Estimation of quality of surface water of Dniester river basin within Lviv and Khmelnytsk regions

B. M. Kalyn, M. V. Khromova, V. I. Vishchur, H. A. Butsiak, S. I. Kropyvka, B. Gutyj
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The main pollutants of surface water bodies in Lviv region in terms of the amount of effluents are enterprises of housing and communal services, enterprises of heat and power, chemical and petrochemical, machine-building and food industries. Among the enterprises of Khmelnytsk region, the largest volumes of wastewater discharges are carried out by the enterprises of heat and power, housing and communal services, food and construction industries. It is established that the major factors influencing the deterioration of surface in the river basin are disposals of sewage. The ecological danger from hydrosphere pollution in the Dniester basin has been assessed on the basis of pollutant concentrations. The results of monitoring water pollution in the river Dniester basin testified that the main pollutants that exceed the level compared to the maximum permissible concentration are nitrites, and for its tributaries river Lug and river Smotrych also ammonium salt, nitrates, sulfates and phosphates. As a result of a comprehensive assessment of the water quality of the river basin, the characteristics assigned to them are weakly and moderately polluted. Except for pollution of water objects, the urgent problem demanding the solution is the acting landscape structure in the basin of river Dniester. The disturbed structure of territories is the result of excessive agricultural land use and reduction of the area of natural lands. We came up with the priority tasks are to minimize the discharges of polluted return water into the water bodies, to improve the economic mechanism of water use and implement of water protection measures, to optimize the landscape-ecological structure of the territory, in particular increase the areas of nature reserve fund. \n \nKey words: surface water, the Dniester River basin, tributary, water service, pollution, water quality, landscape structure. \n  \n \nReferences \n \n  \n \nAfanasiev-Chuzhbynskyi, O.S. (2016). Narysy Dnistra. Lviv: Apriori (in Ukrainian). \n \nBorshch, O.O., Gutyj, B.V., Borshch, O.V., Sobolev, O.I., Chernyuk, S.V., Rudenko, O.P., Kalyn, B.M., Lytvyn, N.A., Savchuk, L.B., Kit, L.P., Nahirniak, T.B., Kropyvka, S.I., & Pundyak, T.O. (2020). Environmental pollution caused by the manure storage. Ukrainian Journal of Ecology, 10(3), 110-114. doi: 10.15421/2020_142 \n \nBovsunivska, V. (2014). Landshaftna struktura Khmelnytskoi oblasti. Visnyk Lvivskoho universytetu. Seriia heohrafichna, 48, 68–74 (in Ukrainian). \n \nGrynevych, N., Sliusarenko, A., Dyman, T., Sliusarenko, S., Gutyj, B., Kukhtyn, M., Hunchak, V., & Kushnir, V. (2018). Etiology and histopathological alterations in some body organs of juvenile rainbow trout Oncorhynchus mykiss (Walbaum, 1792) at nitrite poisoning. Ukrainian Journal of Ecology, 8(1), 402–408. doi: 10.15421/2018_228  \n \nHnatiuk R. (2017). Desiat pozytsii za richkove pokhodzhennia verkhnikh (supishchano-suhlynystykh) horyzontiv pleistotsenovykh teras Ukrainskoho Peredkarpattia ta serednoho Prydnisteria (chastyna 4). Problemy heomorfolohii i paleoheohrafii Ukrainskykh Karpat i prylehlykh terytorii, 7, 85-101 (in Ukrainian). \n \nHoncharova, O.V., Paranjak, R.P., & Gutyj, B.V. (2019). Functional state of an organism of freshwater fish under the influence of abiotic factors. Scientific Messenger of Lviv National University of Veterinary Medicine and Biotechnologies. Series: Agricultural sciences, 21(90), 82–87. doi: 10.32718/nvlvet-a9014 \n \nIatsyk, A. V. (2004). Vodohospodarska ekolohiia. Kiev. Heneza (in Ukrainian). \n \nKalyn, B. M., Dziana, H. O., & Cherevko, M. V. (2011). Ekolohichni zakony i pravove rehuliuvannia okhorony dovkillia: navch. posib. Lviv. Lviv regional Institute of State Management of National Academy of State Management (in Ukrainian). \n \nKhilchevskyi, V. K., Honchar, O. M., & Zabokrytska, M. R. (2013). Hidrokhimichnyi rezhym ta yakist poverkhnevykh vod baseinu Dnistra na terytorii Ukrainy. Kiev. Nika-Tsentr (in Ukrainian). \n \nKrainiukov, O. M., & Timchenko, V. D. (2016). Udoskonalennia