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Abstract

W latach 2000-2002 badano niektóre naturalne i antropogenne właściwości wód powierzchniowych Kampinoskiego Parku Narodowego. Uzyskane wartości średnie omówiono w porównaniu do odpowiednich norm. Analizy większości próbek wykazały, że odpowiadają one I klasie czystości. Benzo(a)pirenu nie wykryto. Jednak w dwóch przypadkach zaobserwowano wysokie stężenie żelaza i manganu. Próbki pobrane w listopadzie zawierały więcej manganu. W jednym przypadku oznaczono wysokie stężenie azotanów. Większość próbek pobranych w Aleksandrowie odpowiadała li klasie czystości ze względu na zawartość fosforanów.
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Authors and Affiliations

Krystyna Oprządek
Krystyna Syrocka
Mariusz Kluska
Wojciech Kroszczyński
Witold Zalewski
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Abstract

The objective of the study was to characterise the quality of surface waters in order to de-termine their vulnerability to pollution by nitrogen compounds from agricultural activity, as well as to specify the areas with increased exposure, where nitrogen runoff from agricultural sources has to be reduced. It was necessary to determine surface waters liable to pollution by these compounds due to the fact that agricultural production should be carried out in the way which limits and prevents water pollution by nitrogen compounds of agricultural origin. The study addressed the following is-sues: the concentration of nitrogen compounds in the surface waters of the Middle Odra Basin, and the extent of eutrophication in flowing inland waters (with nitrogen as the main nutrient). The results have been plotted in figures and gathered in tables.

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Authors and Affiliations

Agnieszka Kolanek
Rafalina Korol
Marzenna Strońska
Urszula Szyjkowska
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Abstract

Biochar was prepared from corn ( Zea mays) stalks and impregnated with sulfuric acid. The biomass was impregnated for 24 h with a 50% solution of H2SO4 with impregnation ratios 1:2 (B 1:2) and 1:3 p/v (B 1:3); then, it was carbonized in a muffle furnace at 520°C for 30 min with a 10°C per min ramp. The adsorption capacity to remove anions (nitrate, sulfate, and phosphate) in an aqueous solution was evaluated by varying the temperature. The adsorption mechanism was studied by determining the thermodynamic parameters: Gibbs free energy (ΔGº), enthalpy (ΔHº) and entropy (ΔSº) standard. The biochars were characterized by Scanning Electron Microscopy-Energy Dispersive X-Ray Spectroscopy (SEM-EDS) analysis and were found to exhibit a heterogeneous surface and porous nature, with C, O, S, and Si. The experiments in the batch system showed the best performance of B 1: 2 in the removal of the three anions occurred at 303 K, while B 1: 3 had the best performance at 298 K. From the thermodynamic parameters, it was found that the removal processes are endothermic, their mechanism is by chemisorption. It is concluded that synthesized biochar is an excellent alternative to removing nutrient anions present in the solution.
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Authors and Affiliations

Ángel Villabona-Ortiz
1
Candelaria Tejada-Tovar
1
ORCID: ORCID
Rodrigo Ortega-Toro
2
ORCID: ORCID

  1. Universidad de Cartagena, Faculty of Engineering, Department of Chemical Engineering, Cartagena de Indias, Colombia
  2. Universidad de Cartagena, Faculty of Engineering, Department of Food Engineering, Avenida Del Consulado 48-152, Cartagena 130014, Colombia
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Abstract

The use of ammonium nitrate due to its high nitrogen content (> 26%) has made it the most utilized fertilizer in agricultural areas. However, being easily accessible with this feature encouraged its use for different purposes. Ammonium nitrate is usually produced with large tonnage (> 50 ton/h) and high cost (> $20 million) production processes. Therefore, any changes that can be made in the process must be applied in the process so that the result can be achieved easily without increasing the cost in any way. In this study, it is aimed to reduce the explosion sensitivity of ammonium nitrate used for explosive purposes in terrorist attacks. Thus, it was aimed to solve the problem by adding various chemicals to the ammonium nitrate production process so that it can only be used for agricultural purposes. For this purpose, the production process was examined by adding carboxymethyl cellulose and polyethylene glycol to the ammonium nitrate production process and the accuracy of the results was tested by instrumental analysis methods.

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Authors and Affiliations

Ahmet Ozan Gezerman
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Abstract

This paper presents the results of a study on the level of nitrate leaching from the 0–30 cm layer of grassland (GL) soil in the Lublin Voivodship during the winters of 2018/2019, 2019/2020 and 2020/2021. The amounts of leached nitrates were determined using the Burns model. For the calculations based on this model – directly and indirectly, the results determination of residual nitrate nitrogen, texture and organic matter in GL soils, obtained within the framework of agricultural monitoring of soils by the National Chemical and Agricultural Station (KSChR), and results of system meteorological measurements conducted by the Institute of Meteorology and Water Management – National Research Institute (IMGW-PIB) were used.
The analysed soil samples were taken from 39 permanent control and measurement grassland sites. The research discovered in particular that:
– the average leaching of nitrate nitrogen from GL mineral soil in the three analysed periods was 16.2 and 5.1 kg N∙ha–1 from organic soil;
– on average, in autumn during the entire study period, 55.3% of NO3-N leached from the 0–30 cm layer of GL mineral soil, and 27.3% from organic soil;
– among different agronomic categories of mineral soil, the highest leaching of NO3-N was recorded from medium soil (17.4 kg N∙ha–1) and the lowest from heavy soil (11.5 kg N∙ha–1);
– individually determined values of NO3-N leaching from soil varied significantly from 0 to 68.5 kg N∙ha–1 for mineral soil and from 0.1 to 23.65 kg N∙ha–1 for organic soil.

