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Abstract

In Poland, in recent years, there has been a rapid accumulation of sewage sludge – a by-product in the treatment of urban wastewater. This has come about as a result of infrastructure renewal, specifically, the construction of modern sewage treatment plants. The more stringent regulations and strategic goals adopted for modern sewage management have necessitated the application of modern engineering methodology for the disposal of sewage sludge. One approach is incineration. As a consequence, the amount of fly ash resulting from the thermal treatment of municipal sewage sludge has grown significantly. Hence, intensive work is in progress for environmentally safe management of this type of waste. The aim of the experiment was to evaluate the possibility of using the fly ash that results from municipal sewage sludge thermal treatment (SSTT) as an additive to hardening slurries. The article presents the technological and functional parameters of hardening slurries with an addition of fly ash obtained by SSTT. Moreover, the usefulness of these slurries is analyzed on the basis of their basic properties, i.e., density, contractual viscosity, water separation, structural strength, volumetric density, hydraulic conductivity, compressive and tensile strength. The research on technological and functional properties was carried out, the aim of which was to determine the practical usefulness of the hardening slurries used in the experiment. Subsequently, leaching tests were performed for heavy metals in the components, the structure of the hardening slurries. An experiment showed leaching of hazardous compounds at a level allowing their practical application. The article presents the potential uses of fly ash from SSTT in hardening slurry technology.
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Bibliography

  1. Asavapisit, S., Naksrichum, S. & Harnwajanawong, N. (2005). Strength, lechability, and microstructure characteristics of cement-based solidified plating sludge. Cement and Concrete Research 35, pp. 1042–1049.
  2. Batchelor, B. (2006). Overview of waste stabilization with cement. Waste Management 26, pp. 689–698.
  3. Bobrowski, A., Gawlicki, M. & Małolepszy, J. (1997). Analytical Evaluation of Immobilization of Heavy Metals in Cement Matrices, Environmental Science & Technology, 31, 3, pp. 745-749.
  4. Chang, F.C., Lin, J.D., Tsai, C.C. & Wang, K.S. (2010). Study on cement mortar and concrete made with sewage sludge ash. Water Science and Technology, 62, 7, pp. 1689-1693, 2010.
  5. Chiang, K. Y., Chou, P. H., Hua, C. R., Chien, K. L. & Cheeseman, C. (2009). Lightweight bricks manufactured from water treatment sludge and rice husks. Journal of hazardous materials. 171 (1-3), pp. 76-82.
  6. Chou, J.-D., Wey, M.-Y. & Chang, S.-H. (2009). Evaluation of the distribution patterns of Pb, Cu and Cd from MSWI fly ash during thermal treatment by sequential extraction procedure. Journal of Hazardous Materials 162 (2–3), pp. 1000–1006.
  7. Elicker, C., Sanches Filho P.J. & Castagno K.R.L. (2014). Electroremediation of heavy metals in sewage sludge. Braz. J. Chem. Eng. Sao Paulo, 31(2), pp. 365–371.
  8. EN 450-1:2012. (2012). Fly ash for concrete. Definition, specifications and conformity criteria.
  9. Falaciński, P. (2012). Possible applications of hardening slurries with fluidal fly ashes in environment protection structures. Archives of Environmental Protection. 38, 3, pp. 91-104. DOI: 10.2478/v10265-012-0031-7.
  10. Falaciński, P. & Szarek, Ł. (2016).Possible Applications of Hardening Slurries with Fly Ash from Thermal Treatment of Municipal Sewage Sludge in Environmental Protection Structures. Archives of Hydro-Engineering and Environmental Mechanics, 63, 1, pp. 47–61. DOI: 10.1515/heem-2016-0004
  11. Gawdzik, J. & Latosińska, J. (2014). Assessment of sewage sludge incineration fly-ash heavy metal immobilization. Engineering and Protection of Environment, t. 17, vol. 3, pp. 415-421.
  12. Guo, B., Liu, B., Yang, J. & Zhang, S. (2017).The mechanisms of heavy metal immobilization by cementitious material treatments and thermal treatments: A review. Journal of environmental management, 193, pp. 410-422.
  13. Hoi, K. L., Barford, J.P. & Makay, G. (2010). Utylization of Incineration Waste Ash Residues in Portland Cement Clinker, Chemical Engineering Transaction, 21, pp. 757-762.
  14. Ibragimow, A., Głosińska, G., Siepak, M. & Walna, B. (2010). Preliminary studies of heavy metal pollution in floodplain sediments. Works and Geographic Studies 44, pp. 233–247.
  15. Jakob, A., Stucki ,S. & Kuhn, P. (1995). Evaporation of heavy metals during the heat treatment of municipal solid waste fly ash. Environmental Science and Technology 29, pp. 2429–2436.
  16. Jama-Rodzeńska, A., Bocianowski, J. & Nowak, W. (2014). Impact of municipal sewage sludge on heavy metal content in the sprouts of Salix viminalis L. clones. ZPPNR 576, pp. 45–56. (in Polish)
  17. Kledynski, Z. & Rafalski, L. (2009). Hardening slurries, Warszawa, KILiW PAN, IPPT PAN.(in Polish)
  18. Le Forestier, L. & Libourel, G. (2008). High temperature behavior of electrostatic precipitator ash from municipal solid waste combustors. Journal of Hazardous Materials 154 (1–3) pp. 373–380.
  19. Li, Z. & Shuman, L.M. (1996). Redistribution of forms of zinc, cadmium and nickel in soils treated with EDTA. Sci Total Environ 191, pp. 95–107.
  20. Łukawska, M. (2014). Speciation analysis of phosphorous in sewage sludge after thermal incineration. Inżynieria i Ochrona Środowiska, 17 (3), pp. 433-439 (in Polish)..
  21. Marcinkowski, T. (2004). Alkaline stabilization of municipal sewage sludges. Scientific Papers of the Institute of Environment Protection Engineering of the Wroclaw University of Technology No. 76, Poland.
  22. Nowaka, B., Rochaa, S.F., Aschenbrennerb, F., Rechbergerb, H. & Wintera, F. (2012). Heavy metal removal from MSW fly ash by means of chlorination and thermal treatment: Influence of the chloride type. Chemical Engineering Journal 179 pp. 178– 185.
  23. Petruzzelli, G., Szymura, I., Lubrano,L. & Pezzarossa, B. (1989). Chemical speciation of heavy metals in different size fractions of compost from solid urban wastes. Environetal Technology Letter. 10, pp. 521 – 526.
  24. Polowczyk, I., Bastrzyk, A., Sawiński, W., Koźlecki, T., Rudnicki, P., Sadowski, Z. & Sokołowski, A. (2010). Sorption properties of fly ash from coal burning. Chemical Engineering and Apparatus, 49(1), pp. 93–94.
  25. Poluszyńska. J. & Ślęzak, E. (2015). Characteristics of biomass incineration ashes and the assessment of their possible use for natural purposes. Scientific Works of Institute of Ceramics and Building Materials. 23, pp. 71-78.
  26. Renbo, Y., Wing-Ping, L. & Pin-Han, W. (2012). Basic characteristics of leachate produced by various washing processes for MSWI ashes in Taiwan, Journal of Environmental Management, 104, pp. 67-76.
  27. Rodríguez, N. H., Ramírez, S. M., Varela, M. B., Guillem, M., Puig, J., Larrotcha, E. & Flores, J. (2010). Re-use of drinking water treatment plant (DWTP) sludge: characterization and technological behaviour of cement mortars with atomized sludge additions. Cement and Concrete Research, 40(5), pp. 778-786.
  28. Rosik-Dulewska, Cz. (2001). The content of fertilizer ingredients and heavy metals with their fractions in municiapl waste composts. Problem Journals of Advances in Agricultural Sciences 477, pp. 467-477.
  29. Sánchez-Chardi, A. (2016). Biomonitoring potential of five sympatric Tillandsia species for evaluating urban metal pollution (Cd, Hg and Pb). Atmospheric Environment, 131, pp. 352-359.
  30. Sørum, L., Frandsen-Flemming, J. & Hustad, J. E. (2008). On the fate of heavy metals in municipal solid waste combustion part I: devolatilisation of heavy metals on the grate. Fuel, 82 (18) pp. 2273–2283.
  31. Struis, R.P.W., Ludwig, C., Lutz, H. & Scheidegger A.M. (2004). Speciation of zinc in municipal solid waste incinerator fly ash after heat treatment: an X-ray absorption spectroscopy study. Environmental Science and Technology, 38, pp. 3760–3767.
  32. Szarek, Ł. (2020). Leaching of heavy metals from thermal treatment municipal sewage sludge fly ashes. Archives of Environmental Protection, 46, 3, pp. 49-59, DOI:10.24425/aep.2020.134535.
  33. Szarek, Ł., Falaciński P. & Wojtkowska, M. (2018). Immobilization of selected heavy metals from fly ash from thermal treatment of municipal sewage sludge in hardening slurries, Archives of Civil Engineering, 64, 3, pp.131-144. DOI:10.2478/ace-2018-0034.
  34. Szarek, Ł. & Wojtkowska, M. (2018). Properties of fl y ash from thermal treatment of municipal sewage sludge in terms of EN 450-1. Archives of Environmental Protection 44, 1, pp. 63–69. DOI:10.24425/118182.
  35. Teixeira, S. R., Santos, G. T. A., Souza, A. E., Alessio, P., Souza, S. A. & Souza, N. R. (2011). The effect of incorporation of a Brazilian water treatment plant sludge on the properties of ceramic materials. Applied Clay Science, 53(4), pp. 561-565.
  36. Ure, A.M., Davidson, C.M. & Thomas, R.P. (1995). Single and sequential extraction schemes for tracę metal speciation in soil and sediment, Techniąues and Instruinentation in Analytical Chemistry, 17, pp. 505-523.
  37. Vassilev, S., Baxter, D., Andersen, L. & Vassileva, C. (2013a). An overview of the composition and application of biomass ash. Part 1.Phase–mineral and chemical composition and classification. Fuel, 105, pp. 40–76.
  38. Vassilev, S., Baxter, D., Andersen, L. & Vassileva, C. (2013b). An overview of the composition and application of biomass ash. Part 2. Potential utilisation, technological and ecological advantages and challenges. Fuel, 105, pp. 19-39.
  39. Wojtkowska, M. & Bogacki, J. (2012). Use of Speciation Analysis for Monitoring Heavy Metals in the Bottom Sediments of the Utrata River‎, Environmental Protection, 34, 4, pp. 43-46.
  40. Woodard, C. (2006). Industrial Waste Treatment Handbook. Second Edition, Elselvier, USA.
  41. Wzorek, Z. (2008). Recovery of phosphorous compounds from thermally processed waste and their application as a substitute for natural phosphorous raw materials. Kraków, Publishing House of the Cracow University of Technology.
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Authors and Affiliations

