.037+0.005

Dissolved organic

5.6+0.1

0.28+0.011

6+0.9

5+0.6

1260+480

271+86

matter

 

 

 

 

 

 

 

Without

 

 

 

 

 

 

 

Easily oxidated

0.5+0.02

0.03+0.001

6+0.9

3.54+0.42

54+7.1

 

matter

 

 

 

 

 

 

 

Volatile phenolic

0.002+0.001

 

 

0.003+0.001

0.07+0.07

0.015+0.001

compounds

 

 

 

 

 

 

 

Sulfur-containing

0.012+0.001

 

 

 

0.12+0.06

 

compounds

 

 

 

 

 

 

 

Oil products

0.002+0.0001

0.25+0.01

0.06+0.01

0.16+0.02

0.93+0.38

0.198+0.049

Hardly oxidated

5+0.4

 

 

 

387+102

 

matter

 

 

 

 

 

 

 

Surfactants

 

 

 

0.01+0.001

0.04+0.01

0.37+0.15

 

Particulate matter

0.673+32

2.5+0.1

780+112

10.1+1.2

818+370

550+234

% of total

0.91

0.04

0.20

0.30

83.34

15.22

Source: From State report.[2633]

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Lake Baikal: Current Environmental Problems

is supported by the high content of oxygen in baikalian water, which is benecial both for chemical as well as biological oxidation of pollutants. Synthetic organic substances and heavy metals are adsorbed by particulate matter, by surface of bacteria, protozoa, and algae, by feeding mechanisms of ltering organisms of benthos (sponges) and, especially, zooplankton. Part of the substances, adsorbed by plankton organisms, is included in trophic chain after eating their carriers by other organisms of plankton and nekton. In the end they are sedimented to the bottom with animal bodies and fecal pellets. At the bottom they are partly buried in bottom sediments, and partly continue movement along the trophic chains of coprophages, necrophages, and detritus-consumers. All these substances end

their movement in terrestrial ecosystems, or, mostly, in bottom sediments.[35,37,44]

It is necessary to emphasizealthough there is some contamination (Table 5) of lake Baikal, nevertheless, that the water of lake Baikal remains the purest among the natural lake waters and is drinkable even in the regions of local pollution.

7

CONCLUSION

We have analyzed the consequences of anthropogenic inuence on the lake ecosystem with mathematical model, taking into account input of nutrients, toxic, and non-toxic compounds at the level of end of 1980s to the beginning of 1990s, when industry and agriculture were more powerful than they are now. According to predictions of this model[4451] we can wait for decrease of biomass of underice phytoplankton and increase of summer phytoplankton, some decrease of under-ice and increase of summer zoo-

plankton. These predictions were supported by observations between 1990 and 2000.[57,11]

It is necessary to note that global climate change caused a decrease of share of large-cells phytoplankton, increase of share of small-cells phytoplankton, and mass development

of some groups of phytoplankton (cladocerans[51]). All of these processes are described for Baikal.[810,1214]

We must emphasize the predicted consequences of chemical pollution of the lake and possible shifts caused by climate change are practically the same. In both cases

Fig. 4 Lake Baikal in early spring (A), midsummer (B), late autumn (C), and middle of winter (D).

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we await the growth of small-cells phytoplankton share, strengthening of summer phytoplankton, cladocerans, and cyclops development. The picture observed coincide with this. Therefore, today we cannot select one of the explanations of observed pictureis this consequence of local and regional anthropogenic impact in the form of pollution the result of global climate change, or the effect of natural oscillating processes? We can say that lake Baikal obviously is withstanding quite successfully to current anthropogenic impact due to its high self-purication potential, based on its morphometry (volume, depth, relation of water surface area to depth), hydrophysical and hydrochemical features (saturation of water with oxygen to maximal depths, low starting concentrations of chemical components), and functioning of its ecosystem (Fig. 4).

ACKNOWLEDGMENTS

Authors are grateful to program of strategic development of Irkutsk state university for 20122016, supported this research with grant #R212-IB-001.

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