10 research outputs found
Microflora of drinking water distributed through decentralized supply systems (Tomsk)
The paper considers microbiological quality of waters from decentralized water supply systems in Tomsk. It has been proved that there are numerous microbial contaminants of different types. The authors claim that the water distributed through decentralized supply systems is not safe to drink without preliminary treatment
Groundwater microflora of the Aptian-Cenomanian deposits at the Igolsko-Talovoe field in Tomsk Region
The authors have studied the microbiological composition of the groundwater of the Aptian-Cenomanian deposits in the territory of the Igolsko-Talovoe field in Tomsk Region. The detected diversity of the physiological groups of bacteria can be a corrosive component for waters used in the reservoir pressure maintenance system. The research findings have allowed making conclusions about the need to study the contribution of all microorganisms inhabiting the waters of the Aptian-Cenomanian deposits to corrosion
Microbiological composition of river waters in the Ob' basin (West Siberia) and its associations with hydrochemical indices
Chemical and microbiological composition of the Mid-Ob' and its feeders' waters has been studied. Swampiness of the area is the cause of significant organic and biogenic substance content in streams, and it is also responsible for a large variety of organotrophic microflora. Microbiological composition of studied streams characterizes them as contaminated. Settlements are the main sources of the investigated area water pollution
Hydrogeological Conditions Changes of Tomsk, Russia
The hydro-geological conditions of Tomsk are determined by both natural factors and the impact of the urban infrastructure. Important impact on subsurface water flows involves the complex hydraulic relationship of several geological layers and the ancient and modern relief. Increasing groundwater abstraction has generally led to lowered piezometric heads in the deeper aquifer horizons, while in the uppermost horizons, rises in the water table and formation of new perched water tables are experienced due to leaking pipes and impedance of groundwater flow by deep foundations. In this paper special attention is paid to the Quaternary aquifer complex. Barrage effects of pile foundations and the intensive development of perched water distributed on flat surfaces of the watersheds and high terraces, complicated conditions for the construction and operation of facilities, leading in some cases to emergency situations
Groundwater chemical and microbiological composition in Aptian-Cenomanian deposits (Kaimisovsky oil-gas bearing province)