Paweł Falaciński
1
ORCID: ORCID
Małgorzata Wojtkowska
1

  1. Warsaw University of Technology, Faculty of Building Services, Hydro and Environmental Engineering, Warsaw
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Abstract

Sewage sludge from municipal wastewater treatment plants is currently a serious environmental problem, given its diversity due to the variability of time and heavy metal content. Current research on the monitoring of heavy metals is based on the determination of Pb, Cd, Hg, Ni, Zn, Cu and Cr. This makes any thallium content data difficult to access. The study estimated the degree of contamination of sewage sludge with thallium. The sludge samples came from a sewage treatment plant located in Poland. The results are presented for the total concentration of thallium and its mobile forms. These samples were analyzed by differential pulse voltammetry. The results showed that the average thallium content was 0.203 μg/g and its mobile form was 0.025 μg/g. The conducted research shows that almost 13% of thallium from sewage sludge can be gradually released into the environment.
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Bibliography

  1. Ahumada, I., Escudero, P., Ascar, L., Mendoza, J.& Richter, P. (2004). Extractability of Arsenic, Copper, and Lead in Soils of a Mining and Agricultural Zone in Central Chile. Communications in Soil Science and Plant Analysis, 35, pp. 1615-1634. DOI:10.1081/CSS-120038558
  2. Alvarez-Ayuso, E., Otones, V., Murciego, A., Garcia-Sanchez, A. & Santa Regina, I. (2013). Zinc, cadmium and thallium distribution in soils and plants of area impacted by sphalerite-bearing mine wastes. Geoderma, 207-208, pp. 25-34. DOI:10.1016/j.geoderma.2013.04.033
  3. Council Directive of 21.III.1991 concerning urban wastewater treatment. 91/271/EEC.
  4. De La Rochebrochard, S., Naffrechoux, E., Drogui, P., Mercier, G. & Blais, J. (2013). Low frequencyultrasound-assisted leaching of sewage sludge for toxic metal removal, dewatering and fertilizingproperties preservation. Ultrasonics Sonochemistry, 20, pp. 109-117. DOI:10.1016/j.ultsonch.2012.08.001
  5. Dmowski, K., Kozakiewicz, A. & Kozakiewicz, M. (2002). Bioindication thallium search in southern Poland. Kosmos, 51(2), pp. 151–163. (in Polish)
  6. Finkelman, R. (1999). Trace elements in coal. Environmental and health significance. Biological Trace Element Research, 67(3), pp. 197–204. DOI:10.1007/BF02784420 .
  7. Frankowski, M., Zioła-Frankowska A., Kowalski, A. & Siepak., J. (2010). Fractionation of heavy metals in bottom sediments using Tessier procedure. Environmental Earth Sciences, 60, pp. 1165-1178. DOI:10.1007/s12665-009-0258-3
  8. Fytili, D. & Zabaniotou, A. (2008). Utilization of sewage sludge in EU application of old and new methods a review. Renewable and Sustainable Energy Reviews, 12 (1), pp. 116-140. DOI: 10.1016/j.rser.2006.05.014
  9. Galván–Arzate, S. & Santamaria, A. (1998). Thallium toxicity. Toxicology Letters, 99(1), pp. 1–13. DOI:10.1016/s0378-4274(98)00126-x
  10. Ibragimow, A., Głosińska., G., Siepak, M. & Walna, B. (2010). Heavy metals in fluvial sediments of the Odra river flood plains-introductory research. Quaestiones geographicae, 29, pp. 37-47. DOI:10.2478/v10117-010-0004-7
  11. Kowalik, R,, Gawdzik, J., Gawdzik. B. & Gawdzik, A. (2020). Analysis of the mobility of heavy metals in sludge for the sewage treatment plant in Daleszyce. Structure and Environment, 12, 85 DOI: 10.30540/sae-2020-010
  12. Larner, B., Seen, A. & Townsend, A. (2006). Comparative study of optimized BCR sequential extraction scheme and acid leaching of elements in the certified reference material NIST 2711. Analytica Chimica Acta, 556, pp. 444-449. DOI:10.1016/j.aca.2005.09.058
  13. Łukaszewski, Z., Jakubowska, M., Zembrzuski, W., Karbowska, B. & Pasieczna,A. (2010). Flow – injection differential pulse anodic stripping voltammetry as a tool for thallium monitoring in the environment. Electroanalysis, 22 (17-18), pp. 1963-1966. DOI:10.1002/elan.201000151
  14. Lukaszewski, Z., Karbowska, B., Zembrzuski, W. & Siepak, M. (2012). Thallium in fractions of sediments formed during the 2004 tsunami in Thailand. Ecotoxicology and Environmwntal Safety, 80, pp. 184-189. DOI:10.1016/j.ecoenv.2012.02.026
  15. Madrid, F., Reinoso, R., Florido, M., Barrientos, E., Ajmone - Marsan, F., Davidson, C. & Madrid, L. (2007). Estimating the extractability of potentially toxic metals in urban soils: A comparison of several extracting solutions. Environmental Pollution, 147, pp. 713-722. DOI:10.1016%2Fj.envpol.2006.09.005
  16. Merrington, G., Oliver, I., Smernik., R. & McLaughlin, M. (2003). The influence of sewage sludge properties on sludge-borne metal availability. Advances in Environmental Research, 8, pp.21-36. DOI:10.1016/S1093-0191(02)00139-9
  17. Pathak, A., Dastidar, M. & Sreekrishnan, T. (2009). Bioleaching of heavy metals from sewage sludge: A review. Journal of Environmental Management, 90, pp. 2343-2353. DOI:10.1016/j.jenvman.2008.11.005
  18. Querol, X., Fernandez-Turiel, J. & Lopez-Soler, A. (1995). Trace elements in coal and their behaviour during combustion in a large power station. Fuel, 74(3), pp. 331–343. DOI:10.1016/0016-2361(95)93464-O
  19. Quevauviller, Ph. (2002). SM&T activities in support of standardization of operationally defined extraction procedures for soil and sediment analysesd, [In] Ph. Quevauviller (ed.), Methodologies in soil and sediment fractionation studies. Single and sequential extraction procedures, European Commission, DG Research, Brussels, Belgium, pp. 1–9.
  20. Regulation of the Minister of the Environment (Rozporządzenie Ministra Środowiska z dnia 6 lutego 2015 r. w sprawie komunalnych osadów ściekowych. Dz.U. 2015 poz. 257)
  21. Regulation of the Minister of the Environment dated. 1.8.2002r. on municipal sewage sludge, Acts. Laws No. 134, item 1140.
  22. Resolution of the Council of Ministers of Polish Government No 233, 29.12.2006.
  23. Smith, K., Fowler, G., Pullket, S. & Graham, N. (2009). Sewage sludge-based adsorbents: A review of their production, properties and use in water treatment applications. Water Research, 43, pp. 2569-2594. DOI:10.1016/j.watres.2009.02.038.
  24. Svancara, I., Ostapczuk, P., Arunchalam, J., Emons, H.E. & Vytras, K. (1997). Determination of thallium in environmental samples using potentiometric stripping analysis. Method development, Electroanalysis, 9(1), pp. 26-31. DOI:10.1002/elan.1140090108
  25. Szarek, Ł. (2020). Leaching of heavy metals from thermal treatment municipal sewage sludge fly ashes. Archives of Environmental Protection, 46(3), pp. 49–59. DOI:10.24425/aep.2020.134535
  26. Vanek, A., Chrastny, V., Komarek, M., Penizek, V., Teper, L., Cabala, J. & Drabek, O. (2013). Geochemical position of thallium in soils from a smelter-impacted area. Journal of Geochemical Exploration, 124, pp. 176-182. DOI:org/10.1016%2Fj.gexplo.2012.09.002
  27. Vanek, A., Komarek, M., Vokurkova, P., Mihaljevic, M., Sebek, O., Panuskova, G., Chrastny, V. & Drabek, O. (2011). Effect of illite and birnessite on thallium retention and bioavailability in contaminated soils. Journal of Hazardous Materials, 191, pp. 170-176. DOI:10.1016/j.jhazmat.2011.04.065
  28. Viraraghavan, T. & Srinivasan, A. (2011). Thallium: Environmental Pollution and Health Effects, Encyclopedia of Environmental Health, pp. 325-333. DOI:10.1016/B978-0-444-52272-6.00643-7
  29. Woźniak, M., Żygadło, M. & Latońska, J. (2004). Assessing the Chemical Stability of Sewage Sludges Deposited Landfills under Natural Conditions. Ochrona Środowiska, 26, pp. 25-31.
  30. Xiao, T., Guha, J., Boyle, D., Liu, C. & Chen, J.(2004). Environmental concerns related to high thallium levels in soils and thallium uptake by plants in southwest Guizhou, China. Science of The Total Environment, 318(1-3), pp. 223-244. DOI:10.1016/S0048-9697(03)00448-0
  31. Zitko, V. (1975). Toxicity and pollution potential of thallium, The Science of the Total Environment, 4, pp. 185-192. DOI:10.1016/0048-9697(75)90039-X
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Authors and Affiliations