kompleksnoi otsinky ekolohichnoho stanu ta yakosti vody vodnykh obiektiv. Visnyk KhNU imeni V.N. Karazina. Seriia “Ekolohiia”, 14, 9-14 (in Ukrainian). \n \nMelnychuk, V. P., & Protsiv, H. P. (2019). Nastanova z upravlinnia baseinamy malykh richok – prytok richky Dnister: metod. posibn. Lviv: Spolom (in Ukrainian). \n \nMetodyka rozrakhunku koefitsiienta zabrudnenosti pryrodnykh vod: KND 211.1.1.106-2003 Orhanizatsiia ta zdiisnennia sposterezhen za zabrudnenniam poverkhnevykh vod (v systemi Minekoresursiv). No89-M 04.06.2003. Kiev, 25–30 (in Ukrainian). \n \nParaniak, R. P., Voitovych, N. V., & Kalyn, B. M. (2014). Systema upravlinnia vodnymy resursamy u Lvivskii oblasti. Nauk. visnyk LNUVMBT imeni S.Z. Gzhytskoho, 16, 3(60), 386-393 (in Ukrainian). \n \nParanjak, R.P., Kalyn, B.M., & Gutyj, B.V. (2019). Prospects of transgenic plants in the agro-sphere of Lviv region. Scientific Messenger of Lviv National University of Veterinary Medicine and Biotechnologies. Series: Agricultural sciences, 21(90), 54–58. doi: 10.32718/nvlvet-a9009 \n \nPylypovoch, O. V., & Kovalchuk, I. P. (2017). Heoekolohiia richkovo-baseinovoi systemy verkhnoho Dnistra: monohrafiia. Lviv-Kyiv: LNU imeni Ivana Franka (in Ukrainian). \n \nRudenko, O.P., Paranjak, R.P., Kovalchuk, N.A., Kit, L.P., Hradovych, N.I., Gutyj, B.V., Kalyn, B.M., Sukhorska, O.P., Butsiak A.A., Kropyvka S.I., Petruniv V.V., & Kovalska L.M. (2019). Influence of seasonal factors on carp fish immune reactivity. Ukrainian Journal of Ecology, 2019, 9(3), 168-173 \n \nTomiltseva, A. I., Yatsyk, A. V., & Mokin, V. B. (2017). Ekolohichni osnovy upravlinnia vodnymy resursamy. Kiev. Instytut ekolohichnoho upravlinnia ta zbalansovanoho pryrodokorystuvannia (in Ukrainian).","PeriodicalId":23422,"journal":{"name":"Ukrainian Journal of Ecology","volume":" ","pages":"127-132"},"PeriodicalIF":0.0000,"publicationDate":"2020-12-28","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"8","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Ukrainian Journal of Ecology","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.15421/2020_271","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 8

Abstract

The problem of deterioration of the ecological condition of river basins of Ukraine is extremely important. Particular attention is paid to transboundary rivers, which include the Dniester River. The article describes the physical and geographical conditions of the Dniester basin, analyzes the scale of water use and discharge of return water in to the surface reservoirs in the basin. The use of water resources of the basin by different sectors of the economy is studied. 50% in Lviv region and 72% in Khmelnytsk region of abstracted water is used for commercial and drinking purposes, respectively 30% and 25% - for production. The largest sources of river basin pollution within Lviv and Khmelnytsk regions are considered. The main pollutants of surface water bodies in Lviv region in terms of the amount of effluents are enterprises of housing and communal services, enterprises of heat and power, chemical and petrochemical, machine-building and food industries. Among the enterprises of Khmelnytsk region, the largest volumes of wastewater discharges are carried out by the enterprises of heat and power, housing and communal services, food and construction industries. It is established that the major factors influencing the deterioration of surface in the river basin are disposals of sewage. The ecological danger from hydrosphere pollution in the Dniester basin has been assessed on the basis of pollutant concentrations. The results of monitoring water pollution in the river Dniester basin testified that the main pollutants that exceed the level compared to the maximum permissible concentration are nitrites, and for its tributaries river Lug and river Smotrych also ammonium salt, nitrates, sulfates and phosphates. As a result of a comprehensive assessment of the water quality of the river basin, the characteristics assigned to them are weakly and moderately polluted. Except for pollution of water objects, the urgent problem demanding the solution is the acting landscape structure in the basin of river Dniester. The disturbed structure of territories is the result of excessive agricultural land use and reduction of the area of natural lands. We came up with the priority tasks are to minimize the discharges of polluted return water into the water bodies, to improve the economic mechanism of water use and implement of water protection measures, to optimize the landscape-ecological structure of the territory, in particular increase the areas of nature reserve fund. Key words: surface water, the Dniester River basin, tributary, water service, pollution, water quality, landscape structure.   