Valorisation of sewage sludge humic compounds in the aspect of its application in natural environment

• Autorzy: Jakubus Monika , Bakinowska Ewa , Tobiašová Erika

Identyfikatory

DOI

10.37190/epe210106

• Języki publikacji: EN

Abstrakty

EN

The valorization of sewage sludge (SS) has been presented originating from four wastewaters treated in wastewater treatment plants (WWTPs) located in the Wielkopolska province. In the SS samples collected in two successive years, the quantity and quality of humic substances (HSs), fulvic and humic acids (FAs, HAs), amounts of organic carbon (TOC), organic matter (OM), labile carbon (CL), and water extracted organic carbon (WEOC) were determined. It was investigated how the defined parameters depend on the size of the installation and select those which in a routine SS analysis facilitate rapid assessment of their quality and suitability for application in the natural environment. Regardless of WWTP size and the year of analysis, SS was characterized by a significant share of easily decomposable compounds such as FAs and WEOC. The statistical analysis showed significant usefulness of CL, FAs, and HAs in the evaluation of SS quality and usability.

Słowa kluczowe

EN

sewage sludge valorisation; humic; TOC; total organic carbon

PL

waloryzacja osadów ściekowych; humus; węgiel organiczny

• Wydawca: Oficyna Wydawnicza Politechniki Wrocławskiej
• Czasopismo: Environment Protection Engineering
• Rocznik: 2021
• Tom: Vol. 47, nr 1
• Strony: 67--83
• Opis fizyczny: Bibliogr. 27 poz., rys., tab.

Twórcy

autor

Jakubus Monika

• Department of Soil Science and Land Protection, Poznan University of Life Sciences, Poland

autor

Bakinowska Ewa

• Institute of Mathematics, Poznan University of Technology, Poznan, Poland

autor

Tobiašová Erika

• Department of Soil Science, Slovak University of Agriculture in Nitra, Slovak Republic

