Environmental safety of the territory in the gas station zone
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IOP Conference Series: Earth and Environmental Science PAPER • OPEN ACCESS Environmental safety of the territory in the gas station zone To cite this article: G I Sarapulova 2021 IOP Conf. Ser.: Earth Environ. Sci. 808 012067 View the article online for updates and enhancements. This content was downloaded from IP address 46.4.80.155 on 26/09/2021 at 19:02
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 Environmental safety of the territory in the gas station zone G I Sarapulova Irkutsk National Research Technical University, 83, Lermontov st, Irkutsk, 666074, Russia E-mail: sara131@mail.ru Abstract. The article deals with the problem of ecological safety and ecological diagnostics of soils in the gas station zone located in the center of the city of Irkutsk. The factors of disruption of natural properties when polluted with oil products have been investigated. The physicochemical parameters of soils, integral indicators of the state have been analyzed, the violation of their natural properties has been revealed, the composition of the surface runoff from the object has been studied. Technogenic halos of oil products spreading outside the source of supply on the basis of GIS were obtained, the accumulation of oil products in the soil up to a distance of 250 m from the filling station was revealed. The results of the dynamic behavior of petroleum products, the methods of ecodiagnostics used can be the basis for determining the direction of the soil distribution of pollutants outside the hazardous facility. The sampling system around fuel stations will make it possible to build GIS maps of technogenic oil pollution fields and develop preventive environmental protection measures. The results obtained are of practical importance for the environmental management of the city, for the cadastral valuation of land, for adjusting the placement of transport routes and the network of gas stations. 1. Introduction The scale of pollution of the territory of cities and the deterioration of their ecological state is caused by an increase in the supply of oil products (OP) to the soil, the sources of which are vehicles and oil product supply facilities - gas stations and gas stations [1-3]. At modern filling stations with sealed equipment, the likelihood of underground fuel leaks is minimized. However, the number of spills at fuel dispensers and at the fuel discharge site remains high - up to 100 g per 1 ton of gasoline and 50 g per 1 ton of diesel fuel. The main sources of oil supply to soils from gas stations: Reservoirs with oil products (evaporation of oil products - "big and small breaths"), their overflow; Fuel dispensers (evaporation when filling car gas tanks); Accidental and unintentional spills of oil products on the territory of the filling station; Leaks of technological equipment and communications; Ventilation devices of industrial premises of gas stations; Disconnection of connections in technological connections and tank breakdowns; Pipeline accidents as a result of metal aging. Urban soils are a depository environment, reflect the processes of disruption of geochemical cycles, affect the formation of technogenic geochemical anomalies in anthropogenic landscapes, and serve as Content from this work may be used under the terms of the Creative Commons Attribution 3.0 licence. Any further distribution of this work must maintain attribution to the author(s) and the title of the work, journal citation and DOI. Published under licence by IOP Publishing Ltd 1
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 indicators of the ecological state of urbanized territories. Studying the patterns of accumulation and migration of petroleum products, identifying their lateral and intraprofile distribution, obtaining criteria for the ecological state of soils constitute the scientific aspect of these studies and are an urgent geoecological problem. In Russia, about 22 thousand gas stations are engaged in retail sales of fuel, which are objects of high environmental hazard [4-6]. The growth of the Russian car park is predicted from 41.5 million units. in 2009 up to 68.0 million units. In 2030 in accordance with the Transport Strategy of the Russian Federation for the period up to 2030. However, there is no systematic environmental monitoring of the city's soil pollution and monitoring of urban soils in the zone of influence of the gas station. Control of the oil content at the filling station is carried out only on the basis of the Maximum permissible concentration of oil vapors in the air of the working area of the space up to 2 meters above the level of the site. The development of control methods and means for detecting petroleum products, preventing, eliminating negative processes are necessary for the development of conceptual foundations and new approaches of geoecological science. However, despite the severity of the problem under consideration, many issues related to assessing the impact of oil pollution on the soil cover and identifying the mechanism of their transformation are still poorly understood. The purpose of our research is a geo-ecological assessment of the city's territories and obtaining new criteria, on the basis of which it is possible to assess the environmental safety of soils in the zone of influence of oil product supply facilities - gas stations, refineries, transportation. 