References   Afanasiev-Chuzhbynskyi, O.S. (2016). Narysy Dnistra. Lviv: Apriori (in Ukrainian). Borshch, O.O., Gutyj, B.V., Borshch, O.V., Sobolev, O.I., Chernyuk, S.V., Rudenko, O.P., Kalyn, B.M., Lytvyn, N.A., Savchuk, L.B., Kit, L.P., Nahirniak, T.B., Kropyvka, S.I., & Pundyak, T.O. (2020). Environmental pollution caused by the manure storage. Ukrainian Journal of Ecology, 10(3), 110-114. doi: 10.15421/2020_142 Bovsunivska, V. (2014). Landshaftna struktura Khmelnytskoi oblasti. Visnyk Lvivskoho universytetu. Seriia heohrafichna, 48, 68–74 (in Ukrainian). Grynevych, N., Sliusarenko, A., Dyman, T., Sliusarenko, S., Gutyj, B., Kukhtyn, M., Hunchak, V., & Kushnir, V. (2018). Etiology and histopathological alterations in some body organs of juvenile rainbow trout Oncorhynchus mykiss (Walbaum, 1792) at nitrite poisoning. Ukrainian Journal of Ecology, 8(1), 402–408. doi: 10.15421/2018_228  Hnatiuk R. (2017). Desiat pozytsii za richkove pokhodzhennia verkhnikh (supishchano-suhlynystykh) horyzontiv pleistotsenovykh teras Ukrainskoho Peredkarpattia ta serednoho Prydnisteria (chastyna 4). Problemy heomorfolohii i paleoheohrafii Ukrainskykh Karpat i prylehlykh terytorii, 7, 85-101 (in Ukrainian). Honcharova, O.V., Paranjak, R.P., & Gutyj, B.V. (2019). Functional state of an organism of freshwater fish under the influence of abiotic factors. Scientific Messenger of Lviv National University of Veterinary Medicine and Biotechnologies. Series: Agricultural sciences, 21(90), 82–87. doi: 10.32718/nvlvet-a9014 Iatsyk, A. V. (2004). Vodohospodarska ekolohiia. Kiev. Heneza (in Ukrainian). Kalyn, B. M., Dziana, H. O., & Cherevko, M. V. (2011). Ekolohichni zakony i pravove rehuliuvannia okhorony dovkillia: navch. posib. Lviv. Lviv regional Institute of State Management of National Academy of State Management (in Ukrainian). Khilchevskyi, V. K., Honchar, O. M., & Zabokrytska, M. R. (2013). Hidrokhimichnyi rezhym ta yakist poverkhnevykh vod baseinu Dnistra na terytorii Ukrainy. Kiev. Nika-Tsentr (in Ukrainian). Krainiukov, O. M., & Timchenko, V. D. (2016). Udoskonalennia kompleksnoi otsinky ekolohichnoho stanu ta yakosti vody vodnykh obiektiv. Visnyk KhNU imeni V.N. Karazina. Seriia “Ekolohiia”, 14, 9-14 (in Ukrainian). Melnychuk, V. P., & Protsiv, H. P. (2019). Nastanova z upravlinnia baseinamy malykh richok – prytok richky Dnister: metod. posibn. Lviv: Spolom (in Ukrainian). Metodyka rozrakhunku koefitsiienta zabrudnenosti pryrodnykh vod: KND 211.1.1.106-2003 Orhanizatsiia ta zdiisnennia sposterezhen za zabrudnenniam poverkhnevykh vod (v systemi Minekoresursiv). No89-M 04.06.2003. Kiev, 25–30 (in Ukrainian). Paraniak, R. P., Voitovych, N. V., & Kalyn, B. M. (2014). Systema upravlinnia vodnymy resursamy u Lvivskii oblasti. Nauk. visnyk LNUVMBT imeni S.Z. Gzhytskoho, 16, 3(60), 386-393 (in Ukrainian). Paranjak, R.P., Kalyn, B.M., & Gutyj, B.V. (2019). Prospects of transgenic plants in the agro-sphere of Lviv region. Scientific Messenger of Lviv National University of Veterinary Medicine and Biotechnologies. Series: Agricultural sciences, 21(90), 54–58. doi: 10.32718/nvlvet-a9009 Pylypovoch, O. V., & Kovalchuk, I. P. (2017). Heoekolohiia richkovo-baseinovoi systemy verkhnoho Dnistra: monohrafiia. Lviv-Kyiv: LNU imeni Ivana Franka (in Ukrainian). Rudenko, O.P., Paranjak, R.P., Kovalchuk, N.A., Kit, L.P., Hradovych, N.I., Gutyj, B.V., Kalyn, B.M., Sukhorska, O.P., Butsiak A.A., Kropyvka S.I., Petruniv V.V., & Kovalska L.M. (2019). Influence of seasonal factors on carp fish immune reactivity. Ukrainian Journal of Ecology, 2019, 9(3), 168-173 Tomiltseva, A. I., Yatsyk, A. V., & Mokin, V. B. (2017). Ekolohichni osnovy upravlinnia vodnymy resursamy. Kiev. Instytut ekolohichnoho upravlinnia ta zbalansovanoho pryrodokorystuvannia (in Ukrainian).
