تأثیر لجن فاضلاب و بیوچارهای حاصل از آن بر قابلیت استفاده و ویژگی‌های آزادشدن مس در یک خاک آهکی آلوده

نوع مقاله : مقاله پژوهشی

نویسندگان

گروه علوم و مهندسی خاک، دانشکده کشاورزی، دانشگاه شهرکرد، شهرکرد، ایران

چکیده

هدف این پژوهش بررسی تأثیر سطوح مختلف لجن فاضلاب و همچنین بیوچار آن بر قابلیت استفاده و سینتیک آزاد­شدن مس در یک خاک آهکی آلوده به مس بود. برای این منظور لجن فاضلاب و بیوچار حاصل از آن در دو دمای تولید بیوچار شامل 400 و 600 درجه سلسیوس در سه سطح صفر، 5/0 و 1 درصد وزنی/وزنی به یک خاک آهکی آلوده به مس افزوده و به مدت 5 ماه خوابانده شدند. نمونه­های خاک به روش عصاره­گیری متوالی و با استفاده از عصاره­گیر دی ­تی ­پی آ (DTPA-TEA) در دوره­های زمانی 1 تا 504 ساعت عصاره­گیری شدند. نتایج نشان داد که تیمار لجن فاضلاب در هر دو سطح باعث افزایش معنی­دار (05/0p <) آزاد شدن مس نسبت به خاک شاهد شد، درحالی‌که مقدار مس آزادشده در تیمارهای بیوچار 400 و همچنین بیوچار 600 در هر دو سطح به طوری معنی­داری (05/0p <) نسبت به خاک شاهد کمتر بود. مقدار مس آزادشده در خاک تیمار شده با 1 درصد بیوچار 600 نسبت به خاک شاهد 2/54 درصد کاهش یافت. مقایسه ضرایب سرعت معادلات سینتیکی نشان داد که بیشترین و کمترین سرعت آزاد شدن مس به­ترتیب در تیمارهای 1 درصد لجن فاضلاب و 1 درصد بیوچار 600 بود. بطور کلی نتایج این تحقیق نشان داد که تبدیل لجن فاضلاب در یک دمای گرماکافت بهینه (در این مطالعه دمای 600 درجه سلسیوس) به بیوچار، علاوه بر اینکه راهکار مناسبی برای مدیریت لجن فاضلاب است، می­تواند در تثبیت مس و اصلاح خاک­های آلوده به مس نیز مفید باشد.

کلیدواژه‌ها

موضوعات


عنوان مقاله [English]

The Effect of Sewage Sludge and its Biochars on the Availability and Desorption Characteristics of Copper in a Contaminated Calcareous Soil

نویسندگان [English]

  • morteza shirmohammadi
  • ALI REZA HOSSEINPUR
  • Hamidreza Motaghian
Department of Soil Science, Faculty of Agriculture, Shahrekord University, Shahrekord, Iran
چکیده [English]

The aim of this study was to investigate the effect of different levels of sewage sludge and its biochars on availability and release kinetics of Cu in a contaminated calcareous soil. For this purpose, the sewage sludge and its biochars produced at two temperatures including 400 and 600 0C were added to a contaminated calcareous soil at 0, 0.5 and 1% levels (w/w), and samples were incubated for 5 months. The kinetics of Curelease was determined by successive extraction with DTPA-TEA in periods of 1 to 504 h in the amended and control soils. Results showed that the desorbed Cu from the soils treated with 0.5 and 1% sewage sludge significantly increased (p < 0.05) as compared to the control soil, whereas, the amount of Cu desorbed from soils treated with 0.5 and 1% biochar produced at 400 and 600 0C significantly decreased (p < 0.05), as compared with the control soil. Desorbed Copper from treated soil with 1% biochar produced at 600 0C was reduced 54.2% as compared to the control soil. The comparsion of release rate constants indicated that the highest and lowest desorption rate of Cu were observwd in 1% sewage sludge and 1% biochar produced at 600 0C treatments respectively. Overall, the results demonstrated that the conversion of sewage sludge to biochar is a suitable method for its management and it can be used for stabilization and remediation of Cu contaminated soils.