2. Materials and methods A typical gas station in the center of the city of Irkutsk next to a passing motorway was chosen as the object of the study. This Siberian city with a population of over 600 thousand people is located in an area with relatively high environmental stress. The research methods used: field, a complex of physicochemical analyzes of soils, geochemical, statistical processing of empirical dependencies in Excel, modeling. Soil samples were taken in the summer in the dry period (August) in accordance with the compiled regular network, taking into account the landscape slope from the territory of the gas station: - in the organic layer (AO horizon 0-5 cm); - mineral layer (A2 horizon 10 cm); - horizon (B) 30 cm to the final root zone of herbaceous and shrubby plants. IR spectrometry was used to determine petroleum products in soils [7-8]. The extraction of petroleum products was carried out with carbon tetrachloride [9]. The end of the analysis is the chromatographic separation of petroleum products from associated organic compounds of other classes [10, 11]. As reference standards, we used background soils taken 20 km from the city in a known clean zone. The results of the survey of the territory in the zone of the gas station are presented along with the integral indicators: acid-base properties (pH) and the organic component of the soil Corg - the pyrogenic component of organic matter at 500 ⁰С. The pH values were determined potentiometrically. Organic carbon and Ntot were determined according to Tyurin. These characteristics determine the degree of fixation of the products of technogenesis in soils and their transformation. In solving the set tasks, the methodology of landscape, migration and technogenic principles of changing soil properties was used. 3. Results At the site of the filling station there are 4 horizontal fuel tanks with a capacity of 50 m3 and 4 dispensers with Genstar pistols. The diagram in figure 1 shows the points of taking soil samples for analysis for the content of petroleum products up to a distance of 250 m from the object. Table 1 shows the daily dynamics of petroleum products dispensed at the city gas station. 2
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 Figure 1. Layout of 4 tanks, 4 dispensers at gas stations and points for taking soil samples for analysis from the border of the industrial site. Table 1. Daily statistics of petrol station dispensing at gas stations. Gasoline AI 80 Gasoline AI-92 Diesel fuel Times of Day Number of cars liter Number of cars liter Number of cars liter 0900-1000 6 70 9 112 10 128 1000-1100 3 87 12 50 5 60 1100-1200 4 30 4 120 7 175 1200-1300 7 170 10 250 9 230 1300-1400 5 80 14 338 3 570 1400-1500 2 15 4 195 3 1650 1500-1600 4 58 3 700 9 1301 1600-1700 4 80 3 50 2 2120 1700-1800 6 65 9 320 9 23 1800-1900 3 100 18 855 17 1091 1900-2000 6 45 57 960 4 150 2000-2100 2 25 3 275 11 170 2100-2200 13 67 9 710 4 480 2200-2300 4 155 13 650 1 47 2300-2400 2 13 5 60 6 520 0000-0100 6 49 5 72 9 220 0100-0200 2 20 4 88 15 100 0200-0300 7 33 5 160 4 520 0300-0400 3 18 7 710 5 951 0400-0500 2 56 8 505 3 937 0500-0600 7 131 12 124 4 732 0600-0700 11 260 10 290 3 150 0700-0800 12 95 6 85 5 75 0800-0900 21 450 13 179 8 510 Total 142 2172 243 7858 156 12919 3
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 4. Discussion From the results of the analysis, it was revealed that the surface runoff from the territories of the filling station contains: • oil products - from 1.2 to 28.7 mg / l (MPC - 0.05 mg / l); • chlorides - up to 109 mg / l; • sulfates - up to 17 mg / l; • lead - up to 0.005 mg / l, copper - up to 0.05 mg / l, zinc - up to 0.08 mg / l. It should be emphasized that the system of state environmental control and monitoring of soil pollution in the gas station area is practically absent. The procedure for handling oily waste and methods for preventing secondary pollution of the environment is poorly developed. However, it should be noted that the composition of petroleum products contains such toxic substances as benz-a- prirene, benzene, styrene, toluene, xylene, etc. [12]. These substances are highly toxic and stable in any environment, have a low solubility and a high degree of absorption on the surface, and decompose within months and years even if the soil layer is enriched with organic matter and humic substances [13]. Their determination on the territories of filling stations, filling stations, oil depots, adjacent urban areas is not carried out, although these substances can form technogenic pollution fields on impact soils [14]. From the point of view of studying the impact on the geological environment, soil