Bożena Karbowska
1
ORCID: ORCID
Włodzimierz Zembrzuski
1
ORCID: ORCID
Joanna Zembrzuska
1
ORCID: ORCID

  1. Poznan University of Technology, Faculty of Chemical Technology, Poland
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Abstract

Recent studies have shown that over half of the world’s population lives in urban areas, with the number of people living in slums growing by over 20 million per year and people living in urban areas lacking access to adequate sanitation. This study presents a review of the challenges facing fecal sludge management (FSM). A globally relevant issue in developing urban centers, especially in selected developing countries in West Africa was discussed. Some key findings of the review are that effective sanitation in developing areas depends on the chain of services and that one of the largest problems in sanitation is FSM. This study presents the initial steps toward understanding the main issues involving FSM in developing cities of West Africa. Results are intended to be used as a support for decisions on policies, strategies for FSM, and investments for improved treatment facilities in the region. The study suggests that governments and private sector organizations should develop adequate measures for handling fecal sludge.

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Authors and Affiliations

Emmanuel Alepu Odey
Bodjui Olivier Abo
Abdulmoseen Segun Giwa
Zifu Li
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Abstract

The article describes problems related to intensification of energy production at a sewage treatment plant. The authors analyze anaerobic co-digestion of sludge from a water treatment plant and sewage treatment plant. The authors proposed a methodology of the research and analyzed the preliminary results, which showed that co-digestion of sewage and water sludge enhanced biogas production. The authors hope that the results of the study will provide a basis for development of methodology for sludge control and disposal.

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Authors and Affiliations

Justyna Łucja Górka
Małgorzata Cimochowicz-Rybicka
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Abstract

Clay was admixtured with 1, 2, 3 and 10% of waste sludge precipitated from lead electroplating fluoroborate electrolyte. The sludge contained, besides 60.7% of lead, 3.7% of fluorine. Small standardized ceramic bricks were burnt at 980°C and then tested for physical and mechanical features (contraction, water soaking, freeze resistance, compressive strength) and for leaching with water saturated with carbon dioxide. The tests showed that 1% of added sludge did not change properties of ceramic bricks and leaching of lead and fluorine is not hazardous, while the larger admixtures result in spoiling of quality features. On burning fluorine is emitted to exhaust gases.
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Authors and Affiliations

Tadeusz Stefanowicz
Małgorzata Osińska
Stefania Napieralska-Zagozda
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Abstract

The present paper describes a cycle, which may be applied in sewage treatment plants as a system to convert biological waste into process heat and electricity. In sludge stabilization processes anaerobic fermentation acts as the source of methane, which can be used then to generate heat and electric current in gas turbines. Products of high-temperature oxidation can be utilized in organic Rankine cycles to generate electric power. Waste heat is used for heating the fermenting biomass. Energy balance equations mentioned in the thesis: organic Rankine cycle, regenerative gas turbine engine, anaerobic sludge stabilization system.

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Authors and Affiliations

Robert Matysko
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Abstract

This study investigated the Octyl Phenol Ethoxylate (OPE) removal potentials of raw and treated industrial treatment sludges (ITS) at different pH. Experiments were conducted in a set of 500 ml Erlenmeyer flasks, into which OPE solutions of 300 ml with different initial concentrations (50–300 μg/l) were added into. Adsorption of Octyl Phenol Ethoxylate from an aqueous solution into ITS105 (T=105°C), ITS300 (T=300°C), ITS600 (T=600°C) and ITS450 (pyrolyzed, T=450°C) was carried out at a room temperature. The OPE adsorption rate increase in the treatment sludge processed at 600°C. As opposed to the sludge treated at 105°C, the adsorption rate decreased as the concentration increased. The reason for this was that the porous structure was degraded at 600°C, and the surface charge balance was disrupted. ITS300 had a lower adsorption capacity for Octyl Phenol Ethoxylate removal than ITS105, ITS600 and ITS450 (pyrolyzed). The treatment sludge pyrolyzed at 450°C conformed with the Freundlich isotherm at pH 4 (R2=0.94) and pH 7 (R2=0.89). The treatment sludge heat-treated at 600°C conformed with the Freundlich isotherm at pH 4 (R2=0.97), pH 7 (R2=0.98) and pH 10 (R2=0.99). Additionally, for ITS600, the Brunauer, Emmett and Teller (BET) isotherm was valid at neutral pH. The OPE adsorption coefficient for ITS600 at pH 4 and pH 7 was calculated as 1.05 L/μg and 1.083 L/μg, respectively. According to the BET isotherm (for ITS600) the qm values at pH 4 and pH 7 were respectively 8.21 μg/g and 2.92 μg/g. The temperature of the adsorption value obtained with the Temkin isotherm showed that the interaction between the OPE and the adsorbent substances was not a chemical or ionic interaction but probably a physical interaction.
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Bibliography

