8 research outputs found
Influence of Copper Pollution of Haplic Calcic Chernozem With Various Contents of Sand Fractions on Morphobiometric Indicators of Spring Barley
The growth and development of plants is one of the criteria for assessing the degree of soil pollution with heavy metals. Morphological and anatomical changes in test plants affected by pollutants, such as growth retardation, shoot bending, and decreased root length and mass, indicate the worsening of environmental conditions. The effect of various ratios of soil and sand polluted with copper (Cu) on morphobiometric parameters of spring barley (Hordeum sativum distichum), Ratnik variety, was studied in a model vegetative experiment. Haplic calcic chernozem was used as a substrate with different ratios of soil/sand. It was determined that an addition of sand into the soil in the amounts of 25%, 50% and 75% of soil mass resulted in the alteration of the physical properties of the chernozem, which was reflected in the morphometric parameters of the plants. The most notable changes in the parameters were observed after pollution of soil-sand substrates with Cu(CH3COO)2 in the amounts of 250 mg/kg, 500 mg/kg, 1000 mg/kg and 2000 mg/kg. The maximum growth and development retardation of the barley plants was found at the maximum content of sand and the maximum concentration of Cu. The pollutant reduced the root length and, to a lesser degree, the height of the aboveground components of the plant, which as a result, decreased the total plant biomass.
Keywords: trace elements, soil, agricultural crops, particle size distributio
Main factors in polycyclic aromatic hydrocarbons accumulations in the long-term technogenic contaminated soil
The PAHs transformation in the soils of the coal mining enterprises impact zones and thermal power plants remains poorly studied. In turn, coal mining can be considered as a primary cycle in the production of electricity. One of the main sources of negative environmental impact is the coal mining industry located on the territory of the upland in the south of the East European Plain. The features of PAHs accumulation in the soils of fuel and energy enterprises have been studied on the example of mines impact zones with different service life and the current coal-fired power plant. It was established that, regardless of the period and intensity of the emission source, as well as its current status, the polycyclic aromatic hydrocarbons (PAHs) content in the soils of the impact zones was significantly higher than in the soils of the background territory. The content of low molecular and high molecular weight PAHs in the