ecosystems and for assessing environmental hazard, such control is necessary. It is important to emphasize the special sensitivity of Siberian soils to technogenic impact, since the main soil component - organic matter - is represented in them by a very low content. But it is the organic component of the soil that is able to neutralize the harmful effects of toxic substances, in particular, oil products. Oil hydrocarbons interact with functional molecular groups and ligands of humic acids to form new structures of compounds, which contributes to the process of destruction and humification of oil-contaminated lands and, accordingly, to reduce environmental hazards. The antidote activity of humic compounds towards petroleum products is based on their ability to act as surface-active agents, complexing agents and safe molecular destructors. Despite the relevance of research in this area, there is practically no systematized information on the geoecological assessment of soil pollution by NP, the patterns of their migration in the environment, as well as their transformation issues with the assessment of their degradation products. Difficulties are caused by the multifactorial impact of NP and the specifics of their distribution in the soil system, which, for example, creates problems in the development of criteria for determining its permissible content [15-17]. It is known that the rate of decomposition of oil products in landscapes depends on many factors, including soil moisture, mechanical composition and temperature. A granulometric analysis was carried out, which revealed that the soil of the urban area in the zone of influence of the gas station consists of: • pebbles by 64%; • sand by 20.6%; • dust by 8.8%; • clays by 5.7%. It is quite obvious that in such conditions, oil products that have got into the soil can easily seep to a sufficiently large depth. According to hydrological studies, it was revealed that at the site of this gas station, groundwater is at a depth of 3.8 m. The soil moisture was determined, which is an insignificant value of W = 0.098, which contributes to the penetration of oil products into deeper soil layers. However, in the rainy season, the groundwater level rises. When oil spills and seeps into the soil layer, the entire volume of oil pollution uncontrollably collects on a certain area in the city center, concentrating on the water component (water barrier) of the watered soil. Analysis of water pollution in control wells drilled to determine the level of groundwater is not carried out. In addition, there is an areal washout of oil products in the direction of the slope of the industrial site into natural depressions of the urbanized landscape, where oil products are also accumulated. The most rapid decomposition of oil and oil products occurs at ± 100 ⁰C, but it slows down in sharply continental and cold climatic zones. Considering the number of cold months per year in Siberia and, in particular, in Irkutsk, one should not expect rapid destruction and transformation of oil products in the soil horizons of the city. Therefore, soil pollution with oil and oil products, especially 4
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 in the northern territories, is a problematic, environmentally hazardous and difficult to eliminate type of pollution. Ecological and geochemical analysis of soils revealed a deterioration in their nitrogen regime - the N content does not exceed 0.065–0.115%, the C / N ratio is increased to 25–50 (for natural clean soils it is not more than 10), the alkalinity is increased - pH 9–10 units. Together with a high carbonated nature (CO2 = 0.54%), a low humus content of 1.3%, an increased cation absorption capacity of up to 33.2 mg-eq / per 100 g, the results obtained are signs of a technogenic transformation of the natural soil properties in the gas station zone, which does not provide it protective buffering properties [18- 20]. As a result of work with the use of GIS, the aureoles of the distribution of oil products in the zone of influence of the city gas station were revealed. It can be seen that NPs migrate a considerable distance from the source of supply (figure 2). Figure 2. Distribution of oil products in the gas station area. The scale is labeled in mg / kg. 1-tanks, 2-gas stations, 3-office, 4-slope, 5-motorway. The results obtained convincingly showed that in urban landscapes in the gas station zone there are significant violations of the buffer properties of soils, a new ecogeochemical situation is formed with the formation of technogenic lateral zones with an anomalous distribution of oil products. It also forms secondary pollution of urban areas with unaccounted for toxic substances. 5. Conclusion Thus, on the basis of geoecological studies of the territory in the zone of influence of the gas station, methods of ecodiagnostics, modeling methods, new data on the dynamic behavior of petroleum products in soils were obtained, which makes it possible to reveal the picture of their soil distribution outside the hazardous facility. The scientific significance of the results of the work is that they expand the understanding of the mechanism of violation of the resistance of urbanized soils to chemical pollution, and the approaches taken to study their buffer properties contribute to the methodology of ecological diagnostics of urban areas. The ongoing research and study of the spatial distribution of soil pollution by oil products will contribute to a differentiated assessment of the ecological state of the city's territories and the targeted inventory of land. The development of a sampling system around fuel stations will make it possible to build schematic maps of oil pollution fields. For these purposes, it is necessary to use GIS technologies. 5