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Authors and Affiliations

Stefan Pietrzak
1
ORCID: ORCID
Marek Urbaniak
1
ORCID: ORCID

  1. Institute of Technology and Life Sciences – National Research Institute, Falenty, Hrabska Ave., 3, 05-090 Raszyn, Poland
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Abstract

As a rule, nitrates are present in all natural water bodies. Their increased concentrations are connected with the discharge of insufficiently treated wastewater from industrial and communal enterprises, agricultural and livestock complexes. Recent scientific publications concerning treatment methods for nitrates removal from natural water and wastewater were analyzed in order to create effective and low-waste technology for obtaining high quality water. It has been established that the ion exchange method is quite effective for removing nitrates from water. In the paper, the processes of ion exchange removal of nitrates from water on low-axis anionite in DOWEX Marathon WBA in Сl- form were investigated. During the sorption of nitrates with a concentration of 186, 205, 223 and 2200 mg/dm3, it was established that the full exchangeable dynamic capacity was 1.075, 1.103, and 1.195, 1.698 g-eq/dm3, respectively. To regenerate anionite, solutions of ammonia as well as potassium chloride, ammonium chloride and potassium carbonate were used in this work. The choice of potassium and ammonium compounds is due to the prospect of further use of regeneration solutions for the production of liquid fertilizers.
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Bibliography

  1. Alguacil-Duarte, F., González-Gómez, F. & Romero-Gámez, M. (2022). Biological nitrate removal from a drinking water supply with an aerobic granular sludge technology: An environmental and economic assessment. Journal of Cleaner Production, 367. DOI:10.1016/j.jclepro.2022.133059
  2. Bodzek, M. (2019). Membrane separation techniques – removal of inorganic and organic admixtures and impurities from water environment – review. Archives of Environmental Protection, 45, 4, pp. 4–19. DOI:10.24425 / aep.2019.130237.
  3. Boubakri, A., Al-Tahar Bouguecha, S. & Hafiane, A. (2022). FO–MD integrated process for nitrate removal from contaminated groundwater using seawater as draw solution to supply clean water for rural communities. Separation and Purification Technology, 298. DOI:10.1016/j.seppur.2022.121621
  4. Gutiérrez, M., Biagioni, R.N., Alarcón-Herrera, M.T. & Rivas- Lucero, B.A. (2018). An overview of nitrate sources and operating processes in arid and semiarid aquifer systems. Science of the Total Environment, 624, pp. 1513–1522. DOI:10.1016/j. scitotenv.2017.12.252
  5. Hansen, B., Sonnenborg, T.O., Møller, I., Bernth, J.D., Høyer, A., Rasmussen, P., Sandersen P.B.E. & Jørgensen, F. (2016). Nitrate vulnerability assessment of aquifers. Environmental Earth Sciences, 75, 12. DOI:10.1007/s12665-016-5767-2
  6. Kaushal, S.S. (2016). Increased salinization decreases safe drinking water. Environ. Sci. Technol., 50, pp. 2765–2766. doi:10.1021/ acs.est.6b00679.
  7. Królak, E. & Raczuk, J. (2018). Nitrate concentration-related safety of drinking water from various sources intended for consumption by neonates and infants. Archives of Environmental Protection, 44, 1, pp. 3–9. DOI:10.24425/118176
  8. National report on drinking water quality and drinking water supply in Ukraine in 2021. Database ‘Ministry of Regional Development of Ukraine’ (in Ukrainian).
  9. Nujić, M., Milinković, D. & Habuda-Stanić, M. (2017). Nitrate removal from water by ion exchange. Croatian journal of food science and technology, 9, 2, pp. 182–186. DOI:10.17508/ CJFST.2017.9.2.15
  10. Preetham, V. & Vengala, J. (2023). Adsorption isotherm, kinetic and thermodynamic studies of nitrates and nitrites onto fish scales. In Recent Advances in Civil Engineering, pp. 429–442. doi:10.1007/978-981-19-1862-9_27
  11. Remeshevska, I., Trokhymenko, G., Gurets, N., Stepova, O., Trus, I. & Akhmedova, V. (2021). Study of the ways and methods of searching water leaks in water supply networks of the settlements of Ukraine. Ecological Engineering and Environmental Technology, 22, 4, pp. 14–21. DOI:10.12912/27197050/137874
  12. Song, Q., Zhang, S., Hou, X., Li, J., Yang, L., Liu, X. & Li, M. (2022). Efficient electrocatalytic nitrate reduction via boosting oxygen vacancies of TiO2 nanotube array by highly dispersed trace cu doping. Journal of Hazardous Materials, 438. DOI:10.1016/j. jhazmat.2022.129455
  13. Trus, I., Gomelya, M., Skiba, M., Pylypenko, T. & Krysenko, T. (2022). Development of Resource-Saving Technologies in the use of sedimentation inhibitors for reverse osmosis installations. J. Ecol. Eng., 23(1), pp. 206–215. DOI:10.12911/22998993/144075
  14. Trus, I. (2022). Optimal conditions of ion exchange separation of anions in low-waste technologies of water desalination. Journal of Chemical Technology and Metallurgy, 57, 3, pp. 550–558.
  15. Trusa, I. M., Gomelya, M. D. & Tverdokhlib, M. M. (2021). Evaluation of the contribution of ion exchange in the process of demanganization with modified cation exchange resin ku-2- 8. Journal of Chemistry and Technologies, 29, 4, pp. 540–548. DOI:10.15421/jchemtech.v29i4.242561
  16. Trus, I. & Gomelya, M. (2022). Low-waste technology of water purification from nitrates on highly basic anion exchange resin. Journal of Chemical Technology and Metallurgy, 57, 4, pp. 765–772. https://dl.uctm.edu/journal/node/j2022-4/14_21- 93_br4_2022_pp765-772.pdf
  17. Trusb, I., Gomelya, M., Skiba, M. & Vorobyova, V. (2021). Promising method of ion exchange separation of anions before reverse osmosis. Archives of Environmental Protection, 47, 4, pp. 93–97. DOI:10.24425/aep.2021.139505
  18. Trus, I., Gomelya, N., Halysh, V., Radovenchyk, I., Stepova, O. & Levytska, O. (2020). Technology of the comprehensive desalination of wastewater from mines. Eastern-European Journal of Enterprise Technologies, 3(6–105), pp. 21–27. DOI:10.15587/1729-4061.2020.206443 Vasilache, N., Cruceru, L., Petre, J., Chiriac, F. L., Paun, I., Niculescu, M., Pirvu F. & Lupu, G. (2018). The removal of nitrate from drinking water, natural water by ion exchange using ion exchange resin, purolite A520E and A500. Iternational Symposium “The Environment and the Industry”, SIMI 2018, Proceedings Book DOI:10.21698/simi.2018.fp53 Voutchkova, D.D., Schullehner, J., Rasmussen, P. & Hansen, B. (2021). A high-resolution nitrate vulnerability assessment of sandy aquifers (DRASTIC-N). Journal of Environmental Management, 277. DOI:10.1016/j.jenvman.2020.111330 Ward, M.H., Jones, R.R., Brender, J.D., de Kok, T.M., Weyer, P. J., Nolan, B. T., Vilanueva C.M. & van Breda, S.G. (2018). Drinking water nitrate and human health: An updated review. International Journal of Environmental Research and Public Health, 15, 7. DOI:10.3390/ijerph15071557 Wiśniowska, E. & Włodarczyk-Makuła, M. (2020). Removal of nitrates and organic compounds from aqueous solutions by zero valent (ZVI) iron reduction coupled with coagulation/ precipitation process. Archives of Environmental Protection, 46, 3, pp. 22–29. DOI: 10.24425 / aep.2020.134532.
  19. Zabłocki, S., Murat-Błażejewska, S., Trzeciak, J.A. & Błażejewski, R. (2022). High-resolution mapping to assess risk of groundwater pollution by nitrates from agricultural activities in Wielkopolska Province. Poland. Archives of Environmental Protection, 48, 1, pp. 41–57. DOI:10.24425/aep.2022.140544
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Authors and Affiliations