impact zones soils differed depending on the land use type, as well as the period and intensity of an industrial effect type. The pollutants content of in the soils of all considered impact zones significantly exceeded the background values and according to the low molecular weight PAHs content in the soils, they formed the following decreasing series: Mayskiy β₯ Ayutinsky > Novoshahtinsk > Power station > Background. According the high molecular weight PAHs content, the series changed to: Novoshahtinsk >Mayskiy β₯ Ayutinsky > Power station > Background. Soil pollution markers for enterprises of the fuel and energy complex were identified as pyrene and chrysene, which are part of coal, formed from the hydrocarbon sources. The influence of the power plant was accompanied by the benzo(g,h,i)perylene concentration increase
The influence of diatomite on the growth and development of
The effect of various doses of diatomite introduced into soil artificially contaminated by benzo[a]pyrene was analyzed. The negative effect of benzo[a]pyrene on the growth of barley (Hordeum sativum distichum) seedlings and reduction of toxic effect of polyarene on plants after implementation of diatomite as a sorbent into contaminated soil are shown. A significant increase (by 2β3 times) of the plant growth in contaminated soil with the addition of diatomite has been revealed. The introduction of 2.5% diatomite into contaminated soil had the significant positive effect on barley seedlings
The Morphological and Functional Organization of Cattails <em>Typha laxmannii</em> Lepech. and <em>Typha australis</em> Schum. and Thonn. under Soil Pollution by Potentially Toxic Elements
The aim of this study is to investigate the adaptation of two species of cattail Typha australis Schum. and Thonn. and Typha laxmannii Lepech. based on analysis of the morphological and anatomical features of their vegetative and generative organs to soil pollution with potentially toxic elements (PTE) in the riparian zones of the sea edge of the Don River delta (Southern Russia). Both species of the cattail are able to accumulate high concentrations of Ni, Zn, Cd, Pb and can be used for phytoremediation of polluted territories. The pattern of PTE accumulation in hydrophytes has changed on polluted soils of coastal areas from roots/rhizomes > inflorescences > stems to roots/rhizomes > stems β₯ inflorescences. The comparative morphological and anatomical analysis showed a statistically significant effect of the environmental stress factor by the type of proliferation in T. australis, and species T. laxmannii was visually in a depressed, deformed state with mass