کلیدواژه‌ها [English]

  • DTPA-TEA
  • Release kinetics
  • Biochar
  • Pyrolysis temperatures
Agrafioti, E., Bouras, G., Kalderis, D. and Diamadopoulos, E. (2013). Biochar production by sewage sludge pyrolysis. Journal of Analytical and Applied Pyrolysis, 101, 72-78.
Abu Khatita, A.M., Koch, R. and Bamousa, O.A. (2020). Sources identification and contamination assessment of heavy metals in soil of Middle Nile Delta, Egypt. Journal of Taibah University for Science, 14, 750-761.
Ahmad, M., Rajapaksha, A.U., Lim, J.E., Zhang, M., Bolan, N., Mohan, D., Vithanage, M., Lee, S.S. and Ok, Y.S. (2014). Biochar as a sorbent for contaminant management in soil and water: a review. Chemosphere, 99, 19-33.
Aishah, R.M., Shamshuddin, J., Fauziah, C.I., Arifin, A. and Panhwar, A. (2018). Adsorption-desorption characteristics of zinc and copper in oxisol and ultisol amended with sewage sludge. Journal of the Chemical Society of Pakistan, 40, 842-855.
Alva, A.K., Baugh, T.J., Paramasive, S. and Sajwan, K.S. (2005). Adsorption/desorption of a sandy soil amendment with various rates of manure, sewage sludge, and incineratedsewage sludge. Journal of Environmental Science and Health, 4, 687-696.
Barani­ Motlagh M. (2012). Kinetics and mechanism of copper release from selected agricultural calcareous soils of northern Iran. Soil Research, 50, 312-319.
Bogusz, A., Oleszczuk, P. and Dobrowolski, R. (2017). Adsorption and desorption of heavy metals by the sewage sludge and biochar-amended soil. Environmental Geochemistry and Health, 3, 1-12.
Buss, W., Graham, M.C., Shepherd, J.G. and Mašek, O. (2016). Risks and benefits of marginal biomass-derived biochars forplant growth. Science of the Total Environment, 569, 496-506.
Cantrell, K.B., Hunt, P.G., Uchimiya, M., Novak, J.M. and Ro, K.S. (2012). Impact ofpyrolysis temperature and manure source on physicochemical characteristicsof biochar. Bioresource Technology, 107, 419-428.
Dang, Y.P., Edwards, D.G. and Tiller, K.G. (1994). Kinetics of zinc desorption from Vertisols. Soil Science Society of America Journal, 58, 1392-1399.
Demirbas, A. (2004). Effects of temperature and particle size on bio-char yield from pyrolysis of agricultural residues. Journal of Analytical and Applied Pyrolysis, 72, 243–248.
Dias, B.O., Silva, C.A., Higashikawa, F.S., Roig, A. and Sanchez-Monedero, M.A. (2010). Use of biochar as bulking agent for the composting of poultry manure; effect on organic matter degradation and humification. Bioresource Technology, 101, 1239–1246.
Gasco, G. and Lobo, M.C. 2007. Composition of a Spanish sewage sludge and effects on treated soil and olive trees. Waste Management, 27, 1494-1500.
Gee, G.H. and Bauder, J.W. (1986). Particle size analysis. PP. 383-409. In: Klute A. (ed.), Methods of Soil Analysis. Part 2. Physical Properties. Soil Science Society of American. Madison. Wisconsin. USA.
Ghasemi-Fasaei, R., Maftoun, M., Ronaghi, A., Karimian, N., Yasrebi, j., Assad, M.T. and Ippolito, J.A. (2006). Kinetics of copper desorption from highly calcareous soils. Communications in Soil Science and Plant Analysis, 37, 797-809.
Gwenzi, W., Muzava, M., Mapanda, F. and Tauro, T.P. (2016). Comparative short-term effects of sewage sludge and its biochar on soil properties, maize growth and uptake of nutrients on a tropical clay soil in Zimbabwe. Journal of Integrative Agriculture, 15, 1395-1406.
Havlin, J.L., Westfall. D.G. and Olsen. S.R. (1985). Mathematical models for potassium release kinetics in calcareous soils. Soil Science Society of America Journal, 49, 371-376.
Hossain, M.K., Strezov, V., Chan, K.Y., Ziolkowski, A. and Nelson, P.F. (2011). Influence of pyrolysis temperature on production and nutrient propertiesof wastewater sludge biochar. Journal of Environmental Management, 92, 223-228.
Hoyt, P.B. and Nyborg, M. (1971). Toxic metals in acid soil: 2. Estimation of plant available manganese. Soil Science Society of America Proceedings, 35, 141-144.
Jin, Y., Connor, D.O., Ok, Y.S., Tsang, D.C.W., Liu, A. and Hou, D. (2019). Assessment of sources of heavy metals in soil and dust at children's playgrounds in Beijing using GIS and multivariate statistical analysis. Environment International, 124, 320-328.