Inna Trus
1
ORCID: ORCID
Mukola Gomelya
1
ORCID: ORCID
Vita Halysh
1
ORCID: ORCID
Mariia Tverdokhlib
1
ORCID: ORCID
Iryna Makarenko
1
Tetiana Pylypenko
1
ORCID: ORCID
Yevhen Chuprinov
2
ORCID: ORCID
Daniel Benatov
1
ORCID: ORCID
Hennadii Zaitsev
2

  1. National Technical University of Ukraine «Igor Sikorsky Kyiv Polytechnic Institute», Kyiv, Ukraine
  2. State University of Economics and Technology: Kryvyi Rih, Ukraine
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Abstract

The removal of nitrates from aqueous solutions is cumbersome because of their high solubility in water. The use of zero-valent iron (ZVI) for the reduction of nitrates is the chemical process and it is an alternative method to the biological ones. The aim of the present study was to evaluate the eff ectiveness of nitrates removal from water solution by using the ZVI process. The process was coupled with the removal of COD, phosphates and turbidity by using by-products of nitrates reduction. Batch tests were performed to evaluate the eff ectiveness of ZVI in the removal of nitrates from aqueous solutions. The eff ectiveness of nitrates removal was analyzed after 5, 10, 20, 30 and 60 min. and compared to the initial concentration of pollutants. Simultaneously analysis of ammonium nitrogen and nitrites was controlled to identify products of nitrates reduction under various pH. The removal of COD, phosphates and turbidity was also performed in batch tests. The eff ectiveness of the emoval by using three types of chemicals was compared – PIX, FeSO4, and waste Fe2+/Fe3+ from the ZVI process. The results obtained in the study indicate that ZVI can be eff ectively used in the treatment of water polluted with nitrates and the by-products of the process could be further applied in the removal of COD, phosphates and turbidity. Based on the results the method should be advised as a promising alternative to the technologies used nowadays under technical scale as a technology that fits with a circular economy.

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Authors and Affiliations

Ewa Wiśniowska
1
Maria Włodarczyk-Makuła
1

  1. Częstochowa University of Technology, Poland
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Abstract

The ground source of drinking water for the village of Skalice nad Svitavou is located 35 km North of Brno (Czech Republic). An evaluation of developments in selected indicators of water quality in this groundwater source in the period 2013–2017 was the essence of this work. The data was provided by Vodárenská akciová společnost, a.s., i.e. the operator. At the same time, annual monitoring of water quality in the Úmoří stream, which flows through the catchment area and can affect the quality of groundwater, was carried out. Water samples were collected in 2017–2018 from 6 profiles on the Úmoří stream and its two tributaries. Raw water from the groundwater source does not meet the requirements for drinking water in some indicators and needs to be treated. Monitoring of surface water shows that the most problematic indicator is total phosphorus, the concentration of which exceeded limit values on all sampling profiles. The highest values were found in the tributaries, where total phosphorus concentrations exceeded 10 mg∙dm–3. There are 12 municipalities in the area of interest, only two of which have their own sewage treatment plant. It is clear from the results that wastewater in some municipalities is discharged directly into the recipient and is the cause of above-limit concentrations of both phosphorus and nitrogen. Intensively used agricultural land is another major source of pollution. Based on an analysis of sources of pollution, corrective measures have been proposed to improve the quality of surface and groundwater in the area.

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Authors and Affiliations

Petra Oppeltová
Jana Boráková
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Abstract

The article deals with the technological principles regarding the final drying process of the porous ammonium nitrate (PAN) granules in multistage gravitational shelf dryers. The data on the dryer’s optimal technological operating modes are obtained. PAN samples are studied; the regularity of the porous structure change in the granule depending on the dryer’s hydrodynamic and thermodynamic conditions is established. Experimental data obtained during the research will be used to create a methodology for the engineering calculation of gravitational shelf dryers. Moreover, the data on the optimal operating conditions of the drying machines at the final drying stage will be used to improve the technology to form porous granules from agricultural ammonium nitrate.
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Bibliography