1. Adegoke, K.A. & Bello, O.S. (2015). Dye sequestration using agricultural wastes as adsorbents, Water Resources and Industry, 12, pp.8–24, https://doi.org/10.1016/j.wri.2015.09.002
2. Araujo, C.S.T., Almeida, I.L.S., Rezende, H.C. & Marcionilo, S.M.L.O. (2018). Elucidation of mechanism involved in adsorption of Pb(II) onto lobeira fruit(Solanum ly-cocarpum) using Langmuir, Freundlich and Temkin isotherms, Microchemical Journal, 137, pp. 48-354, https://doi.org/10.1016/j.microc.2017.11.009
3. Auta, M. & Hameed, B.H. (2012). Modified mesoporous clay adsorbent for adsorp-tion isotherm and kinetics of methylene blue, Chemical Engineering Journal,198-199, pp. 219-227, https://doi.org/10.1016/j.cej.2012.05.075
4. Choi, H.J. & Yu, S.W. (2019). Biosorption of methylene blue from aqueous solution by agricultural bioadsorbent corncob, Environmental Engineering Research, 24, 1, pp.99-106, https://doi.org/10.4491/eer.2018.107
5. Cirja, M., Ivashechkin, P., Schäffer, A. & Corvini, P. F. (2008). Factors affecting the removal of organic micropollutants from wastewater in conventional treatment plants (CTP) and membrane bioreactors (MBR), Reviews in Environmental Science and Bio/Technology, 7, 1, pp. 61-78, DOI 10.1007/s11157-007-9121-8.
6. Kulkarni, S.J. (2015). A short review on arsenic removal from water, International Journal of Innovative Research in Science Engineering and Technology, 1, 1, pp. 253-256.
7. Dinçer, A.R., Güneş, Y., Hancı, T.Ö., Güneş, E. & Khoei, S. (2018). Effects of Endocrine Disrupting compounds (Bisphenol A and Octyl Phenol Ethoxylate) on COD removal efficiency, SAR Journal, 1, 2, pp. 35-4, doi: 10.18421/SAR12-01
8. Fan, X. & Zhang,X. (2008). Adsorption properties of activated carbon from sewage sludge to alkaline-black, Materials Letters, 62, 10-11, pp. 1704-1706, DOI: 10.1016/j.matlet.2007.09.085
9. Ferguson, P. L., Iden, C. R.& Brownawell, B. J. (2000). Analysis of alkylphenol etox-ylate metabolities in the aquatic environment using liquid chromatography electros pray mass spectrometry, Analytical Chemistry, 72, 18, pp. 4322-4330, https://doi.org/10.1021/ac000342n
10. Gu, H., Lin, W., Sun, S., Wu, C., Yang, F., Ziwei, Y., Chen, N., Ren, J. & Zheng, S. (2021). Calcium oxide modification of activated sludge as a low-cost adsorbent: Prep-aration and application in Cd(II) removal, Ecotoxicology and Environmental Safety, 209, 111760, https://doi.org/10.1016/j.ecoenv.2020.111760 11. Gupta, S. & Babu, B.V. (2009). Removal of toxic metal Cr(VI) from aqueous solu-tions using sawdust as adsorbent: Equilibrium, kinetics and regeneration studies, Chemical Engineering Journal, 150, 2-3, pp. 352-365, https://doi.org/10.1016/j.cej.2009.01.013
12. Jain,A.K., Gupta, V. K., Bhatnagar, A. & Suhas. (2003). Utilization of industrial wasteproducts as adsorbent for the removal of dyes, Journal of Hazardous Materials, 101, 1, pp. 31-42, https://doi.org/10.1016/S0304-3894(03)00146-8
13. Joshi, M., Bansal, R., Purwar, R. (2004). Colour removal from textile effluents, Indian Journal of Fibre and Textile Research, 29, 2, pp.239-259.
14. Khoshbouy, R., Takahashi, F. & Yoshikawa, K. (2019). Preparation of high sutface area sludge based activated hydrochar via hydrothermal carbonization and application in the removal of basic dye, Environmental Research, 175, pp. 457-467, DOI: 10.1016/j.envres.2019.04.002
15. Li, Y., Chang, F., Huang, B., Song, Y., Zhao, H. & Wang, K. (2020). Activated car-bon preparation from pyrolysis char of sewage sludge and its adsorption performance for organic compounds in sewage, Fuel, 266, 117053, https://doi.org/10.1016/j.fuel.2020.117053
16. Lonappan, L., Rouissi, T., Das, R.K., Brar, S.K., Ramirez, A.V., Verma, M., Suram-palli, R.Y. & Valero, J.R. (2016). Adsorption of metylene blue on biochar microparti-cles derived from different waste materials, Waste Management, 49, pp. 537-544, DOI: 10.1016/j.wasman.2016.01.015
17. Moreira, M.T., Noya, I. & Feijoo, G. (2017). The prospective use of biochar as adsorp-tion matrix – a review from a lifecycle perspective, Bioresource Technology, 246, pp. 135–141. https://doi.org/10.1016/j.biortech.2017.08.041
18. Namasivayam, C. & Yamuna, R.T. (1992). Removal of congo red from aqueous solu-tions by biogas waste slurry, Journal of Chemical Technology and Biotechnolo-gy, 53, 2, pp. 153-157, https://doi.org/10.1002/jctb.280530208
19. Nidheesh, P.V., Gandhimathi, R., Ramesh, S.T. & Singh, T.S.A. (2012). Kinetic anal-ysis of crystal violet adsorption on to bottom ash, Turkish Journal of Engineering and Environmental Sciences, 36, pp. 249-262, DOI: 10.3906/muh-1110-3.
20. Nimrod, A.C.& Benson, W.H. (1996). Environmental estrogenic effects of Alkyphe-nol ethoxylates, Critical Reviews in Toxicology, 26, 3, pp.335-364, DOI: 10.3109/10408449609012527.
21. Nunes A, Franca, S.A. & Olievera, L.S. (2009). Activated carbon from waste biomass: An alternative use for biodiesel production solid residues, Bioresource Technology, 100, 5, pp. 1786 -1792, https://doi.org/10.1016/j.biortech.2008.09.032
22. Perez, M., Torrades, F., Domenech, X. & Peral, J.F. (2002). Oxidation of Textile Effluents, Water Research, 36, 11, pp. 2703-2710, https://doi.org/10.1016/S0043-1354(01)00506-1
23. Ravenni, G., Gafaggi, G., Sarossy, Z., Nielsen, K.T.R., Ahrenfeldt, J. & Henriksen, U.B. (2020). Waste chars from wood gosification and wastewater sludge pyrolysis compared to commercial activated carbon for the removal of cationic and anionic dyes from aqueous solution, Bioresource Technology Reports, 10, 100421, DOI: 10.1016/j.biteb.2020.100421.
24. Ringot, D., Lerzy, B., Chaplain, K., Bonhoure, J. P., Auclair, E. & Larondelle,Y. (2007). In vitro biosorption of ochratoxin A on the yeast industry by-products: com-parison of isotherm models, Bioresource Technology, 98,9, pp. 1812–1821, DOI: 10.1016/j.biortech.2006.06.015.
25. Seo, J. H., Kim, N., Park, M., Lee, S., Yeon, S. & Park, D. (2020). Evaluation of metal removal performance of rod-type biosorbent prepared from sewage-sludge, Environmental Engineering Research, 25, 5, pp. 700-706, https://doi.org/10.4491/eer.2019.201
26. Sewu, D. D., Boakye, P. & Woo, S. H. (2017). Highly efficient adsorption of cationic dye bybiochar produced with Korean cabbage waste, Bioresource Technology, 224, pp. 206–213. https://doi.org/10.1016/j.biortech.2016.11.009
27. Sirianuntapiboon, S. & Saengow, W. (2004). Removal of Vat Dyes from Textile Wastewater Using Biosludge, Water Quality Research Journal, 39, 3, pp. 276-284, DOI: 10.2166/wqrj.2004.038.
28. Tan, I. A. W., Ahmad, A. L. & Hameed, B. H. (2009). Adsorption isotherms, kinetics, thermodynamics and desorption studies of 2,4,6-trichlorophenol on oil palm empty fruit bunch-based activated carbon, Journal of Hazardous Materials, 164, 2-3, pp. 473–482, https://doi.org/10.1016/j.jhazmat.2008.08.025
29. Tsai, W. T., Lai, C. W. & Su, T. Y. (2006). Adsorption of Bisphenol-A from Aqueous Solution onto Minerals and Carbon Adsorbats, Journal of Hazardous Materials, 134, 1-3, pp. 169-175. https://doi.org/10.1016/j.jhazmat.2005.10.055
30. Umar, M., Roddick, F., L.Fan. & Aziz, H.A. (2013). Application of ozone for the re-moval of bisphenol A from water and wastewater - A review, Chemosphere, 90, 8, pp. 2197-2207, https://doi.org/10.1016/j.chemosphere.2012.09.090
31. Vera, L. M., Bermejo, D., Uguna, M. F., Garcia, N., Flores, M. & Gonzalez, E. (2019). Fixed bed column modeling of lead(II) and cadmium(II) ions biosorption on sugarcane bagasse, Environmental Engineering Research, 24, 1, pp. 33-37, https://doi.org/10.4491/eer.2018.042
32. Vijayaraghavan, K., Padmesh, T. V. N., Palanivelu, K. &Velan, M. (2006). Biosorption of nickel (II) ions onto Sargassum wightii: Application of two-parameter and three-parameter isotherm models, Journal of Hazardous Materials, 133, 1-3, pp. 304–308, https://doi.org/10.1016/j.jhazmat.2005.10.016
33. Wang, H., Lou, X., Hu, Q. & Sun, T. (2021). Adsorption of antibiotics from water by using Chnese herbal medicine residues derived biochar: Preparation and properties studies, Journal of Molecular Liquids, 325, 114967, https://doi.org/10.1016/j.molliq.2020.114967.
34. Yang, X., Xu, G., Yu, H. & Zhang, Z. (2016). Preparation of ferric activated sludge based adsorbent from biological sludge for tetracycline removal, Bioresource Technology, 211, pp. 566-573, https://doi.org/10.1016/j.biortech.2016.03.140
35. Zhang, L., Pan, J., Liu, L., Song, K. & Wang, Q. (2019). Combined physical and chemical activation of sludge-based adsorbent enhances Cr(VI) removal from wastewater, Journal of Cleaner Production, 238, 117904, https://doi.org/10.1016/j.jclepro.2019.117904
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Authors and Affiliations