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 The following measures can contribute to the reduction of soil pollution in NP cities: Creation of a unified long-term plan for the location of filling stations, filling stations and oil depots, taking into account the environmental situation in the city; Optimization of traffic management; Development of engineering methods for protecting the environment from oil spills; Creation of environmental monitoring and control systems in the gas station area. The results obtained are also of practical importance for the environmental management of the city, for the cadastral valuation of land, for adjusting the placement of transport routes and the network of gas stations, as well as for the development of geoecological monitoring of the urbanized area. References [1] Garmonov K V, Polosin I I 2014 Influence of petrol stations within urban development on the ecological state of the environment. Ecology of industrial production 1 51-54 [2] Belozertseva I A 2018 Ecological state of soils in Verkhnelenya. Journal of the nature of inner Asia 3 17-27 [3] Slyusarevsky A, Zinnatshina L and Vasilyeva G 2018 Comparative ecological and economic analysis of methods for remediation of oil-contaminated soils by in situ bioremediation and mechanical soil replacement. Ecology and industry of Russia 22 (11) 40-45 [4] Buzmakov S A 2013 Land restoration at different levels of oil pollution. Notes of the Mining Institute 203 128-132 [5] Panina Yu, Smirnova T, Vishnetskaya M and Mkrtychan V 2018 Assessment of the influence of hydrocarbon pollution on the quality of urban soils. Ecology and industry of Russia 22(5) 59- 63 [6] Song H G, Bartha R 1990 Effects of Jet Fuel Spills on the Microbial Community of Soil. Appl. Env. Microbiol. 56(3) 646-651 [7] Nature Conservation. Soils. Methods of sampling and preparation of samples for chemical, bacteriological, helminthological analysis. GOST 17.4.4.02-2017 [8] Soil quality. Express method of IR spectroscopy is the share of quality determination and identification of soil pollution with oil products. GOST R 54039-2010 [9] Arinushkina E B 1970 Guide to the Chemical Analysis of Soils (Moskow: Moscow State University Press) 487 [10] Drugov Yu S Rodin AA 2007 Environmental Analysis of Oil and Petroleum Product Spills (Moskow: BINOM. Knowledge Laboratory) 270 [11] Belik E S, Rudakova L V 2013 Obtaining a biosorbent based on carbonizate for the purification of oil-contaminated soils and grounds. Ecology and industry of Russia 11 48-52 [12] Bigaliev A A, Ishanova N E, Bigaliev AB and Bijasheva Z M 2008. Ecological assessment of oil -gas producing area in Kazakhstan zone of Caspian sea and using bioremediation technology for cleaning of high level oil polluted sites. International journal Colloid and Surface 57–63 [13] Nikolaeva O, Tikhonov V, Vecherskii M , Kostina N and Astaikina A 2019 Ecotoxicological effects of traffic -related pollutants in roadside soils of Moscow. Ecotoxicology and Environmental Safety 17215 538–546 [14] Fismes J, Perrin Ganier C and More J L 2002 Soil-to-root transfer and translocation of polycyclic aromatic hydrocarbons by vegetables grown on industrial contaminated soils/ mpereur issonnet. Journal of Environmental Quality 31 1649–1656 [15] Grechishcheva N, Perminova I and Meshcheryakov S 2016 Prospects for the use of humic substances in technologies for cleaning oil-contaminated soils. Ecology and industry of Russia 20(1) 30-36 [16] Vaysman YaI, Glushankova I S and Rudakova L V 2013 Development of technology 6
APEC 2021 IOP Publishing IOP Conf. Series: Earth and Environmental Science 808 (2021) 012067 doi:10.1088/1755-1315/808/1/012067 remediation soil contaminated by oil using GUMIKOM. Oil industry 10 128 [17] Sarapulova G I Study of the Immobilizing Capacity of Humic Substances in Soils at Oil Contamination. 2021 IOP Conf. Ser.: Earth Environ. Sci. 720 012046 [18] Safarov A, Valiakhmetova Yu and Yagafarova G 2018 Method of Remediation of Oil-Saline Soils. Ecology and Industry of Russia 22(10) 44-47 [19] Haritash A K and Kaushik C P 2009 Biodegradation aspects of polycyclic aromatic hydrocarbons. J. Hazard Mater 169 1-3 [20] GOST R 57447-2017 best available technology. reclamation of lands and land plots contaminated with oil and oil products (Moscow) 34 7
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