  1.  T.J. Janssen, Explosive materials: classification, composition and properties, Nova Science Publishers, Inc., New York, 2011.
  2.  Patent No. 5540793 US: Porous prilled ammonium nitrate, 1996.
  3.  Patent No. 2118074, CA: Porous prilled ammonium nitrate, 2002.
  4.  Patent No. 2093727, CA: Hardened porous ammonium nitrate, 2004.
  5.  Patent No. 2004‒256365, JP: Method of manufacturing porous granular ammonium nitrate, 2004.
  6.  Patent No. 2005‒350276, JP: Method for producing porous granular ammonium nitrate, 2005.
  7.  Patent No. 2221717, CA: Procedure and installation for the manufacture of porous ammonium nitrate, 2005.
  8.  Patent No. 102093146, CN: Microporous granular ammonium nitrate and preparation methods thereof, 2011.
  9.  Patent No. 102173968, CN: Production method of porous granular ammonium nitrate, 2011.
  10.  Patent No. 2452719, RU: Device for production of porous granulated ammonium nitrate and method for production of porous granulated ammonium nitrate, 2012.
  11.  Patent No. 391973, PL: Method for producing granulated porous ammonium nitrate, 2012.
  12.  Patent No. 103896695, CN: Microporous pelletal ammonium nitrate and preparation method thereof, 2014.
  13.  Patent No. 204384319, CN: Device for producing porous ammonium nitrate and industrial ammonium nitrate, 2015.
  14.  Patent No. 204237724, CN: Recycling device for caked ammonium nitrate during production of porous ammonium nitrate, 2015.
  15.  Patent No. 104311372, CN: Porous ammonium nitrate production caking ammonium nitrate recycling apparatus and method of use, 2016.
  16.  Patent No. 106316727 CN: Porous and granular ANFO (ammonium nitrate fuel oil) and preparation method thereof, 2017.
  17.  Patent No. 2599170, RU: Method of producing porous granulated ammonium nitrate, 2016.
  18.  Patent No. 2600061, RU: Method of porous granulated ammonium nitrate producing and device for its implementation, 2016.
  19.  Patent No. 112294 UA: Device for granulation in the suspended layer, 2016.
  20.  Patent No. 112393 UA: Vortex granulator with utilization of waste gases, 2016.
  21.  Patent No. 112394 UA: Vortex granulator, 2016.
  22.  Patent No. 112622 UA: Vortex granulator, 2016.
  23.  Patent No. 113141 UA: Vortex granulator, 2017.
  24.  G. Martin and W. Barbour, Industrial nitrogen compounds and explosives, Chemical Manufacture and Analysis, Watchmaker Publishing, Seaside, 2003.
  25.  N. Kubota, Propellants and explosives: thermochemical aspects of combustion. 3rd ed., Wiley-VCH Verlag & Co.,Weinheim, 2015.
  26.  D. Buczkowski and B. Zygmunt, “Detonation Properties of Mixtures of Ammonium Nitrate Based Fertilizers and Fuels”, Cent. Eur. J. Energetic Mater., vol. 8, no. 2, pp. 99–106, 2011.
  27.  A.E. Artyukhov and V.I. Sklabinskyi, “Experimental and industrial implementation of porous ammonium nitrate producing process in vortex granulators”, Naukovyi Visnyk Natsionalnoho Hirnychoho Universytetu, vol. 6, pp. 42–48, 2013.
  28.  A.E. Artyukhov and N.A. Artyukhova, “Utilization of dust and ammonia from exhaust gases: new solutions for dryers with different types of fluidized bed”, J. Environ. Health Sci. Eng., vol. 16, no. 2, pp. 193–204, 2018.
  29.  A.E. Artyukhov and V.I. Sklabinskyi, “Investigation of the temperature field of coolant in the installations for obtaining 3D nanostructured porous surface layer on the granules of ammonium nitrate”, J. Nano- and Electron. Phys., vol. 9, no. 1, pp. 01015-1–01015-4, 2017.
  30.  N.A. Artyukhova, “Multistage finish drying of the N4HNO3 porous granules as a factor for nanoporous structure quality improvement”, J. Nano- and Electron. Phys., vol. 10, no. 3, pp. 03030-1–03030-5, 2018.
  31.  J. Hahm and A. Beskok, “Numerical simulation of multiple species detection using hydrodynamic/electrokinetic focusing”, Bull. Pol. Acad. Sci. Tech. Sci., vol. 53, no. 4, pp. 325–334, 2005.
  32.  А.E. Artyukhov, V.K. Obodiak, P.G. Boiko, and P.C. Rossi, Computer modeling of hydrodynamic and heat-mass transfer processes in the vortex type granulation devices, in CEUR Workshop Proceedings, vol. 1844, pp. 33–47, 2017.
  33.  A.E. Artyukhov, N.O. Artyukhova, and A.V. Ivaniia, “Creation of software for constructive calculation of devices with active hydrodynamics”, in Proceedings of the 14th International Conference on Advanced Trends in Radioelectronics, Telecommunications and Computer Engineering (TCSET 2018), 2018, pp. 139–142.
  34.  A.E. Artyukhov, N.A. Artyukhova, A.V. Ivaniia, and J. Gabrusenoks, “Multilayer modified NH4NO3 granules with 3D nanoporous structure: effect of the heat treatment regime on the structure of macro- and mezopores”, in Proc IEEE International Young Scientists Forum on Applied Physics and Engineering (YSF-2017), 2017, pp. 315–318.
  35.  A.E. Artyukhov and J. Gabrusenoks, “Phase composition and nanoporous structure of core and surface in the modified granules of NH4NO3”, Springer Proc. Phys., vol. 210, pp. 301–309, 2018.
  36.  N.O. Artyukhova and J. Krmela, “Nanoporous structure of the ammonium nitrate granules at the final drying: The effect of the dryer operation mode”, J. Nano- Electron. Phys., vol. 11, no. 4, pp. 04006-1–04006-4, 2019.
  37.  V.K. Obodiak, N.O. Artyukhova, and A.E. Artyukhov, “Calculation of the residence time of dispersed phase in sectioned devices: Theoretical basics and software implementation” Lect. Notes Mech. Eng., pp. 813‒820, 2020.
  38.  B. Paprocki, A. Pregowska, and J. Szczepanski, “Optimizing information processing in brain-inspired neural networks”, Bull. Pol. Acad. Sci. Tech. Sci., vol. 68, no. 2, pp. 225–233, 2020, doi: 10.24425/bpasts.2020.131844.
  39.  W. Jefimowski A. Nikitenko Z. Drążek, and M. Wieczorek, “Stationary supercapacitor energy storage operation algorithm based on neural network learning system”, Bull. Pol. Acad. Sci. Tech. Sci., vol. 68, no. 4, pp. 733–738, 2020, doi: 10.24425/bpasts.2020.134176.
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Authors and Affiliations

Nadiia Artyukhova
1
Jan Krmela
2
ORCID: ORCID
Artem Artyukhov
1
ORCID: ORCID
Vladimíra Krmelová
3
Mária Gavendová
3
Alžbeta Bakošová
2

  1. Sumy State University, Oleg Balatskyi Academic and Research Institute of Finance, Economics and Management, Department of Marketing, Rymskogo-Korsakova st. 2, 40007, Sumy, Ukraine
  2. Alexander Dubček University of Trenčín, Faculty of Industrial Technologies in Púchov, Department of Numerical Methods and Computational Modeling, Ivana Krasku 491/30, 020 01 Púchov, Slovakia
  3. Alexander Dubček University of Trenčín, Faculty of Industrial Technologies in Púchov, Department of Material Technologies and Environment, Ivana Krasku 491/30, 020 01 Púchov, Slovakia
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Abstract

A method to improve the quality of purifi ed water, reduce the cost of reagents for the regeneration of resin and create low-waste processes have been developed. This paper presents the results of ion exchange separation of sulfates and nitrates using AV-17-8 anion exchange resin in NO3 form. The effi ciency of anion separation on the highly basic anion exchange resin AV-17-8 depends on the magnitude and ratio of their concentrations in water. Separation on the AV-17-8 anion exchange resin has been shown to be eff ective at concentrations of sulfates up to 800 mg/dm3 and nitrates up to 100 mg/dm3. Conditions for regeneration of 10% NaNO3 anion exchange resin were determined. Reagent precipitation of sulfates from the used regeneration solution in the form of calcium sulfate was carried out. Calcium sulfate precipitate can be used in the manufacturing of building materials. The regeneration solution is suitable for reuse. The developed results will allow to introduce low-waste desalination technology of highly mineralized waters.
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Bibliography