This paper reveals the investigation results of the groundwater chemical and microbiological composition in Aptian-Cenomanian deposits, Kaimisovsky oil-gas bearing province. The mineral-forming behavior of the groundwater was evaluated. It was determined that the diversity of microbial communities could be corrosive- harmful for the groundwater used in reservoir pressure maintenance systems. According to the research results it is necessary to study the groundwater microorganisms in Aptian-Cenomanian deposits and their influence on groundwater itself
Hydrogenous mineral neoformations in Tomsk water intake facility from underground sources
The article considers study outcomes of hydrogenous mineral neoformations precipitated on deferrization filters of Tomsk water intake facility from underground sources. Compositionally, these precipitations are colloform and polymineral including ferrous, carbonate and aluminosilicate mineral phases. Ferrous phase predominates and embraces ferric hydroxides (ferrihydrate, goethite, hematite and lepidocrocite) and ferrous hydrophosphates (vivianite, strengite, strunzite and rockbridgeit). Carbonate and aluminosilicate minerals are calcite and kaolinite-group, respectively
Chemical and microbiological composition of groundwaters of decentralized water supply of southern and central districts of Tomsk region
Relevance of the research is caused by the necessity of assessing the quality of drinking water, consumed by the population, in the conditions of decentralized water supply. The aim of research consists in studying chemical and microbiological composition of groundwater which is formed in a natural environment. Methods of research. Chemical and microbiological compositions of water were investigated in the Problem research hydrogeochemical laboratory (TPU), which is registered in the System of analytical laboratories of Gosstandart of Russia. To carry out the full chemical analysis the authors applied the traditional methods. The microbiological analysis was carried out after sampling, as a rule, during the day, while the samples were kept in the cooler bag. To identify the microorganisms the authors used liquid and firm elective nutrient mediums. The trace elements were determined by mass-spectrometer method with inductively coupled plasma (ICP-MS) on the device Elan 6000 (Perkin Elmer) in Geo assets and environment laboratory of Toulouse (CNRS, France). Results. The data of chemical and microbiological compositions of drinking groundwater of Quaternary, Neogene, Paleogene and Cretaceous sediments shown that water is epidemiologically safe (Escherichia coli is not detected), while they often are not suitable for drinking water supply by chemical composition on such components as Fe, Mn, COD, Si, NO2-, NH4+, trace elements - Ba, B and Li. Excess of these elements reflects natural background of the territory and they are typical of the whole region. The microbial flora reflects the geochemical environment, rich in organic matter, but poor in mineral substances