Ali Rıza Dinçer
1
İbrahim Feda Aral
1

  1. Namık Kemal University, Çorlu, Tekirdağ-Turkey
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Abstract

Throughout the world, considerable quantities of water treatment sludge (WTS) and sewage sludge (SS) are produced as waste. This study assessed in the laboratory, the possibility to use both waste products when they are incorporated as filler at 1% with relation to the total mass of a hot mix asphalt - HMA. To this end, both waste products were initially reduced to ash through a calcination process. Resistance tests under monotonic load (Marshall and indirect tension tests), and cyclic load (resilient modulus test) were applied on mixes that contained WTS and SS. Besides, moisture damage (modified Lotmman test), and abrasion (Cantabro) resistance were assessed. An analysis of variance (ANOVA) test was performed in order to verify if the results are statically equal or not to those of the control HMA. As a general conclusion, it is reported that both materials show a resistance increase under monotonic load and higher stiffness under cyclic load (cohesion) when they are incorporated into the mix as filler despite the fact that the asphalt content used was less than the control mix. However, some problems are observed associated with moisture damage resistance, and friction wear (adherence).

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Authors and Affiliations

J.G. Bastidas-Martínez
J. Camapum De Carvalho
L.C. Lucena
M.M. Farias
H.A. Rondón-Quintana
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Abstract

The concentration of hydrocarbons in the yield of dry matter in ryegrass depended upon the sludge dose. The highest concentrations of hydrocarbons in ryegrass were found in a control object. In objects fertilized with waste activated sludge the highest concentration of hydrocarbons was found in ryegrass with 20% ofwaste activated sludge. After a two-year experiment, the highest concentration of hydrocarbons was found in the control object. In soil materials fertilized with waste activated sludge the concentration of hydrocarbons grew along with the sludge dose.
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Authors and Affiliations

Stanisław Kalembasa
Beata Wiśniewska
Mariusz Kluska
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Abstract

The concentration of hydrocarbons in the yield of dry matter in ryegrass depended upon the sludge dose. The highest concentrations of hydrocarbons in ryegrass were found in a control object. In objects fertilized with waste activated sludge the highest concentration of hydrocarbons was found in ryegrass with 20% ofwaste activated sludge. After a two-year experiment, the highest concentration of hydrocarbons was found in the control object. In soil materials fertilized with waste activated sludge the concentration of hydrocarbons grew along with the sludge dose.
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Authors and Affiliations

Anna Kiepas-Kokot
Anna Iwaniuk
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Abstract

The aim of the study was to estimate the effect otthe composting process in the container technology Kneer on E. coli inactivation. The bacteria placed in the special carriers were introduced into the composted material. The elimination rate of E. coli differed depending on both the carriers· location in the biomass and the thermal conditions. The most effective hygienization, nr the material was noticed in summer - after 48 h in the middle layer, 6 days in the top layer and 10 days in the bottom layer. In spring and autumn, the bacteria survived the longest in the bottom layer - 85 and 45 days, respectively. Apart from the high temperature, the research points out the action of other factors such as competition, antagonism and antibiosis.
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Authors and Affiliations

Beata Szala
Zbigniew Paluszak
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Abstract

In the context of resource utilization, the applications of waste biomass have attracted increasing attention.Previous studies have shown that forming biochar by heat treatment of sludge could replace the traditional sludge disposal methods, and sludge biochar is proved to be efficient in wastewater treatment. In this work, the pyrolysis, hydrothermal carbonization and microwave pyrolysis methods for preparing sludge biochar were reviewed, and the effects of different modification methods on the performance of sludge biochar in the synthesis process were comprehensively analyzed. This review also summarized the risk control of heavy metal leaching in sludge biochar, increasing the pyrolysis temperature and use of the fractional pyrolysis or co-pyrolysis were usually effectively meathods to reduce the leaching risk of heavy metal in the system, which is crucial for the wide application of sludge biochar in sewage treatment. At the same time, the adsorption mechanism of sludge biochar and the catalytic mechanism as the catalytic material in AOPs reaction, the process of radical and non-radical pathway and the possible impacts in the sludge biochar catalytic process were also analyzed in this paper
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Bibliography