  1. Berbar, Y., Amara, M. & Kerdjoudj, H. (2008). Anion exchange resin applied to a separation between nitrate and chloride ions in the presence of aqueous soluble polyelectrolyte, Desalination, 223, 238–242.
  2. Berger, E., Fro¨r, O. & Schäfer, R.B. (2019). Salinity impacts on river ecosystem processes: a critical mini-review, Phil. Trans. R. Soc. B, 374, 20180010. DOI:10.1098/rstb.2018.0010.
  3. Bodzek, M. (2019). Membrane separation techniques – removal of inorganic and organic admixtures and impurities from water environment – review, Archives of Environmental Protection, 45 , 4, pp. 4–19. DOI:10.24425 / aep.2019.130237.
  4. Bodzek, M., Konieczny, K. & Rajca, M. (2019). Membranes in water and wastewater disinfection – review, Archives of Environmental Protection, 45, pp. 3–18. DOI:10.24425/aep.2019.126419.
  5. Boyacioglu, H. (2014). Spatial dıfferentiation of water quality between reservoirs under anthropogenic and natural factors based on statistical approach, Archives of Environmental Protection, 40/1, pp. 41–50. DOI:10.2478 / aep-2014-0002.
  6. Chen, Q.-B., Ren, H., Tian, Z., Sun, L. & Wang, J. (2019). Conversion and pre-concentration of SWRO reject brine into high solubility liquid salts (HSLS) by using electrodialysis metathesis, Separation and Purification Technology, 213, pp. 587-598. DOI:10.1016/j.seppur.2018.12.018.
  7. Dharminder, Ram Kumar Singh, Vishal Kumar, Anoop Kumar Devedee, Mruthyunjaya, M. & Reshu Bhardwaj (2019). The clean water: The basic need of human and agriculture, International Journal of Chemical Studies, 7, 2, pp. 1994-1998.
  8. Hilary A. Dugan, H.A., Bartlett, S.L., Burke, S.M., Doubek, J.P. & Krivak, F.E. (2017). Salting our freshwater lakes, Proc. Natl Acad. Sci. USA, 114, 17, pp. 4453-4458. DOI:10.1073/pnas.1620211114.
  9. Gomelya, M.D., Trus, I.M. & Shabliy, T.O. (2014). Application of aluminium coagulants for the removal of sulphate from mine water, Chemistry & Chemical Technology, 8, 2, pp. 197-203. http://science2016.lp.edu.ua/chcht/application-auminium-coagulants-removal-sulphate-mine-water.
  10. Griffith, M.B. (2017). Toxicological perspective on the osmoregulation and ionoregulation physiology of major ions by freshwater animals: teleost fish, crustacea, aquatic insects, and Mollusca, Environ. Toxicol. Chem., 36, pp. 576-600. DOI:10.1002/etc.3676.
  11. Grodzka-Łukaszewska, M., Pawlak, Z. & Sinicyn, G. (2021). Spatial distribution of the water exchange through river cross-section – measurements and the numerical model, Archives of Environmental Protection, 47, 1, pp. 69–79. DOI:10.24425/aep.2021.136450.
  12. Halysh, V., Trus, I., Nikolaichuk, A., Skiba, M., Radovenchyk, I., Deykun, I., Vorobyova, V., Vasylenko, I. & Sirenko, L. (2020). Spent Biosorbents as Additives in Cement Production, Journal of Ecological Engineering, 21, 2, pp. 131–138. DOI:10.12911/22998993/116328.
  13. Hardikar, M., Marquez, I. & Achilli, A. (2020). Emerging investigator series: membrane distillation and high salinity: analysis and implications, Environmental Science: Water Research & Technology, 6, 6, pp. 1538-1552. DOI:10.1039/C9EW01055F.
  14. Kaushal, S.S. (2016). Increased salinization decreases safe drinking water, Environ. Sci. Technol., 50, pp. 2765-2766. DOI:10.1021/acs.est.6b00679.
  15. Lu, H., Wang, L., Wycisk, R., Pintauro, P.N. & Lin, S. (2020). Quantifying the kinetics-energetics performance tradeoff in bipolar membrane electrodialysis, Journal of Membrane Science, 612, 118279. DOI:10.1016/j.memsci.2020.118279.
  16. Luo, T., Abdu, S. & Wessling, M. (2018). Selectivity of ion exchange membranes: A review, Journal of Membrane Science, 555, pp. 429-454. DOI:10.1016/j.memsci.2018.03.051.
  17. Mester, T., Szabó, G., Bessenyei, É., Karancsi, G., Barkóczi, N. & Balla, D. (2017). The effects of uninsulated sewage tanks on groundwater. A case study in an eastern Hungarian settlement, J. Water Land Dev., 33, pp.123-129. DOI:10.1515/jwld-2017-0027.
  18. Mirzavand, M., Ghasemieh, H., Sadatinejad, S.J. & Bagheri, R. (2020). An overview on source, mechanism and investigation approaches in groundwater salinization studies, Int. J. Environ. Sci. Technol., 17, pp. 2463–2476. DOI:10.1007/s13762-020-02647-7.
  19. Mubita, T., Porada, S., Aerts, P. & van der Wal, A. (2020). Heterogeneous anion exchange membranes with nitrate selectivity and low electrical resistance, Journal of Membrane Science, 607, 118000.
  20. Panagopoulos, A. (2020). A comparative study on minimum and actual energy consumption for the treatment of desalination brine, Energy, 212, 118733. DOI:10.1016/j.energy.2020.118733.
  21. Radovenchyk, I., Trus, I., Halysh, V., Krysenko, T.,Chuprinov, E. & Ivanchenko, A. (2021). Evaluation of Optimal Conditions for the Application of Capillary Materials for the Purpose of Water Deironing, Ecol. Eng. Environ. Technol., 2, pp. 1–7. DOI:10.12912/27197050/133256.
  22. Rajca, M. (2012). The impact of selected factors on the removal of anionic water pollutants in ion-exchange process of MIEX®DOC, Archives of Environmental Protection, 38, pp. 115–121. DOI:10.2478/v10265-012-0010-z.
  23. Schuler, M.S., Cañedo-Argüelles, M., Hintz, W.D., Dyack, B., Birk, S. & Relyea, R.A. (2018). Regulations are needed to protect freshwater ecosystems from salinization, Philos Trans R Soc Lond B Biol Sci, 374, 1764, 20180019. DOI:10.1098/rstb.2018.0019.
  24. Trokhymenko, G., Magas, N., Gomelya, N., Trus, I. & Koliehova, A. (2020). Study of the Process of Electro Evolution of Copper Ions from Waste Regeneration Solutions, Journal of Ecological Engineering, 21, 2, pp. 29–38. DOI:10.12911/22998993/116351
  25. Trus, I. & Gomelya, M. (2021). Effectiveness nanofiltration during water purification from heavy metal ions, Journal of Chemical Technology and Metallurgy, 56, 3, pp. 615–620, https://dl.uctm.edu/journal/node/j2021-3/21_20-03p615-620.pdf.
  26. Trus, I., Radovenchyk, I., Halysh, V., Skiba, M., Vasylenko, I., Vorobyova, V., Hlushko, O. & Sirenko, L. (2019). Innovative Approach in Creation of Integrated Technology of Desalination of Mineralized Water, Journal of Ecological Engineering, 20, 8, pp. 107–113. DOI:10.12911/22998993/110767.
  27. Trus, I.M., Gomelya, M.D., Makarenko, I.M., Khomenlo, A.S. & Trokhymenko, G.G. (2020). The Study of the particular aspects of water purification from heavy metal ions using the method of nanofiltration, Naukovyi Visnyk Natsionalnogo Hirnychogo Universytety, 4, pp.117–123. DOI:10.33271/nvngu/2020-4/117
  28. Vörösmarty, C.J., McIntyre, P.B., Gessner, M.O., Dudgeon, D., Prusevich, A., Green, P., Glidden, S., Bunn, Sullivan, C.A.,LiermannC.R. & Davies, P.M.. (2010). Global threats to human water security and river biodiversity, Nature, 467, pp. 555-561. DOI:10.1038/nature09440.
  29. Wiśniowska, E. & Włodarczyk-Makuła, M. (2020). Removal of nitrates and organic compounds from aqueous solutions by zero valent (ZVI) iron reduction coupled with coagulation/precipitation process, Archives of Environmental Protection, 46, 3, pp. 22–29. DOI:10.24425 / aep.2020.134532.
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Authors and Affiliations