Microbiological conditions of chemical elements distribution on peat deposit depth in ecosystems of the Vasyugan swamp east part (Western Siberia)
ΠΠΊΡΡΠ°Π»ΡΠ½ΠΎΡΡΡ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΠ΅ΡΡΡ Π½Π΅ΠΎΠ±Ρ
ΠΎΠ΄ΠΈΠΌΠΎΡΡΡΡ ΡΡΠ΅ΡΠ° Π²Π·Π°ΠΈΠΌΠΎΡΠ²ΡΠ·Π΅ΠΉ ΠΌΠ΅ΠΆΠ΄Ρ ΡΠ°ΡΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΠ΅ΠΌ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² ΠΏΠΎ Π³Π»ΡΠ±ΠΈΠ½Π΅ ΡΠΎΡΡΡΠ½ΠΎΠΉ Π·Π°Π»Π΅ΠΆΠΈ, ΠΏΡΠΎΡΠ΅ΡΡΠ°ΠΌΠΈ ΡΠΎΡΠΌΠΈΡΠΎΠ²Π°Π½ΠΈΡ, ΡΠ²ΠΎΠ»ΡΡΠΈΠΈ ΠΈ Π΄Π΅Π³ΡΠ°Π΄Π°ΡΠΈΠΈ Π±ΠΎΠ»ΠΎΡ ΠΏΡΠΈ ΡΠ΅ΡΠ΅Π½ΠΈΠΈ ΡΠ΅Π»ΠΎΠ³ΠΎ ΡΡΠ΄Π° ΡΡΠ½Π΄Π°ΠΌΠ΅Π½ΡΠ°Π»ΡΠ½ΡΡ
ΠΈ ΠΏΡΠΈΠΊΠ»Π°Π΄Π½ΡΡ
Π·Π°Π΄Π°Ρ ΠΈΠ·ΡΡΠ΅Π½ΠΈΡ, ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ ΠΈ ΠΎΡ
ΡΠ°Π½Ρ Π±ΠΎΠ»ΠΎΡ. Π¦Π΅Π»Ρ: ΠΎΡΠ΅Π½ΠΊΠ° ΠΌΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΡΠ»ΠΎΠ²ΠΈΠΉ ΡΠ°ΡΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΡ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² ΠΏΠΎ Π³Π»ΡΠ±ΠΈΠ½Π΅ ΡΠΎΡΡΡΠ½ΠΎΠΉ Π·Π°Π»Π΅ΠΆΠΈ ΠΈ Π²ΡΡΠ²Π»Π΅Π½ΠΈΠ΅ ΡΠ²ΡΠ·Π΅ΠΉ ΠΌΠ΅ΠΆΠ΄Ρ Π³Π΅ΠΎΡ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΠΌΠΈ ΠΈ ΠΌΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΠΌΠΈ ΠΏΠΎΠΊΠ°Π·Π°ΡΠ΅Π»ΡΠΌΠΈ ΡΠΎΡΡΠΎΠ² Π² Π²ΠΎΡΡΠΎΡΠ½ΠΎΠΉ ΡΠ°ΡΡΠΈ ΠΠ°ΡΡΠ³Π°Π½ΡΠΊΠΎΠ³ΠΎ Π±ΠΎΠ»ΠΎΡΠ°. ΠΠ΅ΡΠΎΠ΄Ρ: ΠΌΠ΅ΡΠΎΠ΄Ρ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ ΠΈ ΠΌΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ Π°Π½Π°Π»ΠΈΠ·Π° (Π²ΠΊΠ»ΡΡΠ°Ρ ΠΌΠ°ΡΡ-ΡΠΏΠ΅ΠΊΡΡΠΎΠΌΠ΅ΡΡΠΈΡΠ΅ΡΠΊΠΈΠΉ Ρ ΠΈΠ½Π΄ΡΠΊΡΠΈΠ²Π½ΠΎ ΡΠ²ΡΠ·Π°Π½Π½ΠΎΠΉ ΠΏΠ»Π°Π·ΠΌΠΎΠΉ), ΡΡΠ°ΡΠΈΡΡΠΈΡΠ΅ΡΠΊΠΈΠ΅ ΠΌΠ΅ΡΠΎΠ΄Ρ. Π Π΅Π·ΡΠ»ΡΡΠ°ΡΡ ΠΈ Π²ΡΠ²ΠΎΠ΄Ρ. ΠΡΠΏΠΎΠ»Π½Π΅Π½ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΠΉ, ΠΌΠΈΠ½Π΅ΡΠ°Π»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΠΉ ΠΈ ΠΌΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΡ
Π°Π½Π°Π»ΠΈΠ· ΠΏΡΠΎΠ± ΡΠΎΡΡΠΎΠ² ΠΈ ΠΌΠΈΠ½Π΅ΡΠ°Π»ΡΠ½ΠΎΠ³ΠΎ Π³ΡΡΠ½ΡΠ°, ΠΎΡΠΎΠ±ΡΠ°Π½Π½ΡΡ
09.11.2018 Π³. Π² Π²ΠΎΡΡΠΎΡΠ½ΠΎΠΉ ΡΠ°ΡΡΠΈ ΠΠ°ΡΡΠ³Π°Π½ΡΠΊΠΎΠ³ΠΎ Π±ΠΎΠ»ΠΎΡΠ° (Π³ΡΠ°Π½ΠΈΡΠ° Π²ΠΎΠ΄ΠΎΡΠ°Π·Π΄Π΅Π»Π° ΡΠ΅ΠΊ ΠΊΠ»ΡΡ ΠΈ ΠΠ°Π²ΡΠΈΠ»ΠΎΠ²ΠΊΠ° β ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² ΡΠ΅ΡΠ½ΠΎΠΉ ΡΠ΅ΡΠΈ: (ΠΠ»ΡΡβΠΠ°ΠΊΡΠ°Ρ; ΠΠ°Π²ΡΠΈΠ»ΠΎΠ²ΠΊΠ°βΠΠΊΡΠ°) β Π§Π°ΡβΠΠ±Ρ; Π²Π½ΡΡΡΠΈΠ±ΠΎΠ»ΠΎΡΠ½ΡΠ΅ ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΡ: ΠΎΠ»ΠΈΠ³ΠΎΡΡΠΎΡΠ½ΡΠΉ Π³ΡΡΠ΄ΠΎΠ²ΠΎ-ΠΌΠΎΡΠ°ΠΆΠΈΠ½Π½ΡΠΉ ΠΊΠΎΠΌΠΏΠ»Π΅ΠΊΡ, Π³ΡΡΠ΄Π°; ΠΎΠ»ΠΈΠ³ΠΎΡΡΠΎΡΠ½ΠΎΠ΅ ΡΠΎΡΠ½ΠΎΠ²ΠΎ-ΠΊΡΡΡΠ°ΡΠ½ΠΈΡΠΊΠΎΠ²ΠΎ-ΡΡΠ°Π³Π½ΠΎΠ²ΠΎΠ³ΠΎ Π±ΠΎΠ»ΠΎΡΠ° β ΡΡΠΌ; ΠΌΠ΅Π·ΠΎΡΡΠΎΡΠ½ΠΎΠ΅ ΡΠΎΡΠ½ΠΎΠ²ΠΎ-ΠΊΡΡΡΠ°ΡΠ½ΠΈΡΠΊΠΎΠ²ΠΎΠ΅ Π±ΠΎΠ»ΠΎΡΠΎ Π½Π° Π³ΡΠ°Π½ΠΈΡΠ΅ ΡΡΠΌΠ° Ρ Π·Π°Π±ΠΎΠ»ΠΎΡΠ΅Π½Π½ΡΠΌ Π»Π΅ΡΠΎΠΌ β ΠΌΠ΅Π·ΠΎΡΡΠΎΡΠ½Π°Ρ ΠΎΠΊΡΠ°ΠΈΠ½Π°. ΠΠΎΠΊΠ°Π·Π°Π½ΠΎ, ΡΡΠΎ, Π²ΠΎ-ΠΏΠ΅ΡΠ²ΡΡ