  1. Antunes, E., Jacob, M. V., Brodie, G. & Schneider, P. A. (2018).Microwave pyrolysis of sewage biosolids: Dielectric properties, microwave susceptor role and its impact on biochar properties. Journal of Analytical and Applied Pyrolysis, 129, 93-100. DOI:10.1016/j.jaap.2017.11.023.
  2. Bogacki, J.P. & Al-Hazmi, H. (2017). Automotive fleet repair facility wastewater treatment using air/ZVI and air/ZVI/H2O2 processes. Archives of Environmental Protection, 43 (3), pp. 24–31. DOI:10.1515/aep-2017-002
  3. Borgulat, A., Zgórska. A. & Głodniok, M. (2022). Comparison of different municipal sewage sludge products for potential ecotoxicity. Archives of Environmental Protection, 48 (1), pp. 92–99. DOI:10.24425/aep.2022.140548
  4. Chandrasekaran, S., Basak, T. & Srinivasan, R. (2013).Microwave heating characteristics of graphite based powder mixtures. International Communications in Heat and Mass Transfer, 2013, 48, 22-27. DOI: 10.1016/j.icheatmasstransfer.2013.09.008.
  5. Chen, G., Tian, S., Liu, B., Hu, M., Ma, W., Li, X. (2020). Stabilization of heavy metals during co-pyrolysis of sewage sludge and excavated waste. Waste Management, 103, 268-275. DOI:10.1016/j.wasman.2019.12.031.42.
  6. Cherif Lahimer, M.; Ayed, N.; Horriche, J. & Belgaied, S. (2017). Characterization of plastic packaging additives: Food contact, stability and toxicity. Arabian Journal of Chemistry, 10, S1938-S1954. DOI: 10.1016/j.arabjc.2013.07.022.
  7. Danni, L., Rui, S., Li, X, J., Jing, G., Yu, Y, Z., Hao, R, Y. & Yong, C.A. (2020). review on the migration and transformation of heavy metals in the process of sludge pyrolysis. Resources, Conservation & Recycling, 185, 106452. DOI:10.1016/j.resconrec.2022.106452.
  8. Devi, P. & Saroha, A. K. (2014). Risk analysis of pyrolyzed biochar made from paper mill effluent treatment plant sludge for bioavailability and eco-toxicity of heavy metals. Bioresour Technology, 162, 308-315. DOI:10.1016/j.biortech.2014.03.093.
  9. Dong, Q., Zhang, S., Wu, B., Pi, M., Xiong, Y. & Zhang, H. (2019). Co-pyrolysis of Sewage Sludge and Rice Straw: Thermal Behavior and Char Characteristic Evaluations. Energy & Fuels, 34 (1), 607-615. DOI: 0.1021/acs.energyfuels.9b03800.
  10. Duan, D., Chen, D., Huang, L., Zhang, Y., Zhang, Y., Wang, Q., Xiao, G., Zhang, W., Lei, H. & Ruan, R. (2021). Activated carbon from lignocellulosic biomass as catalyst: A review of the applications in fast pyrolysis process. Journal of Analytical and Applied Pyrolysis, 158, 105246. DOI: 10.1016/j.jaap.2021.105246.
  11. Duan, X., Sun, H., Shao, Z. & Wang, S. (2018). Nonradical reactions in environmental remediation processes: Uncertainty and challenges. Applied Catalysis B: Environmental, 224, 973-982. DOI:10.1016/j.apcatb.2017.11.051.
  12. Fang, G., Li, J., Zhang, C., Qin, F., Luo, H., Huang, C., Qin, D. & Ouyang, Z. (2022). Periodate activated by manganese oxide/biochar composites for antibiotic degradation in aqueous system: Combined effects of active manganese species and biochar. Environmental Pollution, 300, 118939. DOI: 10.1016/j.envpol.2022.118939.
  13. Gan, Q., Hou, H., Liang, S., Qiu, J., Tao, S., Yang, L., Yu, W., Xiao, K., Liu, B., Hu, J., Wang, Y. & Yang, J. (2020). Sludge-derived biochar with multivalent iron as an efficient Fenton catalyst for degradation of 4-Chlorophenol. Science of The Total Environment, 725, 138299. DOI: 0.1016/j.scitotenv.2020.138299.
  14. Harvey, O. R., Herbert, B. E., Rhue, R. D. & Kuo, L. J. (2011). Metal interactions at the biochar-water interface: energetics and structure-sorption relationships elucidated by flow adsorption microcalorimetry. Environmental Science& Technology, 45 (13), 5550-6. DOI:10.1021/es104401h.
  15. Issaka, E., Amu-Darko, J. N., Yakubu, S., Fapohunda, F. O., Ali, N. & Bilal, M. (2022). Advanced catalytic ozonation for degradation of pharmaceutical pollutants-A review. Chemosphere, 289, 133208. DOI:10.1016/j.chemosphere.2021.133208.
  16. Jia, H, Z., Zhao, S., Zhou, X, H., Qu, C, T., Fan, D, D. & Wang, C, Y. (2017). Low-temperature pyrolysis of oily sludge: roles of Fe/Al-pillared bentonites. Archives of Environmental Protection, 43 (3), pp. 82–90. DOI: 0.1515/aep-2017-002.
  17. Jin, Z., Jun, W, J., Min, Y. W., Ravi, N., Yan, J, L., Yu, B., Man, Xin, Q, L., Ming, H, W., Christie, P., Yan, Z., Cheng, F, S. & Sheng D, S. (2020). Co-pyrolysis of sewage sludge and rice husk/ bamboo sawdust for biochar with high aromaticity and low metal mobility. Environmental Research, 191,110304. DOI:10.1016/j.envres.2020.110034.
  18. Kappler, A., Wuestner, M. L., Ruecker, A., Harter, J., Halama, M. & Behrens, S. (2014). Biochar as an Electron Shuttle between Bacteria and Fe(III) Minerals. Environmental Science & Technology Letters, 1 (8), 339-344. DOI:10.1021/ez5002209.
  19. Kim, E., Jung, C., Han, J., Her, N., Park, C. M., Jang, M., Son, A. & Yoon, Y. (2016). Sorptive removal of selected emerging contaminants using biochar in aqueous solution. Journal of Industrial and Engineering Chemistry, 36, 364-371. DOI:10.1016/j.jiec.2016.03.004.
  20. Li, H., Dong, X., da Silva, E, B., de Oliveira, L, M., Chen, Y. & Ma, L.Q. (2017). Mechanisms of metal sorption by biochars: Biochar characteristics and modifications. Chemosphere, 178, 466-478. DOI:10.1016/j.chemosphere.2017.03.072.
  21. Li, L., Cao, W., Wang, G., Peng, P., Liu, S., Jin, H., Wei, W. & Guo, L. (2022). Experimental and kinetic study of heavy metals transformation in supercritical water gasification of oily sludge. Journal of Cleaner Production, 373, 133898. DOI:10.1016/j.jclepro.2022.133898.
  22. Li, W, J., Jun, M., Yu, L, Z. Ghulam, H, B., Tida, G., Haibo, Z., Zhang, H. B., Li, Z. T., Yi, J. Yu. & Sheng, D. S. (2022). Co-pyrolysis of sewage sludge and metal-free/metal-loaded polyvinyl chloride (PVC) microplastics improved biochar properties and reduced environmental risk of heavy metals. Environmental Pollution, 302, 119092. DOI:10.1016\/j.envpol.2022.119092
  23. Li, Z., Deng, H., Yang, L., Zhang, G., Li, Y. & Ren, Y. (2018). Influence of potassium hydroxide activation on characteristics and environmental risk of heavy metals in chars derived from municipal sewage sludge. Bioresource Technology, 256, 216-223. DOI:10.1016/j.biortech.2018.02.013.
  24. Ma, J., Zhou, B., Zhang, H. & Zhang, W. (2020), Fe/S modified sludge-based biochar for tetracycline removal from water. Powder Technology, 364, 889-900. DOI:10.1016/j.powtec.2019.10.107.
  25. Smol, M., Kulczycka, J., Lelek, Ł., Gorazda, K. & Wzorek, Z. (2020). Life Cycle Assessment (LCA) of the integrated technology for the phosphorus recovery from sewage sludge ash (SSA) and fertilizers production. Archives of Environmental Protection, 46(2), pp. 42–52. DOI:10.24425/aep.2020.13347.
  26. Mian, M. M., Liu, G., Fu, B. & Song, Y. (2019). Facile synthesis of sludge-derived MnOx-N-biochar as an efficient catalyst for peroxymonosulfate activation. Applied Catalysis B: Environmental, 255, 117765. DOI:10.1016/j.apcatb.2019.117765.
  27. Nie, M., Yang, Y., Zhang, Z., Yan, C., Wang, X., Li, H. & Dong, W. (2014). Degradation of chloramphenicol by thermally activated persulfate in aqueous solution. Chemical Engineering Journal, 246, 373-382. DOI:10.1016/j.cej.2014.02.047.
  28. Oh, S. Y. & Seo, Y. D. (2016). Sorption of halogenated phenols and pharmaceuticals to biochar: affecting factors and mechanisms. Environment Science Pollution Research International, 23 (2), 951-61. DOI:10.1007/s11356-015-4201-8
  29. Peng, B., Liu, Q., Li, X., Zhou, Z., Wu, C. & Zhang, H. (2022). Co-pyrolysis of industrial sludge and rice straw: Synergistic effects of biomass on reaction characteristics, biochar properties and heavy metals solidification. Fuel Processing Technology, 230.107211. DOI:10.1016/j.fuproc.2022.107211.
  30. Piekarski, J., Dąbrowski, T., Dąbrowski, J. & Ignatowicz, K. (2021). Preliminary studies on odor removal in the adsorption process on biochars produced form sewage sludge and beekeeping waste. Archives of Environmental Protection, 47(2), pp.20–28. DOI:10.24425/aep.2021.137275
  31. Pulka, J., Wiśniewski, D., Gołaszewski, J. & Białowiec, A. (2016). Is the biochar produced from sewage sludge a good quality solid fuel. Archives of Environmental Protection, 42 (4), pp. 125–134. DOI:10.1515/aep-2016-0043
  32. Qiu, B., Shao, Q., Shi, J., Yang, C. & Chu, H. (2022). Application of biochar for the adsorption of organic pollutants from wastewater: Modification strategies, mechanisms and challenges. Separation and Purification Technology, 300, 12195. DOI:10.1016/j.seppur.2022.121925
  33. Shi, Q, D., Zheng, Y., Du, Y., Li, L., Yang, S., Zhang, G., Du, L., Wang, G., Cheng, M. & Liu, Y. (2022). The application of transition metal-modified biochar in sulfate radical based advanced oxidation processes. Environmental Research, 212 (Pt B), 113340. DOI:10.1016/j.envres.2022.113340.
  34. Streit, A. F. M., Cortes, L. N., Druzian, S. P., Godinho, M., Collazzo, G. C. Perondi, D. & Dotto, G. L. (2019). Development of high quality activated carbon from biological sludge and its application for dyes removal from aqueous solutions. Science Total Environmental, 660, 277-287. DOI:10.1016/j.scitotenv.2019.01.027
  35. Szarek, Ł. (2020). Leaching of heavy metals from thermal treatment municipal sewage sludge fly ashes. Archives of Environmental Protection, 46 (3), pp. 49–59. DOI:10.24425/aep.2020.134535
  36. Tang, J., Lv, H., Gong, Y. & Huang, Y. (2015). Preparation and characterization of a novel graphene/biochar composite for aqueous phenanthrene and mercury removal. Bioresource Technology, 196, 355-363. DOI:10.1016/j.biortech.2015.07.047.
  37. Wallace, C. A., Afzal, M. T. & Saha, G. C. (2019). Effect of feedstock and microwave pyrolysis temperature on physio-chemical and nano-scale mechanical properties of biochar. Bioresources and Bioprocessing, 6 (1).8. DOI:10.1016/j.jaap.2015.01.010.
  38. Wang, C., Zhang, X., Wang, W., Sun, J., Mao, Y., Zhao, X. & Song, Z. (2022). A stepwise microwave synergistic pyrolysis approach to produce sludge-based biochars: Optimizing and mechanism of heavy metals immobilization. Fuel, 314. (Apr.15) – 122770. DOI:10.1016/j.fuel.2021.122770.
  39. Wang, H., Guo, W., Liu, B., Si, Q., Luo, H., Zhao, Q. & Ren, N. (2020). Sludge-derived biochar as efficient persulfate activators: Sulfurization-induced electronic structure modulation and disparate nonradical mechanisms. Applied Catalysis B: Environmental, 279, 119361. DOI:10.1016/j.apcatb.2020.119361.
  40. Wang, J., Cai, J., Wang, S., Zhou, X., Ding, X., Ali, J., Zheng, L., Wang, S., Yang, L., Xi, S., Wang, M. & Chen, Z. (2022). Biochar-based activation of peroxide: multivariate-controlled performance, modulatory surface reactive sites and tunable oxidative species. Chemical Engineering Journal, 428, 131233. DOI:10.1016/j.cej.2021.131233
  41. Wang, J. & Wang, S. (2018). Activation of persulfate (PS) and peroxymonosulfate (PMS) and application for the degradation of emerging contaminants. Chemical Engineering Journal, 334, 1502-1517. DOI:10.1016/j.cej.2017.11.059.
  42. Wang, S. & Wang, J. (2019). Activation of peroxymonosulfate by sludge-derived biochar for the degradation of triclosan in water and wastewater. Chemical Engineering Journal, 356, pp. 350-358. DOI:10.1016/j.cej.2018.09.062
  43. Wang, X., Wei, Ch. Ch., Li, Z., Song, Y., Li, C. & Wang, Y. (2022). Co-pyrolysis of sewage sludge and food waste digestate to synergistically improve biochar characteristics and heavy metals immobilization. Waste Management, 141, 231-239. DOI:10.1016/j.wasman.2022.02.001.
  44. Wu, W., Zhu, S., Huang, X., Wei, W. & Ni, B, J. (2021). Mechanisms of persulfate activation on biochar derived from two different sludges: Dominance of their intrinsic compositions. Journal Hazard Materials, 408, 124454. DOI:10.1016/j.jhazmat.2020.124454.
  45. Xin, Z., Bao, W. Z., Hui, L. & Liu, J. L. (2022). Effects of pyrolysis temperature on biochar’s characteristics and speciation and environmental risks of heavy metals insewage sludge biochars Environmental Technology & Innovation, 26, 102288. DOI:10.1016/j.eti.2022.102288.
  46. Xu, L., Wu, C., Liu, P., Bai, X., Du, X., Jin, P., Yang, L., Jin, X., Shi, X. & Wang, Y. (2020). Peroxymonosulfate activation by nitrogen-doped biochar from sawdust for the efficient degradation of organic pollutants. Chemical Engineering Journal, 387, 124065. DOI:10.1016/j.cej.2020.124065.
  47. Yan, L., Liu, Y., Zhang, Y., Liu, S., Wang, C., Chen, W., Liu, C., Chen, Z. & Zhang, Y. (2020). ZnCl2 modified biochar derived from aerobic granular sludge for developed microporosity and enhanced adsorption to tetracycline. Bioresource Technology, 297, 122381. DOI:10.1016/j.biortech.2019.122381.
  48. Yang, T, S., Zhang, Y., Cao, X, Q., Zhang, J., Kan, Y, J., Wei, B., Zhang, Y. Z. M., Wang, Z. Z., Jiao, Z., Zhang, X. X. & Li, R. (2022). Water caltrop-based carbon catalysts for cooperative adsorption and heterogeneous activation of peroxymonosulfate for tetracycline oxidation via electron transfer and non-radical pathway. Applied Surface Science, 606, 164823. DOI:10.1016/j.apsusc.2022.154823.
  49. Ye, G. R., Zhou, J. H., Huang, R. T., Ke, W. J., Peng, Y. C., Zhou, Y. X., Weng, Y., Ling, C. T. & Pan, W. X. (2022). Magnetic sludge-based biochar derived from Fenton sludge as an efficient heterogeneous Fenton catalyst for degrading Methylene blue. Journal of Environmental Chemical Engineering, 10, 107242. DOI:10.1016/j.jece.2022.107242.
  50. Yu, H., Zhang, D., Gu, L., Wen, H. & Zhu, N. (2022). Coupling sludge-based biochar and electrolysis for conditioning and dewatering of sewage sludge: Effect of char properties. Environmental Science and Ecotechnology, 2022, 214 (Pt 3), 113974. DOI:10.1016/j.envres.2022.113974.
  51. Yu, J., Tang, L., Pang, Y., Zeng, G., Wang, J., Deng, Y., Liu, Y., Feng, H., Chen, S. & Ren, X. (2019). Magnetic nitrogen-doped sludge-derived biochar catalysts for persulfate activation: Internal electron transfer mechanism. Chemical Engineering Journal, 364, 146-159. DOI:10.1016/j.cej.2019.01.163.
  52. Yu, J., Zhu, Z., Zhang, H., Shen, X., Qiu, Y., Yin, D. & Wang, S. (2020). Persistent free radicals on N-doped hydrochar for degradation of endocrine disrupting compounds. Chemical Engineering Journal, 398, 125538. DOI:10.1016/j.cej.2020.125538.
  53. Zeng, H. P., Li, J. X., Xu, J. X., Qi, W., Hao, R. X., Gao, G. W., Lin, D., Li, D. & Zhang, J. (2022). Preparation of magnetic N-doped iron sludge based biochar and itspotential for persulfate activation and tetracycline degradation. Journal of Cleaner Production, 378, 134519. DOI:10.1016/j.jclepro.2022.134519.
  54. Zhang, A., Li, X., Xing, J. & Xu, G. (2020). Adsorption of potentially toxic elements in water by modified biochar: A review. Journal of Environmental Chemical Engineering, 8 (4), 104196. DOI:10.1016/j.jece.2020.104196.
  55. Zhang, H., Xue, G., Chen, H. & Li, X. (2018). Magnetic biochar catalyst derived from biological sludge and ferric sludge using hydrothermal carbonization: Preparation, characterization and its circulation in Fenton process for dyeing wastewater treatment. Chemosphere, 191, pp. 64-71. DOI:10.1016/j.chemosphere.2017.10.026.
  56. Zhang, L., Pan, J., Liu, L., Song, K. & Wang, Q. (2019). Combined physical and chemical activation of sludge-based adsorbent enhances Cr(Ⅵ) removal from wastewater. Journal of Cleaner Production, 238,11767. DOI:10.1016/j.jclepro.2019.117904
  57. Zhang, S., Lv, J., Han, R. & Zhang, S. (2022). Superoxide radical mediates the transformation of tetrabromobisphenol A by manganese oxides. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 651, 129807. DOI:10.1016/j.colsurfa.2022.129807.
  58. Zhang, Y., Jiang, Q., Xie, W., Wang, Y. & Kang, J. (2019). Effects of temperature, time and acidity of hydrothermal carbonization on the hydrochar properties and nitrogen recovery from corn stover. Biomass and Bioenergy, 122, 175-182. DOI:10.1016/j.biombioe.2019.01.035.
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Authors and Affiliations