Kabata-Pendias, A. and Mukherjee, A.B. (2007). Trace Elements from Soil to Human. Springer-Verlag. Berlin. Germany.550p.
Kabata-Pendias, A., and Pendias, H. (1992). Trace Elements in Soils and Plants. CRC Press, Boca Raton, Florida, USA.
Karer, J., Wawra, A., Zehetner, F., Dunst, G., Wagner, M., Pavel, P.B., Puschenreiter, M., Riesl-Hanl, W. and Soja, G. (2015). Effects of biochars and compost mixtures and inorganic additives on mmobilization of heavy metals in contaminated soils. Water, Air and Soil Pollution, 226, 1–12.
Khanmohammadi, Z., Afyuni, M. and Mosaddeghi, M.R. (2015) Effect of pyrolysis temperature on chemical and physical properties of sewage sludge biochar. Waste Management & Research 33, 275-283.
Kloss, S., Zehetner, F., Buecker, J., Oburger, E., Wenzel, W.W., Enders, A., Lehmann, J. and Soja, G. (2014). Trace elementbiogeochemistry in the soil-water-plant system of a temperate agricultural soil amended with different biochars. Environmental Science and Pollution Research, 22, 4513–4526.
Koppolu, L., Agblevor, F.A. and Clements, L.D. (2003). Pyrolysis as a techniquefor separating heavy metals from hyperaccumulators. Part II: lab scalepyrolysis of synthetic hyperaccumulator biomass. Biomass Bioenergy, 25, 651-663.
Lehmann, J., Rillig, MC., Thies, J., Masiello, CA., Hockaday, WC., Crowley, D. (2011). Biochar effects on soil biota-a review. Soil Biology and Biochemistry, 43, 1812–1836.
Li, S., Fang, B., Wang, D., Wang, X., Man, X. and Zhang, X. (2019). Leaching Characteristics of Heavy Metals and Plant Nutrients in the Sewage Sludge Immobilized by Composite Phosphorus-Bearing Materials. International Journal of Environmental Research and Public Health, 16, 1-18.
Lindsay, W.L. and Norvell, W.A. (1978). Development of a DTPA soil test for zinc, iron, manganese, and copper. Soil Science Society of America Journal, 42, 421-428.
Liu, T., Liu, B. and Zhang, W. (2014).  Nutrients and heavy metals in biochar produced by sewage sludge pyrolysis: Its application in soil amendment. Polish Journal of Environmental Studies, 23, 271-275.
Loeppert, R.H. and Sparks, D.L. (1996). Carbonate and gypsum. PP. 437-474. In: Sparks D.L. (ed.), Methods of Soil Analysis. Part 3. Chemical Methods. Soil Science Society of American. Madison. Wisconsin. USA.
Luo, F. Song, J., Xia, W., Dong, M., Chen, M. and Soudek, P. (2014). Characterization of contaminants and evaluation of the suitability for land application of maize and sludge biochars. EnvironmentalScience and Pollution Research, 21, 8707-8717.
Martin, H.W. and Sparks, D.L. (1983). Kinetics of nonexchangeable potassium release from two coastal plain soils. Soil Science Society of America Journal, 47, 883-887.
Méndez, A., Gómez, A., Paz-Ferreiro, J. and Gascó, G. (2012). Effects of sewage sludge biochar on plant metal availability after application to a Mediterranean soil. Chemosphere, 89, 1354–1359.
Mendez, A., Terradillos, M. and Gasco, G. (2013). Physicochemical and agronomic properties of biochar from sewage sludge pyrolysed at different temperatures. Journal of Analytical and Applied Pyrolysis, 102, 124-130.
Motaghian, H.R. and Hosseinpur, A.R. (2012). Copperr release kinetics: effect of two extractants and (Tricum aestivum L.) rhizosherpe. Plant, Soil and Environment, 58, 471-47.
Murphy, I.C.R. and Riley, J.P. (1962) A modified single solution method for the determination of phosphate in natural waters. Analytica Chimica Acta, 27,31-143.
Nelson, D.W. and Sommers, L.E. (1996). Total carbon organic carbon and organic matter. PP. 961-1011. In: Sparks D.L. (ed.), Methods of Soil Analysis. Part 3. Chemical Methods. Soil Science Society of American. Madison. Wisconsin. USA.
Olama, V., Ronaghi, A. and Karimian, N. (2010). Copper release behavior in two calcareous soils amended with three organic materials. Communications in Soil Science and Plant Analysis, 41, 2448-2458.
Park, J.H., Choppala, G., Lee, S.J., Bolan, N., Chung, J.W. and Edraki, M. (2013). Comparative sorption of Pb and Cd by biocharsand its implication for metal immobilization in soils. Water, Air and Soil Pollution, 224, 1711–1711.