, Π±ΠΎΠ»ΠΎΡΠ½Π°Ρ ΠΌΠΈΠΊΡΠΎΡΠ»ΠΎΡΠ° ΡΠ²Π»ΡΠ΅ΡΡΡ ΠΎΡΠ΅Π½Ρ Π²Π°ΠΆΠ½ΡΠΌ ΡΠ°ΠΊΡΠΎΡΠΎΠΌ ΡΠ°ΡΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΡ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² ΠΏΠΎ Π³Π»ΡΠ±ΠΈΠ½Π΅ ΡΠΎΡΡΡΠ½ΠΎΠΉ Π·Π°Π»Π΅ΠΆΠΈ Π² ΡΠ°Π·Π»ΠΈΡΠ½ΡΡ
Π²Π½ΡΡΡΠΈΠ±ΠΎΠ»ΠΎΡΠ½ΡΡ
ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΠ°Ρ
Π²ΠΎΡΡΠΎΡΠ½ΠΎΠΉ ΡΠ°ΡΡΠΈ ΠΠ°ΡΡΠ³Π°Π½ΡΠΊΠΎΠ³ΠΎ Π±ΠΎΠ»ΠΎΡΠ°. ΠΠ΅ΡΠΎΡΡΠ½ΠΎΡΡΡ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ Π² ΡΠΎΡΡΠ°Ρ
ΠΌΠ°Π»ΠΎΡΠ°ΡΡΠ²ΠΎΡΠΈΠΌΡΡ
ΡΠΎΠ΅Π΄ΠΈΠ½Π΅Π½ΠΈΠΉ ΠΊΠ°Π»ΡΡΠΈΡ, ΠΆΠ΅Π»Π΅Π·Π° ΠΈ ΡΠ΅Π΄ΠΊΠΎΠ·Π΅ΠΌΠ΅Π»ΡΠ½ΡΡ
ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² Π²ΠΎΠ·ΡΠ°ΡΡΠ°Π΅Ρ ΠΏΠΎ ΠΌΠ΅ΡΠ΅ ΡΡΠΈΠ»Π΅Π½ΠΈΡ Π°Π½Π°ΡΡΠΎΠ±Π½ΡΡ
ΡΡΠ»ΠΎΠ²ΠΈΠΉ ΡΠ°Π·Π²ΠΈΡΠΈΡ Π±ΠΎΠ»ΠΎΡΠ½ΠΎΠΉ ΠΌΠΈΠΊΡΠΎΡΠ»ΠΎΡΡ, ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΡΡΠΈΡ
ΡΠ²Π΅Π»ΠΈΡΠ΅Π½ΠΈΠ΅ ΡΠ Π±ΠΎΠ»ΠΎΡΠ½ΠΎΠΉ ΡΡΠ΅Π΄Ρ Π΄ΠΎ 7,8 ΠΈ Π²ΡΡΠ΅, ΡΡΠΎ ΠΏΡΠΈΠ²ΠΎΠ΄ΠΈΡ ΠΊ ΡΠΌΠ΅ΡΠ΅Π½ΠΈΡ ΠΊΠ°ΡΠ±ΠΎΠ½Π°ΡΠ½ΠΎΠ³ΠΎ ΡΠ°Π²Π½ΠΎΠ²Π΅ΡΠΈΡ ΠΈ Π²ΡΠΏΠ°Π΄Π΅Π½ΠΈΡ ΠΌΠ°Π»ΠΎΡΠ°ΡΡΠ²ΠΎΡΠΈΠΌΡΡ
ΡΠΎΠ΅Π΄ΠΈΠ½Π΅Π½ΠΈΠΉ ΠΊΠ°Π»ΡΡΠΈΡ. ΠΠΎ-Π²ΡΠΎΡΡΡ
, Π²ΠΎΠ·ΠΌΠΎΠΆΠ½ΠΎΡΡΡ Π²ΡΠ²Π΅Π΄Π΅Π½ΠΈΡ ΠΈΠ· ΡΠ°ΡΡΠ²ΠΎΡΠ° Π³ΠΈΠ΄ΡΠΎΠΊΡΠΈΠ΄ΠΎΠ² ΠΆΠ΅Π»Π΅Π·Π° ΡΠ²Π»ΡΠ΅ΡΡΡ Ρ
Π°ΡΠ°ΠΊΡΠ΅ΡΠ½ΠΎΠΉ ΠΎΡΠΎΠ±Π΅Π½Π½ΠΎΡΡΡΡ Π³Π΅ΠΎΡ
ΠΈΠΌΠΈΠΈ ΡΠΎΡΡΡΠ½ΡΡ
Π±ΠΎΠ»ΠΎΡ Π½Π° ΡΠΎΠ½Π΅ Π½Π΅Π·Π½Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎΠΉ, Π½ΠΎ ΠΏΠΎΡΡΠΎΡΠ½Π½ΠΎ Π½Π°Π±Π»ΡΠ΄Π°Π΅ΠΌΠΎΠΉ Π°ΠΊΡΠΈΠ²Π½ΠΎΡΡΠΈ ΠΆΠ΅Π»Π΅Π·ΠΎΠ±Π°ΠΊΡΠ΅ΡΠΈΠΉ, ΠΎΠ±ΡΠ°Π·ΡΡΡΠΈΡ
Π³ΠΈΠ΄ΡΠΎΠΊΡΠΈΠ΄Ρ ΠΆΠ΅Π»Π΅Π·Π°. Π-ΡΡΠ΅ΡΡΠΈΡ
, Π²ΡΠ»Π΅Π΄ΡΡΠ²ΠΈΠ΅ ΡΠΎΡΠ±ΡΠΈΠΎΠ½Π½ΡΡ
ΠΏΡΠΎΡΠ΅ΡΡΠΎΠ² Π½Π° Π³ΠΈΠ΄ΡΠΎΠΎΠΊΠΈΡΠ»Π°Ρ
ΠΆΠ΅Π»Π΅Π·Π° (ΠΈ ΠΌΠ°Π»ΠΎΡΠ°ΡΡΠ²ΠΎΡΠΈΠΌΡΡ
ΡΠΎΠ΅Π΄ΠΈΠ½Π΅Π½ΠΈΡΡ
ΠΊΠ°Π»ΡΡΠΈΡ Π² Π½ΠΈΠΆΠ½ΠΈΡ
ΡΠ»ΠΎΡΡ
ΡΠΎΡΡΡΠ½ΠΎΠΉ Π·Π°Π»Π΅ΠΆΠΈ) ΠΏΡΠΎΠΈΡΡ
ΠΎΠ΄ΠΈΡ ΠΎΡΠ°ΠΆΠ΄Π΅Π½ΠΈΠ΅ Π³ΠΈΠ΄ΡΠΎΠΎΠΊΠΈΡΠ»ΠΎΠ², ΡΠΎΡΡΠ°ΡΠΎΠ² ΠΈ ΠΊΠ°ΡΠ±ΠΎΠ½Π°ΡΠΎΠ² (Π²ΠΎΠ·ΠΌΠΎΠΆΠ½ΠΎ β ΡΡΠ»ΡΡΠ°ΡΠΎΠ² ΠΈ ΡΡΠ»ΡΡΠΈΠ΄ΠΎΠ²) ΡΡΠ΄Π° ΠΌΠΈΠΊΡΠΎΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ², Π²ΠΊΠ»ΡΡΠ°Ρ ΡΠ΅Π΄ΠΊΠΎΠ·Π΅ΠΌΠ΅Π»ΡΠ½ΡΠ΅ ΡΠ»Π΅ΠΌΠ΅Π½ΡΡ.Relevance of the research is determined by the necessity to account the interrelations between distribution of chemical elements on peat deposit depth, formation, evolution and degradation of bogs when solving a number of fundamental and applied problems of study, use and protection of bogs. The aim of the research is the estimation of microbiological conditions of chemical elements distribution on peat deposit depth and revealing of relations between