manifestations of hypogenesis. These deformations should be considered, on one hand, as adaptive, but on the other, as pathological changes in the structure of the spikes of the cattails. Light-optical and electron microscopic studies have shown that the degree and nature of ultrastructural changes in cattails at the same level of soil pollution are different and most expressed in the assimilation tissue of leaves. However, these changes were destructive for T. australis, but for T. laxmannii, these indicated a high level of adaptation to the prolonged technogenic impact of PTE
Establishment of regional background for heavy metals in the soils of the Lower Don and the Taganrog Bay coast
Data on the regional geochemical background and threshold values of heavy metals are required to establish anomalies and assess soil pollution. As a rule, the background values are the average contents of elements in natural undisturbed soils, or the threshold values for the study area, obtained by statistical methods. The aim of the study is to obtain geochemical threshold values of heavy metals in the soils of the Lower Don and the Taganrog Bay coast using different statistical approaches. A total of 86 topsoil samples were collected from the study area. The concentrations of Cr, Mn, Ni, Π‘u, Zn, As, Cd, and Pb were analyzed by X-ray fluorescence. The median element concentrations in the soils of the study area were consistent with world soil average and metal concentrations in background soils of protected area. Using a βgeochemicalβ approach is not suitable for this dataset because it does not take into account the natural variability of concentrations in different soil types. The Tukey inner fence method delivers estimates that do not detect outliers for Ni, As, Cd, and Pb. The βmedian + 2 median absolute deviationsβ method was the most appropriate, as it consistently provided the most conservative background values
Accumulation of benzo[a]pyrene in plants of different species and organogenic horizon of soils of steppe phytocenosis under technogenic pollution
ΠΠΊΡΡΠ°Π»ΡΠ½ΠΎΡΡΡ. ΠΠ΅ΡΠΌΠΎΡΡΡ Π½Π° Π·Π½Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎΠ΅ ΠΊΠΎΠ»ΠΈΡΠ΅ΡΡΠ²ΠΎ ΡΠ°Π±ΠΎΡ ΠΏΠΎ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΡ ΠΎΠ±ΡΠ΅ΠΊΡΠΎΠ² ΠΎΠΊΡΡΠΆΠ°ΡΡΠ΅ΠΉ ΡΡΠ΅Π΄Ρ ΠΏΠΎΠ»ΠΈΠ°ΡΠ΅Π½Π°ΠΌΠΈ, Π½Π΅Π΄ΠΎΡΡΠ°ΡΠΎΡΠ½ΠΎ ΡΠ²Π΅Π΄Π΅Π½ΠΈΠΉ ΠΎ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΠΈ ΠΏΠΎΠ»ΠΈΡΠΈΠΊΠ»ΠΈΡΠ΅ΡΠΊΠΈΡ
Π°ΡΠΎΠΌΠ°ΡΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠ³Π»Π΅Π²ΠΎΠ΄ΠΎΡΠΎΠ΄ΠΎΠ² ΠΈ, Π² ΡΠ°ΡΡΠ½ΠΎΡΡΠΈ, Π½Π°ΠΈΠ±ΠΎΠ»Π΅Π΅ ΡΠΎΠΊΡΠΈΡΠ½ΠΎΠ³ΠΎ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° ΡΠ°Π·Π½ΡΠΌΠΈ Π²ΠΈΠ΄Π°ΠΌΠΈ ΡΡΠ°Π²ΡΠ½ΠΈΡΡΡΡ
ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ, ΡΡΠΎ ΠΎΠ±ΡΡΠ»ΠΎΠ²Π»ΠΈΠ²Π°Π΅Ρ Π°ΠΊΡΡΠ°Π»ΡΠ½ΠΎΡΡΡ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΠΉ Π² Π΄Π°Π½Π½ΠΎΠΌ Π½Π°ΠΏΡΠ°Π²Π»Π΅Π½ΠΈΠΈ. ΠΡΠΎΠ²Π΅Π΄Π΅Π½ΠΎ ΠΈΠ·ΡΡΠ΅Π½ΠΈΠ΅ ΡΠ°ΡΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΡ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° ΠΏΠΎ ΠΎΡΠ³Π°Π½Π°ΠΌ ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ ΠΈ ΠΎΡΠ³Π°Π½ΠΎΠ³Π΅Π½Π½ΡΠΌ Π³ΠΎΡΠΈΠ·ΠΎΠ½ΡΠ°ΠΌ ΠΏΠΎΡΠ² Π·ΠΎΠ½Ρ Π²ΠΎΠ·Π΄Π΅ΠΉΡΡΠ²ΠΈΡ ΠΠΎΠ²ΠΎΡΠ΅ΡΠΊΠ°ΡΡΠΊΠΎΠΉ ΠΠ ΠΠ‘. Π¦Π΅Π»Ρ: Π²ΡΡΠ²ΠΈΡΡ Π·Π°ΠΊΠΎΠ½ΠΎΠΌΠ΅ΡΠ½ΠΎΡΡΠΈ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° Π² ΡΠ°ΡΡΠ΅Π½ΠΈΡΡ
ΡΠ°Π·Π½ΡΡ
Π²ΠΈΠ΄ΠΎΠ² ΠΈ ΠΎΡΠ³Π°Π½ΠΎΠ³Π΅Π½Π½ΠΎΠΌ Π³ΠΎΡΠΈΠ·ΠΎΠ½ΡΠ΅ ΠΏΠΎΡΠ² ΡΡΠ΅ΠΏΠ½ΡΡ
ΡΠΈΡΠΎΡΠ΅Π½ΠΎΠ·ΠΎΠ² Π² Π·Π°Π²ΠΈΡΠΈΠΌΠΎΡΡΠΈ ΠΎΡ ΡΠ΄Π°Π»Π΅Π½ΠΈΡ ΠΎΡ ΠΠΎΠ²ΠΎΡΠ΅ΡΠΊΠ°ΡΡΠΊΠΎΠΉ ΠΠ ΠΠ‘. ΠΠ±ΡΠ΅ΠΊΡΡ. Π Π·ΠΎΠ½Π΅ Π΄Π΅ΠΉΡΡΠ²ΠΈΡ ΠΠΎΠ²ΠΎΡΠ΅ΡΠΊΠ°ΡΡΠΊΠΎΠΉ ΠΠ ΠΠ‘ Π±ΡΠ» ΠΏΡΠΎΠ²Π΅Π΄Π΅Π½ ΠΎΡΠ±ΠΎΡ ΠΏΡΠΎΠ± Π½Π°Π΄Π·Π΅ΠΌΠ½ΠΎΠΉ ΠΈ ΠΊΠΎΡΠ½Π΅Π²ΠΎΠΉ ΡΠ°ΡΡΠ΅ΠΉ ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ ΠΈ ΠΏΠΎΠ΄ΡΡΠΈΠ»Π°ΡΡΠΈΡ
ΠΈΡ
ΠΎΡΠ³Π°Π½ΠΎΠ³Π΅Π½Π½ΡΡ
Π³ΠΎΡΠΈΠ·ΠΎΠ½ΡΠΎΠ² ΠΏΠΎΡΠ² Π½Π° Π³Π»ΡΠ±ΠΈΠ½Ρ 0-20 ΡΠΌ. ΠΠ»Ρ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ Π½Π° ΠΌΠΎΠ½ΠΈΡΠΎΡΠΈΠ½Π³ΠΎΠ²ΡΡ
ΠΏΠ»ΠΎΡΠ°Π΄ΠΊΠ°Ρ
Π½Π°ΠΌΠΈ Π±ΡΠ»ΠΈ Π²ΡΠ±ΡΠ°Π½Ρ Π΄ΠΎΠΌΠΈΠ½Π°Π½ΡΠ½ΡΠ΅ Π²ΠΈΠ΄Ρ ΡΡΠ°Π²ΡΠ½ΠΈΡΡΡΡ
ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ: Π°ΠΌΠ±ΡΠΎΠ·ΠΈΡ ΠΏΠΎΠ»ΡΠ½Π½ΠΎΠ»ΠΈΡΡΠ½Π°Ρ (Ambrosia artemisiifolia L.), ΠΏΠΎΠ»ΡΠ½Ρ Π°Π²ΡΡΡΠΈΠΉΡΠΊΠ°Ρ (Artemisia austriaca Jack.), ΡΡΡΡΡΠ΅Π»ΠΈΡΡΠ½ΠΈΠΊ Π±Π»Π°Π³ΠΎΡΠΎΠ΄Π½ΡΠΉ (Achillea nobilis L), ΡΠΈΠΊΠΎΡΠΈΠΉ ΠΎΠ±ΡΠΊΠ½ΠΎΠ²Π΅Π½Π½ΡΠΉ (Cichorium intybus L.), ΠΏΠΈΠΆΠΌΠ° ΠΎΠ±ΡΠΊΠ½ΠΎΠ²Π΅Π½Π½Π°Ρ (Tanacetum vulgare L.), ΠΏΡΡΠ΅ΠΉ ΠΏΠΎΠ»Π·ΡΡΠΈΠΉ (Elytrigia repens (L.) Nevski.). Π’Π°ΠΊΠΆΠ΅ Π±ΡΠ»ΠΈ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½Ρ Π·Π»Π°ΠΊΠΎΠ²ΡΠ΅ ΠΊΡΠ»ΡΡΡΡΡ: ΠΎΠ²ΡΡΠ³ (Avena fatua), ΠΏΡΠ΅Π½ΠΈΡΠ° (Triticum aestivum L.), ΠΎΠ²Π΅Ρ (Avena sativa L.), ΠΎΠ²ΡΡΠ½ΠΈΡΠ° Π²Π°Π»Π»ΠΈΡΡΠΊΠ°Ρ, ΠΈΠ»ΠΈ ΡΠΈΠΏΡΠ°ΠΊ (Festuca valesiaca L.), ΡΡΠΎΡΡΠ½ΠΈΠΊ ΠΎΠ±ΡΠΊΠ½ΠΎΠ²Π΅Π½Π½ΡΠΉ (Phragmites australis L.), ΠΌΡΡΠ»ΠΈΠΊ Π»ΡΠ³ΠΎΠ²ΠΎΠΉ (Poap retense L.). ΠΠ΅ΡΠΎΠ΄Ρ. Π‘ΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° Π² ΠΎΠ±ΡΠ°Π·ΡΠ°Ρ
ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΠ»ΠΈ ΠΌΠΎΠ΄ΠΈΡΠΈΡΠΈΡΠΎΠ²Π°Π½Π½ΡΠΌ ΠΌΠ΅ΡΠΎΠ΄ΠΎΠΌ ΠΎΠΌΡΠ»Π΅Π½ΠΈΡ. ΠΠΎΠ΄ΠΈΡΠΈΠΊΠ°ΡΠΈΡ ΠΏΡΠ΅Π΄ΠΏΠΎΠ»Π°Π³Π°Π΅Ρ Π·Π°ΠΌΠ΅Π½Ρ ΡΡΠ΅Ρ
ΡΠ°Π·ΠΎΠ²ΠΎΠΉ ΡΠΊΡΡΡΠ°ΠΊΡΠΈΠΈ ΡΡΠΎΠΊΡΠΈΡΡΠ°Π½ΠΎΠΌ, ΡΠ²Π»ΡΡΡΠΈΠΌΡΡ ΠΏΡΠ΅ΠΊΡΡΡΠΎΡΠΎΠΌ, Π½Π° Π½-Π³Π΅ΠΊΡΠ°Π½. ΠΠ·Π²Π»Π΅ΡΠ΅Π½ΠΈΠ΅ ΠΏΠΎΠ»Π»ΡΡΠ°Π½ΡΠ° ΡΠ°ΡΡΠ²ΠΎΡΠΈΡΠ΅Π»Π΅ΠΌ ΠΏΡΠΎΠ²ΠΎΠ΄ΠΈΠ»ΠΈ ΠΏΠΎΡΠ»Π΅ ΡΠ΄Π°Π»Π΅Π½ΠΈΡ ΠΌΠ΅ΡΠ°ΡΡΠΈΡ
Π»ΠΈΠΏΠΈΠ΄Π½ΡΡ