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利沃夫和赫梅利尼茨基地区德涅斯特河流域地表水水质估算
乌克兰流域生态状况恶化的问题十分重要。特别注意跨界河流,其中包括德涅斯特河。本文介绍了德涅斯特流域的自然地理条件,分析了该流域地表水库的利用规模和回水排放情况。研究了不同经济部门对流域水资源的利用情况。利沃夫地区50%和赫梅利尼茨克地区72%的抽取水用于商业和饮用目的,分别为30%和25%用于生产。考虑利沃夫和赫梅利尼茨克地区最大的河流流域污染源。就排污量而言,利沃夫地区地表水水体的主要污染物是住房和公共服务企业、热力和电力企业、化学和石化企业、机械制造和食品工业。在赫梅利尼茨克地区的企业中,废水排放量最大的是供热和电力、住房和公共服务、食品和建筑行业的企业。确定了影响流域地表退化的主要因素是污水的处理。基于污染物浓度对德涅斯特流域水圈污染的生态危害进行了评价。德涅斯特河流域水质污染监测结果表明,超过最大允许浓度的主要污染物是亚硝酸盐,其支流卢格河和斯莫特里奇河还包括铵盐、硝酸盐、硫酸盐和磷酸盐。通过对流域水质的综合评价,确定其水质特征为弱污染和中度污染。除了水体的污染问题,德涅斯特河流域的景观结构问题也是亟待解决的问题。土地结构的扰动是农业用地过度利用和自然土地面积减少的结果。我们提出的首要任务是尽量减少受污染的回水排入水体,完善用水经济机制和实施水保护措施,优化国土景观生态结构,特别是增加自然保护区的面积。关键词:地表水,德涅斯特河流域,支流,供水,污染,水质,景观结构参考文献afanasev - chuzhbynskyi, O.S.(2016)。Narysy Dnistra。利沃夫:Apriori(乌克兰语)。Borshch, o.o., Gutyj, b.v., Borshch, o.v., Sobolev, o.i., Chernyuk, s.v., Rudenko, o.p., Kalyn, b.m., Lytvyn, n.a., Savchuk, l.b., Kit, l.p., Nahirniak, t.b., Kropyvka, s.i.和Pundyak, T.O.(2020)。粪便储存造成的环境污染。乌克兰生态学杂志,10(3),110-114。bovunivska, V. (2014). doi: 10.15421/2020_142。赫梅利尼茨科伊州陆桥结构。Visnyk Lvivskoho大学。seria heohrafichna, 48, 68-74(乌克兰语)。gryneych, N., Sliusarenko, A., Dyman, T., Sliusarenko, S., Gutyj, B., Kukhtyn, M., Hunchak, V.和Kushnir, V.(2018)。亚硝酸盐中毒对虹鳟鱼幼鱼身体某些器官的病因学和组织病理学改变。生态学杂志,8(1),402-408。doi: 10.15421/2018_228 Hnatiuk R.(2017)。引用本文:Desiat pozytsii za richkove pokhodzhennia verkhnikh (supishchano-suhlynystykh) horyzontiv pleistotsenovykh teras Ukrainskoho Peredkarpattia serednoho Prydnisteria (chastyna 4). Problemy mormorfolhii i palaeheohrafi Ukrainskykh Karpat i prylehlykh领土,7,85-101(乌克兰文)。Honcharova, o.v., Paranjak, r.p., & Gutyj, B.V.(2019)。在非生物因素影响下淡水鱼有机体的功能状态。利沃夫国立兽医和生物技术大学科学信使。系列:农业科学,21(90),82-87。Iatsyk, a.v. (2004). doi: 10.32718/nvlvet-a9014Vodohospodarska ekolohiia。基辅。Heneza(乌克兰语)。Kalyn, b.m., Dziana, h.o., & Cherevko, m.v.(2011)。[4] [j] [j]。posib。利沃夫。国家管理学院利沃夫地区国家管理研究所(乌克兰语)。Khilchevskyi, V. K, Honchar, O. M.和Zabokrytska, M. R.(2013)。Hidrokhimichnyi rezhym ta yakist popokhnevykh vod basinu Dnistra na territory乌克兰。基辅。Nika-Tsentr(乌克兰语)。Krainiukov, o.m.,和Timchenko, V. D.(2016)。Udoskonalennia kompleksnoi otsinky ekolohicnoho stanu, yakosti vodyvonykkh。Visnyk KhNU imeni V.N. Karazina。“Ekolohiia”杂志,14,9 -14(乌克兰文)。Melnychuk, V. P.和Protsiv, H. P.(2019)。Nastanova, z, avavinnia,基础,malykh - prytok - richky:方法。
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