geochemical and microbiological parameters of peats in east part of the Vasyugan swamp. Methods: methods of chemical and microbiological analysis (including MS-ICP), statistical methods. Results and conclusions. The authors have carried out chemical, mineralogical and microbiological analysis of peats and mineral ground samples. The samples were selected on the 9 of November, 2018 in east part of the Vasyugan swamp (border of a watershed of the Klyuch and Gavrilovka rivers which are the elements of a river network (Β«Klyuch-Bakchar; GavrilovkaIksa-Chaya-ObΒ»; intraswamp eco- logical systems: the oligotrophic hollow-ridge complex, a ridge; the oligotrophic pine-dwarf-shrub-sphagnum raised bog (ryam), the mesotrophic border of an oligotrophic bog). It is shown that, first, the swamp microflora is a very important factor of chemical elements distribution on peat deposit depth in various intraswamp ecosystems in east part of the Vasyugan swamp. The probability of accumulation insoluble compounds of calcium, iron and rare earth elements in peats grows in amplification of microflora development unaerobic conditions. These factors determine increase of ΡΠ up to 7,8 and higher, that results in displacement carbonate balance and loss of in- soluble calcium compounds. Second, the opportunity of iron hydroxides removing from a solution is the prominent feature of geochemistry of peat bogs on a background insignificant, but constantly observable activity of iron bacteria, which formed iron hydroxides. Thirdly, owing to sorption (and insoluble calcium compounds in the bottom layers of a peat deposit) hydrooxides, phosphates and carbonates (possibly sulfates and sulfides) of some microelements, including rare earth elements, are precipitated on iron hydrooxides
Conditions of transformation of municipal wastewater in bog ecosystems (on the example of Obskoe bog, Western Siberia)
ΠΠΊΡΡΠ°Π»ΡΠ½ΠΎΡΡΡ. ΠΡΠΎΠ±Π»Π΅ΠΌΠ° ΠΎΡ
ΡΠ°Π½Ρ ΠΈ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ Π±ΠΎΠ»ΠΎΡ ΡΠ²Π»ΡΠ΅ΡΡΡ Π²Π΅ΡΡΠΌΠ° Π°ΠΊΡΡΠ°Π»ΡΠ½ΠΎΠΉ Π²ΠΎ Π²ΡΠ΅ΠΌ ΠΌΠΈΡΠ΅, Π² ΡΠΎΠΌ ΡΠΈΡΠ»Π΅ Π² ΠΠ°ΠΏΠ°Π΄Π½ΠΎΠΉ Π‘ΠΈΠ±ΠΈΡΠΈ, Π½Π° ΡΠ΅ΡΡΠΈΡΠΎΡΠΈΠΈ ΠΊΠΎΡΠΎΡΠΎΠΉ Π΄ΠΎΠ±ΡΠ²Π°Π΅ΡΡΡ Π·Π½Π°ΡΠΈΡΠ΅Π»ΡΠ½Π°Ρ ΡΠ°ΡΡΡ ΡΠ³Π»Π΅Π²ΠΎΠ΄ΠΎΡΠΎΠ΄Π½ΠΎΠ³ΠΎ ΡΡΡΡΡ Π² Π ΠΎΡΡΠΈΠΉΡΠΊΠΎΠΉ Π€Π΅Π΄Π΅ΡΠ°ΡΠΈΠΈ, ΡΡΠΎ ΡΠΎΠΏΡΠΎΠ²ΠΎΠΆΠ΄Π°Π΅ΡΡΡ ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΠ΅ΠΌ ΠΎΠΊΡΡΠΆΠ°ΡΡΠ΅ΠΉ ΡΡΠ΅Π΄Ρ, Π² ΡΠΎΠΌ ΡΠΈΡΠ»Π΅ ΠΈ Π±ΠΎΠ»ΠΎΡΠ½ΡΡ
ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌ. Π ΡΠ²ΠΎΡ ΠΎΡΠ΅ΡΠ΅Π΄Ρ, ΡΡΠΎ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΠ΅Ρ Π½Π΅ΠΎΠ±Ρ
ΠΎΠ΄ΠΈΠΌΠΎΡΡΡ ΡΠ°Π·ΡΠ°Π±ΠΎΡΠΊΠΈ ΠΌΠ΅ΡΠΎΠ΄ΠΎΠ»ΠΎΠ³ΠΈΠΈ ΠΈ ΡΠ΅Ρ
Π½ΠΎΠ»ΠΎΠ³ΠΈΠΉ ΠΏΡΠΈΡΠΎΠ΄ΠΎΠΎΡ
ΡΠ°Π½Π½ΡΡ