Bibliografia

• [1] Eurostat 2018, https://ec.europa.eu/eurostat/web/waste/data/database (accessed May 2020).
• [2] Journal of Laws 2013, item 38, Ordinance of the Economy and Labor Minister on criteria and procedures for admission of waste to storage in a type of waste.
• [3] SHARMA B., SARKAR A., SINGH P., SINGH R.P., Agricultural utilisation of biosolids. A review on potential effects on soil and plant grown, Waste. Manage., 2017, 64, 117–132.
• [4] Central Statistical Office. Environment Protection, Warszawa 2019, https://stat.gov.pl/obszary-tematyczne/srodowisko-energia/srodowisko/ochrona-srodowiska-2019,1,20.html (accessed 2 May 2020)
• [5] Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste https://eur-lex.europa.eu/legalcontent/EN/TXT/PDF/?uri=CELEX:31999L0031&from=EN (accessed 2 May 2020).
• [6] Report from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions. The Implementation of the Soil Thematic Strategy and ongoing activities, COM (2012) 46 final, https://eur-lex.europa.eu/legal-content/EN/TXT/PDF /?uri=CELEX: 52012DC0046&from=EN (accessed 2 May 2020).
• [7] JAKUBUS M., Sewage sludge. Origin and management, Poznan University of Life Sciences, Poznań 2012, 56 (in Polish).
• [8] BÖRJESSON G., KÄTTERER T., Soil fertility effects of repeated application of sewage sludge in two 30-year-old field experiment, Nutr. Cycl. Agroecosyst., 2018, 112, 369–385.
• [9] GÓRECKI T., JAKUBUS M., KRZYŚKO M., WOŁYŃSKI W., Application of distance covariance in selection of nutrients during dynamic process of sewage sludge conditioning with bio‑preparation, Waste Biom. Valor., 2020, 11 (8), 4157–4166.
• [10] YU H., XIE B., KHAN R., SHEN G., The changes in carbon, nitrogen components and humic substances during organic-inorganic aerobic co-composting, Biores. Technol., 2019, 271, 228–235.
• [11] LV B., XING M., YANG J., QI W., LU Y., Chemical and spectroscopic characterisation of water extractable organic matter during vermicomposting of cattle dung, Bioresour. Technol., 2013, 132, 320–326.
• [12] ADANI F., TAMBONE F., Long-term effect of sewage sludge application on soil humic acids, Chemosphere, 2005, 60, 1214–1221.
• [13] LI H., LI Y., LI C., Characterisation of humic acids and fulvic acids derived from sewage sludge, Asian J. Chem., 2013, 25 (18), 10087–10091.
• [14] LI S., LI D., LI J., LI G., ZHANG B., Evaluation of humic substances during co-composting of sewage sludge and corn stalk under different aeration rates, Biores. Technol., 2017, 245, 1299–1302.
• [15] ANIELAK A.M., KRYŁÓW M., ŁOMIŃSKA-PLATEK D., Characterization of fulvic acids contained in municipal sewage purified with activated sludge, Arch. Environ. Prot., 2018, 44 (1), 70–76.
• [16] ORLOV D.S., GRIŠINA L.A., Guide of humus chemistry, IMU, Moskva 1981 (in Russian).
• [17] LOGINOV W., WISNIEWSKI W., GONET S.S., CIESCINSKA B., Fractionation of organic carbon based on susceptibility to oxidation, Pol. J. Soil Sci., 1987, 20, 47–52.
• [18] GHANI A., DEXTER M., PERROTT K.W., Hot-water extractable carbon in soils. A sensitive measurement for determining impacts of fertilisation, grazing and cultivation, Soil. Biol., 2003, 35, 1231–1245.
• [19] DZIADOWIEC H., GONET S., A methodological guide to soil organic matter research, Polskie Towarzystwo Gleboznawcze, 1999, 120, 31–33 (in Polish).
• [20] JAKUBUS M., Selected issues of soil science and agricultural chemistry, Poznan University of Life Sciences, Poznań, 2013, 156 (in Polish).
• [21] Journal of Laws of 2015, item 257, Ordinance of Ministry of Environment on sewage sludge.
• [22] BUGAJSKI P., CHMIELOWSKI K., CUPAK A., WĄSIK E., Influence of sewage sludge from septic tanks on the variability concentration of pollutants in sewage sludge undergoing purification processes, Infr. Ecol. Rural Areas, 2016, 2 (2), 517–523 (in Polish).
• [23] CORVASCE M., ZSOLNAY A., D’ORAZIO V., LOPEZ R., MIANO T.M., Characterization of water-extractable organic matter in a deep soil profile, Chemosphere, 2006, 62 (10), 1583–1590.
• [24] BU X., WANG L., MA W., YU X., MCDOWELL W.H., RUAN H., Spectroscopic characterization of hotwater extractable organic matter from soils under different vegetation types along an elevation gradient in the Wuyi mountains, Geoderma, 2010, 159, 139–146.
• [25] KALISZ B., ŁACHACZ A., GŁAŻEWSKI R., GRABOWSKI K., Labile organic carbon fractions after amendment of sandy soil with municipal sewage sludge and compost, J. Elem., 2017, 22 (3), 785–791.
• [26] FILIP Z., PECHER W., BERTHELIN J., Microbial utilisation and transformation of humic acid-like substances extracted from a mixture of municipal refuse and sewage sludge disposed of in a landfill, Environ. Pollut., 2000, 109, 83–89.
• [27] IAKIMIENKO O.S., VELICHENKO S.V., Sewage sludge organic matter transformation in soil in incubation experiment, [In:] J. Drozd, S.S. Gonet, N. Senesi, J. Weber (Eds.), The role of humic susbtances in the ecosystems and in environmental protection, IHSS – Polish Society of Humic Substances, Wrocław 1997, 605–612.

Uwagi

Opracowanie rekordu ze środków MNiSW, umowa Nr 461252 w ramach programu "Społeczna odpowiedzialność nauki" - moduł: Popularyzacja nauki i promocja sportu (2021).