Ming Yi Lv
1
Hui Xin Yu
1
Xiao Yuan Shang

  1. Shenyang University of Chemical Technology, China
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Abstract

Przedmiotem dwuletnich badań było poznanie dynamiki rozwoju wybranych grup drobnoustrojów (mikroorganizmy oligotroficzne, kopiotroficznc, proteolityczne, celulolityczne, rozpuszczające fosforany) w glebie nawożonej komunalnymi osadami ściekowymi. Celem przeprowadzonego doświadczenia było wyjaśnienie możliwości zachwiania równowagi biologicznej gleby, przejawiającej się wzmożonym i długotrwałym rozwojem analizowanych grup drobnoustrojów w glebie, po wprowadzeniu do niej materii organicznej w formic osadów ściekowych, w różnych dawkach. W doświadczeniu zastosowano cztery obiekty badawcze: kontrola-gleba + NPK, 2 Mg s.m. osaduha+rok' + NPK, 4 Mg s.m. osadu-hal-rok' + NPK oraz 8 Mg s.m. osaduhatrok' + NPK). Fosfor i potas stosowano przedsiewnie pod orkę, natomiast azot: część przedsiewnie i drugą część pogłównie. Osady ściekowe stosowano przedsiewnie. Poletka glebowe, na których przeprowadzono badania obsiano żytem odmiany Wibro (2003 r.) oraz obsadzono ziemniakami odmiany Bila (2004 r.). Wykazano, że zastosowane dawki osadów ściekowych nic wpływały istotnie statystycznie na namnażanie się mikroorganizmów glebowych. Na podstawie przeprowadzonych analiz mikrobiologicznych stwierdzono, że w badanym okresie (2003-2004) liczebność oznaczonych grup drobnoustrojów ulegała wahaniom, zależnym od terminu pobierania próbek glebowych. Próbki glebowe, niezbędne do przeprowadzenie analiz, pobierane były w lenninach związanych z kolejnymi fazami rozwojowymi roślin. Kolejnym czynnikiem wpływającym na dynamikę rozwoju mikroorganizmów glebowych był gatunek rośliny użytej w doświadczeniu. Żyto uprawiane w 2003 r. stymulowało rozwój większości grup drobnoustrojów (mikroorganizmów oligotroficznych, kopiotroficznych, proteolitycznych, rozpuszczających fosforany). Z kolei ziemniaki w okresie rozwoju generatywnego ( 16.07- 28.08.2004) spowodowały silniejszy rozwój mikroorganizmów celulolitycznych.
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Authors and Affiliations