ΠΌΠ΅ΡΠΎΠΏΡΠΈΡΡΠΈΠΉ Π½Π° Π±ΠΎΠ»ΠΎΡΠ°Ρ
, ΠΏΠΎΠ΄Π²Π΅ΡΠ³Π°ΡΡΠΈΡ
ΡΡ Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π½ΠΎΠΌΡ Π²ΠΎΠ·Π΄Π΅ΠΉΡΡΠ²ΠΈΡ. Π ΡΠ°ΠΌΠΊΠ°Ρ
ΡΠ°ΠΊΠΎΠΉ ΠΌΠ΅ΡΠΎΠ΄ΠΎΠ»ΠΎΠ³ΠΈΠΈ ΡΡΠ΅Π±ΡΠ΅ΡΡΡ Π΄ΠΎΡΡΠΎΠ²Π΅ΡΠ½Π°Ρ ΠΎΡΠ΅Π½ΠΊΠ° ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΠΉ ΡΠΎΡΡΠΎΡΠ½ΠΈΡ Π±ΠΎΠ»ΠΎΡΠ½ΠΎΠΉ ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΡ ΠΏΠΎΠ΄ Π²Π»ΠΈΡΠ½ΠΈΠ΅ΠΌ ΠΏΠΎΡΡΡΠΏΠ»Π΅Π½ΠΈΡ Π²Π΅ΡΠ΅ΡΡΠ² Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π½ΠΎΠ³ΠΎ ΠΏΡΠΎΠΈΡΡ
ΠΎΠΆΠ΄Π΅Π½ΠΈΡ. Π¦Π΅Π»Ρ: Π°Π½Π°Π»ΠΈΠ· ΠΈ ΠΎΠ±ΠΎΡΠ½ΠΎΠ²Π°Π½ΠΈΠ΅ ΡΡΠ»ΠΎΠ²ΠΈΠΉ ΡΡΠ°Π½ΡΡΠΎΡΠΌΠ°ΡΠΈΠΈ ΠΊΠΎΠΌΠΌΡΠ½Π°Π»ΡΠ½ΠΎ-Π±ΡΡΠΎΠ²ΡΡ
ΡΡΠΎΡΠ½ΡΡ
Π²ΠΎΠ΄ Π² Π½ΠΈΠ·ΠΈΠ½Π½ΠΎΠΌ Π±ΠΎΠ»ΠΎΡΠ΅ Π½Π° ΠΏΡΠΈΠΌΠ΅ΡΠ΅ ΡΠΈΠΏΠΈΡΠ½ΠΎΠ³ΠΎ Π΄Π»Ρ ΠΠ°ΠΏΠ°Π΄Π½ΠΎΠΉ Π‘ΠΈΠ±ΠΈΡΠΈ Π΅Π²ΡΡΠΎΡΠ½ΠΎΠ³ΠΎ ΠΠ±ΡΠΊΠΎΠ³ΠΎ Π±ΠΎΠ»ΠΎΡΠ°. ΠΠ΅ΡΠΎΠ΄Ρ. Π₯ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΠΉ ΠΈ ΠΌΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΠΉ ΡΠΎΡΡΠ°Π²Ρ Π²ΠΎΠ΄ ΠΈ ΡΠΎΡΡΠΎΠ² ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π»ΠΈΡΡ Π² ΠΡΠΎΠ±Π»Π΅ΠΌΠ½ΠΎΠΉ Π½Π°ΡΡΠ½ΠΎ-ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°ΡΠ΅Π»ΡΡΠΊΠΎΠΉ Π»Π°Π±ΠΎΡΠ°ΡΠΎΡΠΈΠΈ Π³ΠΈΠ΄ΡΠΎΠ³Π΅ΠΎΡ
ΠΈΠΌΠΈΠΈ (Π’ΠΠ£), Π·Π°ΡΠ΅Π³ΠΈΡΡΡΠΈΡΠΎΠ²Π°Π½Π½ΠΎΠΉ Π² Π‘ΠΈΡΡΠ΅ΠΌΠ΅ Π°Π½Π°Π»ΠΈΡΠΈΡΠ΅ΡΠΊΠΈΡ
Π»Π°Π±ΠΎΡΠ°ΡΠΎΡΠΈΠΉ ΠΠΎΡΡΡΠ°Π½Π΄Π°ΡΡΠ° Π ΠΎΡΡΠΈΠΈ. ΠΠ»Ρ ΠΏΡΠΎΠ²Π΅Π΄Π΅Π½ΠΈΡ ΠΏΠΎΠ»Π½ΠΎΠ³ΠΎ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ Π°Π½Π°Π»ΠΈΠ·Π° ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π»ΠΈΡΡ ΡΡΠ°Π΄ΠΈΡΠΈΠΎΠ½Π½ΡΠ΅ ΠΌΠ΅ΡΠΎΠ΄Ρ. ΠΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΠΉ Π°Π½Π°Π»ΠΈΠ· ΠΏΡΠΎΠΈΠ·Π²ΠΎΠ΄ΠΈΠ»ΠΈ ΠΏΠΎΡΠ»Π΅ ΠΎΡΠ±ΠΎΡΠ° ΠΏΡΠΎΠ±, ΠΊΠ°ΠΊ ΠΏΡΠ°Π²ΠΈΠ»ΠΎ, Π² ΡΠ΅ΡΠ΅Π½ΠΈΠ΅ ΡΡΡΠΎΠΊ. ΠΠΎΡΡΠ°Π²ΠΊΠ° ΠΏΡΠΎΠ± Π² Π»Π°Π±ΠΎΡΠ°ΡΠΎΡΠΈΡ ΠΎΡΡΡΠ΅ΡΡΠ²Π»ΡΠ»Π°ΡΡ Π² ΡΡΠΌΠΊΠ΅-Ρ
ΠΎΠ»ΠΎΠ΄ΠΈΠ»ΡΠ½ΠΈΠΊΠ΅. ΠΠ»Ρ Π²ΡΡΠ²Π»Π΅Π½ΠΈΡ ΠΌΠΈΠΊΡΠΎΠΎΡΠ³Π°Π½ΠΈΠ·ΠΌΠΎΠ² ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π»ΠΈ ΠΆΠΈΠ΄ΠΊΠΈΠ΅ ΠΈ ΡΠ²Π΅ΡΠ΄ΡΠ΅ ΡΠ»Π΅ΠΊΡΠΈΠ²Π½ΡΠ΅ ΠΏΠΈΡΠ°ΡΠ΅Π»ΡΠ½ΡΠ΅ ΡΡΠ΅Π΄Ρ. ΠΠΈΠΊΡΠΎΠΊΠΎΠΌΠΏΠΎΠ½Π΅Π½ΡΠ½ΡΠΉ ΡΠΎΡΡΠ°Π² ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΠ»ΡΡ ΠΏΡΠΈ ΠΏΠΎΠΌΠΎΡΠΈ ΠΌΠ°ΡΡ-ΡΠΏΠ΅ΠΊΡΡΠΎΠΌΠ΅ΡΡΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ ΠΌΠ΅ΡΠΎΠ΄Π° Ρ ΠΈΠ½Π΄ΡΠΊΡΠΈΠ²Π½ΠΎ-ΡΠ²ΡΠ·Π°Π½Π½ΠΎΠΉ ΠΏΠ»Π°Π·ΠΌΠΎΠΉ (ICP-MS). Π‘ΡΡΡΠΊΡΡΡΠ½ΠΎ-Π³ΡΡΠΏΠΏΠΎΠ²ΠΎΠΉ ΡΠΎΡΡΠ°Π² ΡΠ°ΡΡΠ²ΠΎΡΠ΅Π½Π½ΡΡ
ΠΎΡΠ³Π°Π½ΠΈΡΠ΅ΡΠΊΠΈΡ
Π²Π΅ΡΠ΅ΡΡΠ² ΠΈΠ·ΡΡΠ°Π»ΡΡ ΠΌΠ΅ΡΠΎΠ΄ΠΎΠΌ Ρ
ΡΠΎΠΌΠ°ΡΠΎ-ΠΌΠ°ΡΡ-ΡΠΏΠ΅ΠΊΡΡΠΎΠΌΠ΅ΡΡΠΈΠΈ Π² Π»Π°Π±ΠΎΡΠ°ΡΠΎΡΠΈΠΈ ΡΠ°Π·ΡΠ°Π±ΠΎΡΠΊΠΈ ΠΌΠ΅ΡΡΠΎΡΠΎΠΆΠ΄Π΅Π½ΠΈΠΉ Π½Π΅ΡΡΠΈ ΠΈ Π³Π°Π·Π° (Π’ΠΠ£). ΠΠ»Ρ ΠΈΠ·ΡΡΠ΅Π½ΠΈΡ Π³ΠΈΠ΄ΡΠΎΠ³Π΅ΠΎΡ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΡ
ΠΏΡΠΎΡΠ΅ΡΡΠΎΠ² ΠΏΡΠΈΠΌΠ΅Π½ΡΠ»ΠΈΡΡ ΡΡΠ°ΡΠΈΡΡΠΈΡΠ΅ΡΠΊΠΈΠ΅ ΠΌΠ΅ΡΠΎΠ΄Ρ ΠΈ ΠΌΠ°ΡΠ΅ΠΌΠ°ΡΠΈΡΠ΅ΡΠΊΠΎΠ΅ ΠΌΠΎΠ΄Π΅Π»ΠΈΡΠΎΠ²Π°Π½ΠΈΠ΅. Π Π΅Π·ΡΠ»ΡΡΠ°ΡΡ ΠΈ Π²ΡΠ²ΠΎΠ΄Ρ. Π£ΡΡΠ°Π½ΠΎΠ²Π»Π΅Π½ΠΎ, ΡΡΠΎ Π±ΠΎΠ»ΠΎΡΠ½ΡΠ΅ Π²ΠΎΠ΄Ρ ΠΎΡΠ½ΠΎΡΠΈΡΠ΅Π»ΡΠ½ΠΎ ΠΠΠ Ρ