Inna Trus
1
ORCID: ORCID
Mukola Gomelya
1
ORCID: ORCID
Viktoria Vorobyova
1
ORCID: ORCID
Margarita Skіba
2
ORCID: ORCID

  1. National Technical University of Ukraine «Igor Sikorsky Kyiv Polytechnic Institute», Kyiv, Ukraine
  2. Ukrainian State Chemical-Engineering University, Dnipro, Ukraine
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Abstract

The purpose of this research was to determine the groundwater intrinsic vulnerability to pollution of shallow groundwater in Wielkopolska Province, Poland and to assess the risk of pollution by nitrates. Wielkopolska is known as an area where the problem of water pollution by nitrates has existed for a long time due to intensive agriculture. DRASTIC method and its optimized version as well as four other risk evaluation methods were selected to assess the risk pollution with nitrates. The results of either method did not correlate with nitrate concentrations recorded inthe total of 1679 groundwater monitoring points. Therefore a new method of groundwater pollution risk assessment (NV-L) was proposed. The new method is based on optimized results of the DRASTIC system and the L parameter which considers not only land use types, but also the amount of nitrogen loading leached from soil as a result of fertilizer consumption, and from wet deposition. The final results of NV-L method showed that the largest part of the study area is covered by a very low class of pollution risk (30.6%). The high and very high classes occupy 11.6% of the area, mostly in the areas designated until 2012 as the Nitrate Vulnerable Zones. Validation of the results of all methods showed that the other methods than NV-L cannot be used as a basis for reliable assessment of the risk of groundwater pollution by nitrates, as they do not take into account the nitrogen load leached from the soil profile.
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Bibliography