ΠΌΠ°ΠΊΡΠΎΠΊΠΎΠΌΠΏΠΎΠ½Π΅Π½ΡΠΎΠ² ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ, ΠΏΡΠ΅Π΄Π²Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎ ΠΏΠΎΠ΄Π²Π΅ΡΠ³Π°Ρ ΠΊΠΈΠΏΡΡΠ΅Π½ΠΈΡ ΠΎΠ±ΡΠ°Π·Π΅Ρ Π² 2-% ΡΠ°ΡΡΠ²ΠΎΡΠ΅ Π³ΠΈΠ΄ΡΠΎΠΎΠΊΡΠΈΠ΄Π° ΠΊΠ°Π»ΠΈΡ. ΠΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΠ΅ ΠΊΠΎΠ½ΡΠ΅Π½ΡΡΠ°ΡΠΈΠΈ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° ΠΎΡΡΡΠ΅ΡΡΠ²Π»ΡΠ»ΠΈ Π½Π° Ρ
ΡΠΎΠΌΠ°ΡΠΎΠ³ΡΠ°ΡΠ΅ Agilent 1260 Ρ ΡΠ»ΡΠΎΡΠΈΠΌΠ΅ΡΡΠΈΡΠ΅ΡΠΊΠΈΠΌ Π΄Π΅ΡΠ΅ΠΊΡΠΎΡΠΎΠΌ. Π Π΅Π·ΡΠ»ΡΡΠ°ΡΡ. ΠΠ° ΠΎΡΠ½ΠΎΠ²Π°Π½ΠΈΠΈ ΠΊΠ»Π°ΡΡΠ΅ΡΠ½ΠΎΠ³ΠΎ Π°Π½Π°Π»ΠΈΠ·Π° Π²ΡΡΠ²Π»Π΅Π½Ρ ΡΡΠΈ Π³ΡΡΠΏΠΏΡ ΡΡΠ°Π²ΡΠ½ΠΈΡΡΡΡ
ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ ΠΏΠΎ ΡΡΠΎΠ²Π½Ρ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΡ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π°: ΡΠ»Π°Π±ΠΎΠ³ΠΎ, ΡΡΠ΅Π΄Π½Π΅Π³ΠΎ ΠΈ Π°ΠΊΡΠΈΠ²Π½ΠΎΠ³ΠΎ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ. ΠΠ°ΠΊΡΠΈΠΌΠ°Π»ΡΠ½ΡΠ΅ ΡΡΠΎΠ²Π½ΠΈ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° Π²ΡΡΠ²Π»Π΅Π½Ρ Π΄Π»Ρ ΡΠΈΠΏΡΠ°ΠΊΠ°, ΠΌΠΈΠ½ΠΈΠΌΠ°Π»ΡΠ½ΡΠ΅ Π΄Π»Ρ Π°ΠΌΠ±ΡΠΎΠ·ΠΈΠΈ. Π£ΡΡΠ°Π½ΠΎΠ²Π»Π΅Π½ΠΎ, ΡΡΠΎ ΠΌΠ°ΡΡΠΎΠ²Π°Ρ Π΄ΠΎΠ»Ρ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° Π² ΠΏΠΎΡΠ²Π°Ρ
ΠΈ ΡΠ°ΡΡΠ΅Π½ΠΈΡΡ
Π·Π°ΠΊΠΎΠ½ΠΎΠΌΠ΅ΡΠ½ΠΎ ΡΠ½ΠΈΠΆΠ°Π»Π°ΡΡ ΠΏΠΎ ΠΌΠ΅ΡΠ΅ ΡΠ΄Π°Π»Π΅Π½ΠΈΡ ΠΎΡ ΠΏΡΠ΅Π΄ΠΏΡΠΈΡΡΠΈΡ. ΠΠ°ΠΊΡΠΈΠΌΠ°Π»ΡΠ½ΠΎΠ΅ Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΠ΅ Π±ΡΠ»ΠΎ Π²ΡΡΠ²Π»Π΅Π½ΠΎ ΠΏΠΎ ΡΡΠ°Π½ΡΠ΅ΠΊΡΠ΅ Π³Π΅Π½Π΅ΡΠ°Π»ΡΠ½ΠΎΠ³ΠΎ Π½Π°ΠΏΡΠ°Π²Π»Π΅Π½ΠΈΡ, Π² 1,6 ΠΊΠΌ ΠΎΡ ΠΈΡΡΠΎΡΠ½ΠΈΠΊΠ°. ΠΠ°ΠΈΠΌΠ΅Π½Π΅Π΅ Π·Π°Π³ΡΡΠ·Π½Π΅Π½Π½ΡΠΌΠΈ Π±ΡΠ»ΠΈ ΠΏΠ»ΠΎΡΠ°Π΄ΠΊΠΈ, Π·Π°Π»ΠΎΠΆΠ΅Π½Π½ΡΠ΅ Π² Π²ΠΎΡΡΠΎΡΠ½ΠΎΠΌ Π½Π°ΠΏΡΠ°Π²Π»Π΅Π½ΠΈΠΈ. ΠΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΠ΅ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° Π² ΡΠ°Π·Π½ΡΡ
ΠΎΡΠ³Π°Π½Π°Ρ
ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ ΠΏΠΎΠΊΠ°Π·Π°Π»ΠΎ, ΡΡΠΎ Π½Π°ΠΈΠ±ΠΎΠ»ΡΡΠΈΠΌ Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΠ΅ΠΌ ΠΎΡΠ»ΠΈΡΠ°Π»ΠΈΡΡ ΠΊΠΎΡΠ½ΠΈ Π²ΡΠ΅Ρ
ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½Π½ΡΡ
Π²ΠΈΠ΄ΠΎΠ². ΠΠ°ΡΡΠΎΠ²Π°Ρ Π΄ΠΎΠ»Ρ Π±Π΅Π½Π·[Π°]ΠΏΠΈΡΠ΅Π½Π° Π² ΠΎΡΠ³Π°Π½ΠΎΠ³Π΅Π½Π½ΠΎΠΌ Π³ΠΎΡΠΈΠ·ΠΎΠ½ΡΠ΅ ΠΏΠΎΡΠ² Π·Π½Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎ ΠΏΡΠ΅Π²ΡΡΠ°Π»Π° Π΅Π³ΠΎ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ Π² ΡΠ°ΡΡΠ΅Π½ΠΈΡΡ
ΡΠ°Π·Π½ΡΡ