Π°ΡΠ°ΠΊΡΠ΅ΡΠΈΠ·ΡΡΡΡΡ ΠΏΠΎΠ²ΡΡΠ΅Π½Π½ΡΠΌΠΈ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΡΠΌΠΈ ΠΎΡΠ³Π°Π½ΠΈΡΠ΅ΡΠΊΠΈΡ
Π²Π΅ΡΠ΅ΡΡΠ², ΠΏΡΠΎΠ΄ΡΠΊΡΠΎΠ² ΠΈΡ
ΡΡΠ°Π½ΡΡΠΎΡΠΌΠ°ΡΠΈΠΈ, Π° ΡΠ°ΠΊΠΆΠ΅ Π½Π΅ΠΊΠΎΡΠΎΡΡΡ
Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ², Ρ ΠΊΠΎΡΠΎΡΡΠΌΠΈ ΠΎΡΠ³Π°Π½ΠΈΡΠ΅ΡΠΊΠΈΠ΅ Π²Π΅ΡΠ΅ΡΡΠ²Π° ΡΠΏΠΎΡΠΎΠ±Π½Ρ ΠΎΠ±ΡΠ°Π·ΠΎΠ²ΡΠ²Π°ΡΡ ΠΊΠΎΠΌΠΏΠ»Π΅ΠΊΡΡ. Π‘ΡΠ΅Π΄ΠΈ ΡΠ°ΡΡΠ²ΠΎΡΠ΅Π½Π½ΡΡ
ΠΎΡΠ³Π°Π½ΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠΎΠ΅Π΄ΠΈΠ½Π΅Π½ΠΈΠΉ Π² Π±ΠΎΠ»ΠΎΡΠ½ΡΡ
Π²ΠΎΠ΄Π°Ρ
Π΄ΠΎΠΌΠΈΠ½ΠΈΡΡΡΡ ΡΠ»ΠΎΠΆΠ½ΡΠ΅ ΡΡΠΈΡΡ, ΠΊΠ°ΡΠ±ΠΎΠ½ΠΎΠ²ΡΠ΅ ΠΊΠΈΡΠ»ΠΎΡΡ, ΠΊΠΎΡΠΎΡΡΠ΅ ΡΠΏΠΎΡΠΎΠ±ΡΡΠ²ΡΡΡ Π½Π΅ ΡΠΎΠ»ΡΠΊΠΎ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ Π½Π΅ΠΊΠΎΡΠΎΡΡΡ
ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² (Ni, Ba) Π² Π²ΠΎΠ΄Π°Ρ
, Π½ΠΎ ΠΈ ΡΠ°Π·Π²ΠΈΡΠΈΡ ΠΌΠΈΠΊΡΠΎΠΎΡΠ³Π°Π½ΠΈΠ·ΠΌΠΎΠ². ΠΠΎΠΊΠ°Π·Π°Π½ΠΎ, ΡΡΠΎ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΠ΅ Π²Π΅ΡΠ΅ΡΡΠ², ΠΏΠΎΡΡΡΠΏΠ°ΡΡΠΈΡ
Ρ ΠΊΠΎΠΌΠΌΡΠ½Π°Π»ΡΠ½ΠΎ-Π±ΡΡΠΎΠ²ΡΠΌΠΈ ΡΡΠΎΡΠ½ΡΠΌΠΈ Π²ΠΎΠ΄Π°ΠΌΠΈ Ρ. ΠΠ΅Π»ΡΠ½ΠΈΠΊΠΎΠ²ΠΎ, ΠΏΡΠΎΠΈΡΡ
ΠΎΠ΄ΠΈΡ Π² ΠΎΡΠ½ΠΎΠ²Π½ΠΎΠΌ Π½Π° Π³ΡΠ°Π½ΠΈΡΠ΅ Π΄Π΅ΡΡΠ΅Π»ΡΠ½ΠΎΠ³ΠΎ ΠΈ ΠΈΠ½Π΅ΡΡΠ½ΠΎΠ³ΠΎ Π³ΠΎΡΠΈΠ·ΠΎΠ½ΡΠΎΠ² ΡΠΎΡΡΡΠ½ΠΎΠΉ Π·Π°Π»Π΅ΠΆΠΈ. ΠΠΎΠΊΠ°Π·Π°Π½ΠΎ, ΡΡΠΎ ΡΠ±ΡΠΎΡ ΠΊΠΎΠΌΠΌΡΠ½Π°Π»ΡΠ½ΠΎ-Π±ΡΡΠΎΠ²ΡΡ
ΡΡΠΎΡΠ½ΡΡ
Π²ΠΎΠ΄ Π² Π±ΠΎΠ»ΠΎΡΠΎ (Ρ. ΠΠ΅Π»ΡΠ½ΠΈΠΊΠΎΠ²ΠΎ) Π½Π΅ ΠΏΡΠΈΠ²ΠΎΠ΄ΠΈΡ ΠΊ ΡΡΡΠ΅ΡΡΠ²Π΅Π½Π½ΠΎΠΌΡ ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΡ Ρ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ ΡΠΎΡΡΠ°Π²Π° Π±ΠΎΠ»ΠΎΡΠ½ΡΡ
Π²ΠΎΠ΄, Π° Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π½ΠΎΠ΅ Π²ΠΎΠ·Π΄Π΅ΠΉΡΡΠ²ΠΈΠ΅ Π»ΠΈΠΌΠΈΡΠΈΡΡΠ΅ΡΡΡ ΠΌΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΠΌΠΈ ΠΈ Π³Π΅ΠΎΡ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΈΠΌΠΈ ΡΡΠ»ΠΎΠ²ΠΈΡΠΌΠΈ Π² Π±ΠΎΠ»ΠΎΡΠ΅. ΠΠ° ΠΎΡΠ½ΠΎΠ²Π΅ ΠΏΠΎΠ»ΡΡΠ΅Π½Π½ΡΡ
Π΄Π°Π½Π½ΡΡ
ΠΏΡΠ΅Π΄Π»ΠΎΠΆΠ΅Π½ΠΎ ΡΠΊΠΎΡΡΠ΅ΠΊΡΠΈΡΠΎΠ²Π°ΡΡ ΠΏΡΠΈΡΠΎΠ΄ΠΎΠΎΡ
ΡΠ°Π½Π½ΡΠ΅ ΠΌΠ΅ΡΠΎΠΏΡΠΈΡΡΠΈΡ, ΠΎΠ³ΡΠ°Π½ΠΈΡΠΈΠ²Π°ΡΡΠΈΠ΅ ΡΠΎΡΡ Π·Π°Π±ΠΎΠ»ΠΎΡΠ΅Π½Π½ΠΎΡΡΠΈ ΡΠ΅ΡΡΠΈΡΠΎΡΠΈΠΉ Π·Π° ΡΡΠ΅Ρ ΡΠ²Π΅Π»ΠΈΡΠ΅Π½ΠΈΡ Π»Π΅ΡΠ½ΡΡ
ΡΠ³ΠΎΠ΄ΠΈΠΉ Π²ΡΠ»Π΅Π΄ΡΡΠ²ΠΈΠ΅ ΠΎΡΡΡΠΈΡΠ΅Π»ΡΠ½ΡΡ
ΠΌΠ΅Π»ΠΈΠΎΡΠ°ΡΠΈΠΉ ΠΈ Π΄ΠΎΠΏΠΎΠ»Π½ΠΈΡΠ΅Π»ΡΠ½ΠΎΠ³ΠΎ Π²Π½Π΅ΡΠ΅Π½ΠΈΡ ΡΠΎΠ΅Π΄ΠΈΠ½Π΅Π½ΠΈΠΉ Π°Π·ΠΎΡΠ° ΠΈ ΠΊΠ°Π»ΡΡΠΈΡ, Π²Ρ
ΠΎΠ΄ΡΡΠΈΡ
Π² ΡΠΎΡΡΠ°Π² ΡΡΠΎΡΠ½ΡΡ
Π²ΠΎΠ΄ ΠΆΠΈΠ»ΠΈΡΠ½ΠΎ-ΠΊΠΎΠΌΠΌΡΠ½Π°Π»ΡΠ½ΠΎΠ³ΠΎ Ρ