  1. Air quality monitoring, www.powietrze.gios.gov.pl, access on 04.2021
  2. Al-Adamat, R., Foster, I. & Baban, S.M.J. (2003). Groundwater vulnerability mapping for the Basaltic aquifer of the Azraq basin of Jordan using GIS, remote sensing and DRASTIC, Applied Geography, 23, 4, pp. 303-324.
  3. Alam, F., Umar, R., Ahmed, S. & Dar, F. A. (2014). A new model (DRASTIC-LU) for evaluating groundwater vulnerability in parts of central Ganga Plain, India. Arabian Journal of Geosciences. DOI:10.1007/s12517-012-0796-y
  4. Aller, L., Bennett, T., Lehr, J.H., Petty, R.J. & Hackett, G. (1987). DRASTIC: a standardized system for evaluating ground water pollution potential using hydrogeologic settings. EPA-600/2-87-035, EPA, Washington, DC.
  5. Babiker, I.S., Mohammed, M.A.A., Hiyama, T. & Kato, K. (2005). A GIS – based DRASTIC model for assessing aquifer vulnerability in Kakamigahara Heights. Gifu Prefecture central Japan. Science of the Total Environment, 345, pp. 127-140.
  6. Bojarczuk, A., Jelonkiewicz, E., Jelonkiewicz, Ł. & Lenart-Boroń, A. (2019). Changes in the quality of shallow groundwater in agriculturally used catchment in the Wiśnickie Foothills (Southern Poland), Archives of Environmental Protection, 45, 1, pp. 19–25. DOI:10.24425/aep.2019.126420
  7. Central Hydrogeological Data Bank, Groundwater Bodies characteristics, Major Groundwater Reservoirs, www.pgi.gov.pl, access on 03.2021
  8. Corine Land Cover, 2018, https://clc.gios.gov.pl, access on 04.2021
  9. Dąbrowski, S., Przybyłek, J. & Górski, J. (2007). Warta lowland subregion, [in] Paczyński, B.  Sadurski, A., (Eds), Regional hydrogeology of Poland, Państwowy Instytut Geologiczny, Warsaw. (in Polish)
  10. Dąbrowski, S., Rynarzewski, W., Straburzyńska–Janiszewska, R., Janiszewska, B. & Pawlak, A. (2009). Identification of groundwater level changes due to anthropopression in the Warta water region, Biuletyn Państwowego Instytutu Geologicznego, 436, pp. 77-86. (in Polish)
  11. Digital Elevation Model, resolution 100100 m, www.gugik.gov.pl, access on 03.2021
  12. Dragon, K. & Górski, J. (2015). Identification of groundwater chemistry origins in a regional aquifer system (Wielkopolska region, Poland). Environ Earth Sci. 73: pp. 2153–2167. DOI:10.1007/s12665-014-3567-0
  13. Dragon, K. (2013). Groundwater nitrate pollution in the recharge zone of a regional Quaternary flow system (Wielkopolska region, Poland). Environ Earth Sci. 68: pp. 2099–2109. DOI:10.1007/s12665-012-1895-5
  14. Duda, R., Witczak, S. & Żurek, A. (2011). Groundwater Vulnerability Map of Poland in scale 1:500 000. Ministry of the Environment. Cracow.
  15. Fiszer, J. & Derkowska-Sitarz, M. (2010). Forecast of development of depression cone and water inflows to Brown Coal Mine Konin including designed open pits Tomisławice and Ościsłowo, Biuletyn Państwowego Instytutu Geologicznego, 442: pp. 37-41. (in Polish)
  16. Galon, R. (1961). Morphology of the Noteć - Warta (or Toruń - Eberswalde) ice marginal streamway. Geographical Studies, Polish Academy of Sciences. Institute of Geography; no. 29, IGiPZ PAN; Wydaw. Geologiczne, Warsaw.
  17. Hydrogeological Map of Poland in the scale 1:50 000, Uppermost Aquifer, Vulnerability and Quality; Hydrogeological Map of Poland in the scale of 1:50 000, Uppermost Aquifer, Hydrodynamics and Occurrence, Geological Map of Poland in the scale 1:50 000, www.geoportal.pgi.gov.pl, access on 04.2021
  18. Jamorska, I. (2015). Conditions for the occurrence of groundwater in southern Kujawy Region, Przegląd Geologiczny, 63, 10/1: pp. 756-761. (in Polish)
  19. Krogulec, E. (2004). Vulnerability Assessment of Groundwater Pollution in the River Valley on the Basis of Hydrodynamic Evidences. Wydawnictwo UW, Warszawa, Poland. (in Polish)
  20. Krogulec, E. (2011). Intrinsic and specific vulnerability of groundwater in a river valley. Biuletyn Państwowego Instytutu Geologicznego 445, 337–344. (in Polish)
  21. Ławniczak, A.E., Zbierska, J., Nowak, B., Achtenberg, K., Grześkowiak, A. & Kanas, K. (2016). Impact of agriculture and land use on nitrate contamination in groundwater and running waters in central-west Poland. Environ Monit. Assess., 188, 172. DOI:10.1007/s10661-016-5167-9
  22. Local database, NUTS 5, https://stat.gov.pl, access on 04.2021
  23. Map of soil types on a scale of 1:500 000 (updated 2005-2010), www.iung.pl, access on 05.2021
  24. Margat, J. (1968). Groundwater Vulnerability Maps, Conception-Estimation-Mapping; EEC Institut Europeen de l’ Eau: Paris, 1968.
  25. Martínez-Bastida, J.J., Arauzo, M. & Valladolid, M. (2010) Intrinsic and specific vulnerability of groundwater in central Spain: the risk of nitrate pollution. Hydrogeology Journal, 18, pp. 681–698.
  26. Monitoring Data Base – MONBADA, gios.gov.pl, access on 04.2021
  27. Napolitano, P. & Fabbri, A.G. (1996). Single-parameter sensitivity analysis for aquifer vulnerability assessment using DRASTIC and SINTACS, Application of Geographic Information Systems in Hydrology and Water Resources Management (Proceedings of the Vienna Conference), IAHS Publ. no. 235, pp. 559–566.
  28. NUTS 5 = LAU: Local Administrative Units, https://ec.europa.eu/, access on 05.2021
  29. Perrin, J., Pochon, A., Jeannin P.Y. & Zwahlen, F. (2004). Vulnerability assessment in karstic areas: validation by field experiments. Environmental Geology, 46:237–245. DOI:10.1007/s00254-004-0986-3
  30. Regulation of the Council of Ministers of February 14, 2020 on the adoption of the "Action Program to reduce water pollution with nitrates from agricultural sources and to prevent further pollution". Journal of Laws 2020. 243, www.isap.sejm.gov.pl, access on 07.2021. (in Polish)
  31. Regulation of the Director of Regional Water Management Authority in Poznań of July 12, 2012 on the determination of waters in the Warta water region, within the boundaries of the Wielkopolska Province, sensitive to pollution with nitrogen compounds from agricultural sources and particularly vulnerable areas, from which the outflow of nitrogen from agricultural sources to these waters should be limited. Journal of Laws of the Wielkopolska Province 2012.3143; https://poznan.wody.gov.pl/; access on 05.2021. (in Polish)
  32. Regulation of the Minister of the Environment of December 23, 2002 on the criteria for determining waters sensitive to pollution with nitrogen compounds with agricultural sources (2002). Journal of Laws 2002. 241. 2093, www.isap.sejm.gov.pl, access on 04.2021. (in Polish)
  33. Report on the implementation of Directive 91/676/EEC in the years 2016 – 2020 (2021). Ministry of Maritime Economy and Inland Navigation, https://www.gov.pl/attachment/b0a430f6-0555-4b0c-ab82-70d46ae1ffbc, access on 07.2021. (in Polish)
  34. Saha, D. & Alam, F. (2014). Groundwater vulnerability assessment using DRASTIC and Pesticide DRASTIC models in intensive agriculture area of the Gangetic plains, India. Environmental Monitoring and Assessment. DOI: 10.1007/s10661-014-4041-x
  35. Sarkar, M. & Pal, S.C. (2021). Application of DRASTIC and Modified DRASTIC models for modeling groundwater vulnerability of Malda District in West Bengal. J. of the Indian Society of Remote Sensing, 49(5), pp. 1201–1219. DOI: 10.1007/s12524-020-01176-7
  36. Secunda, S., Collin, M. L. & Melloul, A. J. (1998). Groundwater vulnerability assessment using a composite model combining DRASTIC with extensive agricultural land use in Israel’s Sharon region. Journal of Environmental Management. DOI: 10.1006/jema.1998.0221
  37. Shirazi, S.M., Imran, H.M. & Akib, S. (2012). GIS-based DRASTIC method for groundwater vulnerability assessment: a review, Journal of Risk Research, 15:8, 991-1011, DOI:10.1080/13669877.2012.686053
  38. Stewart, B.A., Viets, F.G. Jr. & Hutchinson, G.L. (1968). Agriculture’s effect on nitrate pollution of groundwater. J. Soil Water Conserv. 23, pp. 13–15.
  39. Szczepański, J. & Straburzyńska – Janiszewska, R. (2011). Forecast of the extent of the depression for the coal open pit Mąkoszyn – Grochowiska KWB „Konin” S.A., Biuletyn Państwowego Instytutu Geologicznego 445: 671-684. (in Polish)
  40. Voudouris, K., Mandrali, P. & Kazakis, N. (2018). Preventing groundwater pollution using vulnerability and risk mapping: the case of the Florina Basin, NW Greece. Geosciences 8(4), 129. DOI:10.3390/geosciences8040129
  41. Voutchkova, D.D., Schullehner, J., Rasmussen, P. & Hansen, B. (2021). A high-resolution nitrate vulnerability assessment of sandy aquifers (DRASTIC-N). Journal of Environmental Management 277, 11133.0.
  42. Vrba, J. & Zaporozec, A. (1994). Guidebook on mapping groundwater vulnerability. International Association of Hydrogeologists (International Contributions to Hydrogeology 16). Verlag Heinz Heise, Hannover.
  43. Wiatkowski, M., Wiatkowska, B., Gruss, Ł., Rosik-Dulewska, C., Tomczyk, P., Chłopek, D. (2021) Assessment of the possibility of implementing small retention reservoirs in terms of the need to increase water resources, Archives of Environmental Protection, 47, 1, pp. 80–100, DOI 10.24425/aep.2021.136451
  44. Wrzesiński, D. & Perz, A. (2016). Features of the river runoff regime in the Warta catchment area. Bad. Fizjograf., R. 7, Ser. A – Geogr. Fiz. (A67), PTPN, Poznań, pp. 289–304. (in Polish)
  45. Yang, J., Tang, Z., Jiao, T. & Muhammad, A.M. (2017). Combining AHP and genetic algorithms approaches to modify DRASTIC model to assess groundwater vulnerability: a case study from Jianghan Plain, China. Environ Earth Sci., 76, 426 (2017). DOI:10.1007/s12665-017-6759-6 .
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Authors and Affiliations