Π²ΠΈΠ΄ΠΎΠ².The relevance of the research. Despite a significant amount of research of environmental pollution by polyarenes, there is insufficient information on accumulation of polycyclic aromatic hydrocarbons, and in particular the most toxic benzo[a]pyrene, by various types of herbaceous plants, which determines the relevance of research in this direction. The distribution of benzo[a]pyrene over plant organs and organogenic horizons of soils in the Novocherkassk Power Station effect zone was studied. The main aim was to study the accumulation of benzo[a]pyrene in plants of different species and the organogenic soil horizon of steppe phytocenoses depending on the distance from Novocherkassk Power Station. Objects. In the coverage area of the Novocherkassk Power Station, the samples of the aerial and root parts of plants and the underlying soil horizons of the organogenic layers were taken to a depth of 0-20 cm. For the study on monitoring sites, dominant species of herbaceous plants: ragweed (Ambrosia artemisiifolia L.), Austrian wormwood (Artemisia austriaca Jack.), noble yarrow (Achillea nobilis L), common chicory (Cichorium intybus L.), common tansy (Tanacetum vulgare L.), creeping wheatgrass (Elytrigia repens (L.) Nevski.) were selected. The cereals: oatmeal (Avena fatua), wheat (Triticum aestivum L.), oats (Avena sativa L.), Wallis fescue or fescue (Festuca valesiaca L.), common reed (Phragmites australis L.), meadow bluegrass (Poap retense L.) were studied as well. Methods. The content of benzo[a]pyrene in plants was determined by the standard method RD 52.10.556-95 in a modification that allows removing interfering lipid macrocomponents of plants by saponification (saponification method). When benzo[a]pyrene was determined by the method of saponification, the saponifiable lipid fraction was initially removed in the samples by boiling the plant sample in an alcohol solution of alkali, followed by threefold extraction of benzo[a]pyrene with hexane. The basis for determination of benzo[a]pyrene in soils is the PND 16.1:2:2. 2:3. 39-03 technique. Quantitative determination of benzo[a]pyrene in the extract was carried out by high performance liquid chromatography. The results. Based on cluster analysis, three groups of herbaceous plants were identified by the level of benzo[a]pyrene content: weak, medium, and active accumulation. The maximum levels of benzo[a]pyrene accumulation were found for fescue, and the minimum for ragweed. It was found that the mass fraction of benzo[a]pyrene in soils and plants naturally decreased with distance from the enterprise. Maximum pollution was detected by the transect of the general direction, 1,6 km from the source. The least polluted sites were laid in the eastern direction. A study of polyarenes accumulation in different organs of plants showed that the roots of all the species studied differed the greatest pollution. The mass fraction of benzo[a]pyrene in the organogenic horizon of soils significantly exceeded its content in plants of various species