Agnieszka Wolna-Maruwka
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Abstract

This work presents results of the release of polycyclic aromatic hydrocarbons (PAH) from granules composed of fly ashes, which are the product of hard and coal combustion and sewage sludge. 3 types of granulates by a weight ratio of ash to sludge 3:7 and 1: 1 were used. The research of PAH leaching was conducted within a simulated period of 24 months, with the examination of PAH washing out every three months. The highest amounts of PAH (297 - 330 μg/kg dw.) were obtained_from granulates containing 7 parts by weights of sewage sludge (3 times higher in comparison with the granulate containing ash and sludge in ratio of I: 1 ). The maximum PAH release from all the examined granulates took place in the 9th month of the research. Benzo(k)fluoranthene revealed the highest fraction (67.4-76.0%) of all examined compounds.
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Authors and Affiliations

Czesława Rosik-Dulewska
ORCID: ORCID
Urszula Karwaczyńska
Tomasz Ciesielczuk
ORCID: ORCID
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Abstract

The main objective of presented research work was the assessment of the impact of reduced straw content, as organic carbon source, on the course of sewage sludge composting process. During the research work performed in industrial conditions, the composting process going in periodically overturned windrows differing in proportion of dehydrated sludge, straw and structural material being 4:1:1 and 8:1:2 respectively, was observed. The consequence of increase of sludge concentration with relation to straw was decrease of C:N ratio in the input material from 11.5 to 8.5. The following parameters were analyzed as indicators for the assessment of the composting process: contents of fulvic acids (FA), humic acids (HA), lignin, cellulose and hemicellulose as well as absorbance in UV/VIS (λ=280, 465 and 665 nm) range. The results obtained have indicated that the increase of sludge content extends the elevated temperature (T>50°C) period from 42 days to approximately 65 days. Our tests did not confirm that limitation of straw content added to sewage sludge had any adverse effect on the course of composting. PI index (HA/FA), which qualifies the compost as mature in the first case – No 1, exceeds limit value of 3.6 on the 83rd day whereas, in the second case No 2, on the 48th day.
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Authors and Affiliations

Robert Sidełko
1
Bartosz Walendzik
1
Małgorzata Smuga-Kogut
1
Beata Janowska
1
Kazimierz Szymański
1
Anna Głowacka
2
Aleksandra Leśniańska
1

  1. Koszalin University of Technology, Poland
  2. West Pomeranian University of Technology Szczecin, Poland
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Abstract

Washing is very popular technological operation removing clay particles from aggregates. The amount of mineral washing sludges increases. Besides filling the excavations, there is no common method of their utilization. The usage of sludges from washing aggregates in building ceramics might be environmentally friendly way to utilize them.

This paper presents laboratory research on two type of sludges: from dolomite and limestone aggregates washing. Selected properties of sludges such as water content, particle size distribution (sieve and areometric method), chemical composition (XRF), mineral composition (XRD), thermal properties (STA/EGA, dilatometry, heating microscopy) and stability of fired materials during steam exposure were determined.

It was found that dolomite sludge contains more clay minerals and less carbonates, it is more finely grained than limestone sludge. Limestone sludge has large fluctuations in water content and has high content of potentially hazardous calcite grains. During heating up to 1300°C of both dried sludges decarbonation and sintering take place. Dolomite sludge softens, melts and flows below 1300°C. After firing sludges at 1000°C material made of limestone sludge is not resistant to steam.

The obtained result suggests that dolomite sludge can be used in building ceramics technology without processing as main component of ceramic mass. Limestone sludge have to be ground before its application in building ceramic materials. Results suggest that it can not be used as the main raw material in ceramic masses, but only as an additive.

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Authors and Affiliations

Ewelina Kłosek-Wawrzyn
Anna Bugaj
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Abstract

The primary objective of the present study was to determine the seasonal dynamics of ciliates in activated sludge. Studies were carried out in order to verify the hypothesis that fertility of a habitat may significantly influence the seasonal dynamics of the abundance of ciliates, as well as the number and intensity of correlations between physic-chemical parameters and ciliates. It seems that the values of numbers of ciliates were seasonally changeable. The highest numbers of ciliates were found in spring and summer, however the lowest numbers of ciliate communities were noted in winter. The studies showed that protozoa community is determined by ammonia mainly in summer. In spring and winter additional factors may be important. Probably suspended solid, total organic carbon and concentration of appropriate food (bacteria and flagellates) are the major regulator of abundance of ciliates.
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Authors and Affiliations

Monika Tarkowska-Kukuryk
Tomasz Mieczan
Wojciech Pęczuła
Jacek Rechulicz
Wojciech Płaska
Katarzyna Radomska
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Abstract

Improving the effects of hydrolysis on waste activated sludge (WAS) prior to anaerobic digestion is of primary importance. Several technologies have been developed and partially implemented in practice. In this paper, perhaps the simplest of these methods, alkaline solubilization, has been investigated and the results of hydrolysis are presented. An increase to only pH 8 can distinctively increase the soluble chemical oxygen demand (SCOD), and produce an anaerobic condition effect favorable to volatile fatty acids (VFA) production. Further increases of pH, up to pH 10, leads to further improvements in hydrolysis effects. It is suggested that an increase to pH 9 is sufficient and feasible for technical operations, given the use of moderate anti-corrosive construction material. This recommendation is also made having taken in consideration the option of using hydrodynamic disintegration after the initial WAS hydrolysis process. This paper presents the effects of following alkaline solubilization with hydrodynamic disintegration on SCOD

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Authors and Affiliations

Jan Suschka
Eligiusz Kowalski
Jerzy Mazierski
Klaudiusz Grübel
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Abstract

In the present investigation we have studied the effects of static magnetic field on removal of organic compounds and ammonium nitrogen by high loading activated sludge. The research was carried out on laboratory scale at room temperature. Three or two continuously operating test systems were used in the experiment. In two test systems the return activated sludge was exposed to magnetic field strength of 20 mT or 40 mT. The magnets were attached to a pipe used for activated sludge recirculation. The nitrification rate for test systems when the return activated sludge was exposed to magnetic field was higher than for control system in absence of magnetic field. The best data was observed for test system which was exposed to magnetic field of 40 mT. The nitrification rate was 2 times higher than for control system when the loading of activated sludge was in the range of 0.6 to 0,9 g COD/gMLSS ·d for. The results show that magnetic field improves nitrification of domestic wastewater by high loading activated sludge.
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Authors and Affiliations

Marta Janosz-Rajczyk
Agnieszka Tomska
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Abstract

In the present investigation we studied the effects of static magnetic field on transformation of organic compounds and ammonium nitrogen. The research was carried out on laboratory scale at room temperature. Two continuously operating test systems were run in parallel. In one of the systems the raw sewage was exposed to magnetic field strength of 180 mT. The magnets were attached to a pipe used for raw sewage. The second system was used as a control. The research was carried out without activated sludge and with activated sludge. The investigation carried out in an experiment without activated sludge showed that the removal of COD for system with the raw sewage exposed to magnetic field strength of 180 mT was 15% higher then system in absence of magnetic field. During investigation carried out in an experiment with activated sludge it was observed that the removal of COD was similar in both systems. The nitrification rate for system in which raw sewage was exposed to magnetic field was lower than the system in which it was not.
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Authors and Affiliations

Marta Janosz-Rajczyk
Agnieszka Tomska
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Abstract

Primary or secondary sewage sludge in medium and large WWTP are most often processed by anaerobic digestion, as a method of conditioning, sludge quantity minimization and biogas production. With the aim to achieve the best results of sludge processing several modifications of technologies were suggested, investigated and introduced in the full technical scale. Various sludge pretreatment technologies before anaerobic treatment have been widely investigated and partially introduced. Obviously, there are always some limitations and some negative side effects. Selected aspects have been presented and discussed. The problem of nitrogen has been highlighted on the basis of the carried out investigations. The single and two step - mesophilic and thermophilic - anaerobic waste activated sludge digestion processes, preceded by preliminary hydrolysis were investigated. The aim of lab-scale experiments was pre-treatment of the sludge by means of low intensive alkaline and hydrodynamic disintegration. Depending on the pretreatment technologies and the digestion temperature large ammonia concentrations, up to 1800 mg NH4/dm3 have been measured. Return of the sludge liquor to the main sewage treatment line means additional nitrogen removal costs. Possible solutions are discussed.

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Authors and Affiliations

Jan Suschka
Klaudiusz Grübel

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