ΠΎΠ·ΡΠΉΡΡΠ²Π° ΠΈ Π½Π΅ΡΡΠ΅Π³Π°Π·ΠΎΠ΄ΠΎΠ±ΡΠ²Π°ΡΡΠ΅Π³ΠΎ ΠΊΠΎΠΌΠΏΠ»Π΅ΠΊΡΠ°.Relevance. The issue of conservation and use of bogs is very urgent throughout the world, including Western Siberia, where a large part of hydrocarbon raw materials in the Russian Federation are extracted. It is accompanied by environmental changes, which concern bog ecosystems. This determines the relevance to develop a methodology and technology for environmental protection of bog ecosystems subjected to anthropogenic impact. For this methodology, a reliable assessment of changes in the bog ecosystem under the influence of the influx of substances of anthropogenic origin is required. The aim of the research is to analyze and interprete the conditions of municipal wastewater transformation in lowland bog on the example of typical Western Siberian eutrophic bog Obskoe. Methods. Chemical and microbiological composition of natural waters were analyzed in the Fundamental research laboratory of hydroge-ochemistry (TPU), which is registered in the System of analytical laboratories of Gosstandart of Russia. To carry out the comprehensive chemical analysis the authors applied the traditional methods. The microbiological analysis was carried out after sampling, basically during the day. The samples had been kept in the cooling bag until they were delivered to the laboratory. To identify the microorganisms the authors used liquid and firm elective nutrient mediums. The trace elements were determined by inductively coupled plasma mass-pectrometry (ICP-MS). The structural-group composition of dissolved organic matter was determined by gas chromatography-mass spectrometry method. Statistical methods and mathematical modeling were applied to study hydrogeochemical processes. Results and conclusions. It was found that the bog waters are characterized by high contents (relative to maximum permissible concentrations) of organic matters, products of their transformation, as well as some chemical elements, which are able to form complexes with organic matters. Among the dissolved organic compounds esters, carboxylic acids are dominated in the bog waters. They contribute not only to accumulation of certain elements (Ni, Ba) in the waters but to development of microorganisms as well. It was shown, that accumulation of the elements entering the bog waters from municipal wastewater of Melnikovo settlement takes place mainly on the boundary of active and inert horizons of the peat deposit. It was shown, that the discharge of municipal wastewater to the bog near Melnikovo settlement does not significantly change the chemical composition of the bog waters, and anthropogenic impact is limited by microbiological and geochemical conditions of the bog. Based on the data obtained, it was proposed to adjust environmental measures to limit the expansion of boggy areas by the increase in forest land due to drainage reclamation and the addition of nitrogen and calcium compounds that are part of municipal wastewater and wastewater of oil and gas industry