Sebastian Zabłocki
1
Sadżide Murat-Błażejewska
2
Joanna Alicja Trzeciak
1
Ryszard Błażejewski
2

  1. University of Warsaw, Poland
  2. Poznan University of Life Sciences, Poland
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Abstract

jakość wód podziemnych. W badaniach zastosowano trzy gatunki roślin, jako możliwe kierunki stosowania osadów ściekowych: trawa - rekultywacja gleb zdegradowanych, kukurydza - produkcja pasz, wierzba- wykorzystanie energetyczne biomasy. Jako kontrolę zastosowano lizymetry pozbawione roślinności. Przyjęto nastepujące dawki osadów ściekowych: O. IO, 50. 110,225 i 450 Mg s.m./ha. Statystycznie istotna. liniowa zależność pomiędzy dawką osadów a wielkością przewodności elektrolitycznej właściwej (EC), ChZT oraz azotanów wskazuje na potencjalne zagrożenie zanieczyszczenia wód podziemnych przy przyrodniczym wykorzystaniu osadów ściekowych, szczególnie w przypadku wysokich dawek osadów przekraczających 50 Mg s.m./ha. Zależności te oraz ryzyko zanieczyszczenia wód podziemnych obserwowano przez trzy lata doświadczenia dla wskaźników zanieczyszczenia EC i ChZT. W przypadku azotanów, zagrożenie ich migracji stwierdzono jedynie w pierwszym roku badań. Dodatkowo stężenia metali ciężkich oraz obecność patogenów w wodach gruntowych była na niskim poziomic. Stwierdzono, że zastosowane rośliny nie zmniejszyły negatywnego wpływu osadów ściekowych na jakość wód podziemnych.
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Authors and Affiliations

Marek Agopsowicz
Andrzej Białowiec
Piotr Pijarczyk
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Abstract

In order to maintain and improve water quality, man has an increasing need to understand the relations among basin land use and in stream water quality. Being concerned about quality and quantity status of European waters European Union has adopted Water Framework Directive (2000/60/EU). The process of pressure and impact analyses and water status assessment is termed, in short, as “first characterisation” of water bodies. In accordance to WFD programmes of measures have to be developed by 2009. In WFD programmes existing measures for water protection directed by other EU directives such are Nitrate, Urban Waste Water, Dangerous Substances and IPPC will be further developed and new added. In the paper, we describe the first characterisation of the Slovene waters and show cross compliance of the Nitrate and Water Framework Directives in Slovenia

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Authors and Affiliations

Marina Pintar
Lidija Globevnik
Urška Bremec
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Abstract

In the present work, the dried biomass of soil isolated fungus Eurotium cristatum was used for synthesizing silver na-noparticles (AgNPs). The synthesized AgNPs were spherical in shape with average diameter of 16.56 nm and displayed maximum absorbance at 418. Fourier transform infrared (FTIR) study indicated the presence and binding of proteins with myco-produced silver nanoparticles. The optimum conditions for AgNPs biosynthesis were found to be at temperature of 40°C, pH of 8.0, substrate concentration of 500 ppm and fungal biomass wt. of 0.8 g. The AgNPs showed antibacterial ac-tivity against Staphylococcus aureus, Listeria monocytogenes, Escherichia coli and Shigella flexneri. AgNPs was built-in thin film nanocomposite (TFNC) membrane and the impacts of nanomaterial composition on membrane properties and de-salination process were studied. The AgNPs produced membrane TFNC had better filtration performances than pure thin film composite membrane TFC. The TFNC membrane had enhanced water flux (32.0 vs. 16.5 dm3∙m–2∙h–1) and advanced NaCl rejection (91.7 vs. 89%) compared to the TFC membrane. A pot experiment was conducted to evaluate the effect of the irrigation with desalinated water on yield and productivity of essential oil of the sweet basil (Ocimum basilicum L.) and lavender (Lavandula multifida L.). The irrigation with desalinated water reduced significantly the soil reaction, soil electri-cal conductivity (EC), sodium adsorption ratio and exchangeable sodium percent in rhizospheric soil, it also enhanced the growth and oil yield of both plants compared with those irrigated with salt water.

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Authors and Affiliations

Rabaa Yaseen
Yousra Kotp
Doaa Eissa
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Abstract

In this research different methods for measuring water quality indices were conducted to investigate the performance of the newly designed, constructed and operated 9-Nissan water treatment plant, Iraq. Data gathering and implementation took place throughout winter and summer. Water samples were taken periodically, according to the standard method, the re-search was carried out by collecting different random samples for eight months (Jun. 2015–Jan. 2016) and measuring (tur-bidity, total hardness, pH, total dissolved solids, suspended solids, Cl–, Mg2+, Fe2+,NO3–, NH3+) for each sample. Five dif-ferent approaches and methodologies of calculating the water index were applied. The results revealed that the Water Qual-ity Indices varied from 70.55 to 88.24, when applying Canadian Council of Ministers of the Environment Water Quality Index (CCMEWQI) and British Columbia water quality index (BCWQI) geometric weighted mean respectively. All the results, from the five approaches indicated good water quality, multiple regression analyses were conducted for turbidity, total hardness and suspended solids, they found that these parameters are strongly related to each other and to other pa-rameters.

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Authors and Affiliations

Hayder M. Abdul-Hameed

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