Qadeer, S., Anjum, M., Khalid, A., Waqas, M., Batool, A. and Mahmood, T. (2017). A dialogue on perspectives of biochar applications and its environmental risks. Water, Air and Soil Pollution, 228, 1-26.
Reyhanitabar, A. and Gilkes, R.J. (2010). Kinetics of DTPA extraction of zinc from calcareous soils. Geoderma, 154, 289-293.
Reyhanitabar, A. and Karimian, N. (2008). Kinetics of copper desorption of selected calcareous soils from Iran. American-Eurasian Journal Agriculture and Environment Science, 4, 287-293.
Rhoades, J.D. (1996). Salinity, electrical conductivity and total dissolved solids. PP. 417-437.In: Sparks D.L. (ed.), Methods of Soil Analysis. Part 3. Chemical Methods. Soil Science Society of American. Madison. Wisconsin. USA.
Ryan, J., Estefan, G. and Rashid, A. (2007) Soil and Plant Analysis Laboratory Manual, ICARDA.
Santos, S., Costa, C.A.E., Duarte, A.C., Scherer, H.W., Schneider, R.J. and Esteves, V.I. (2010). Influence of different organic amendments on the potential availability of metals from soil: A study on metal fractionation and extraction kinetics by EDTA. Chemosphere, 78, 389-396.
Sims, J.T. (1996) Lime requirement. PP. 491-515. In: Sparks R.L. (ed.), Methods of Soil Analysis, Part 3, Chemical Methods, SSSA Book Series No. 5. Madison, WI: Soil Science Society of America.
Singh, B., Singh, B.P. and Cowie, A.L. (2010). Characterisation and evaluation ofbiochars for their application as a soil amendment. Soil Research, 48, 516-525.
Song, X.D., Xue, X.Y., Chen, D.Z., He, P.J. and Dai, X.H. (2014). Application of biochar from sewage sludge to plant cultivation: Influence of pyrolysis temperature and biochar-to-soil ratio on yield and heavy metal accumulation. Chemosphere, 109, 213-220.
Sposito, G.L., Lund, J. and Chang, A.C. (1982). Trace metal chemistry in arid-zone field soils amended with sewage sludge: I. Fractionation of Ni, Cu, Zn, Cd, and Pb in solid phases. Soil Science Society of America Journal, 46, 260-265.
Sumner, M.E. and Miller, W.P. (1996). Cation exchange capacity and exchange coefficient. PP. 1201-1229. In: Sparks D.L. (ed.), Methods of Soil Analysis. Part 3. Chemical Methods. Soil Science Society of American. Madison. Wisconsin. USA.
Sun, Y., Gao, B., Yao, Y., Fang, J., Zhang, M., Zhao, Y., Chen, H. and Yang, L. (2014). Effect of feedstock type, production method and pyrolysis temperature on biochar and hydrobiochar properties.  Chemical Engineering Journal, 240, 574-578.
Tang, J., Zhu, W., Kookana, R. and Katayama, A. (2013). Characteristics of biochar and its application in remediation of contaminated soil. Journal of Bioscience and Bioengineering, 116, 653-659
Tang, X.Y., Zhu, Y.G., Cui, Y.S., Duan, J. and Tang, L. (2006). The effect of ageing on the bioaccessibility and fractionation of cadmium in some typical soils of China. Environment International, 32, 682-689.
Thomas, G.W. 1996. Soil pH and soil acidity. PP. 475-491. In: Sparks D.L. (ed.), Methods of Soil Analysis. Part 3. Chemical Methods.Soil Science Society of American. Madison. Wisconsin. USA.
Venegas, A., Rigol, A. and Vidal, M. (2015). Viability of organicwastes and biochars as amendments for the remediation ofheavy metal-contaminated soils. Chemosphere, 119, 190–198.
Waqas, M., Li, G., Khan, S., Shamshad, I., Reid, B.J., Qamar, Z. and Chao, C. (2015). Application of sewage sludge and sewage sludge biochar to reduce polycyclic aromatic hydrocarbons (PAH) and potentially toxic elements (PTE) accumulation in tomato. Environmental Science and Pollution Research, 22, 12114-12123.
Wuana, R.A., Yiase, S.G., Iorungwa, P.D. and Iorungwa, M.S. (2013). Evaluation of copper and lead immobilization in contaminated soil by single, sequential and kinetic leaching tests. African Journal of Environmental Science and Technology, 7, 249-258.
Yang, X., Liu, J., McGrouther, K., Hung, H., Lu, K., Gao, X., He, L., Lin, X., Che, L., Ye, Z. and Wang, H. (2016). Effect of biochar on the extractability of heavy metals (Cd, Cu, Pb, and Zn) and enzyme activity in soil. EnvironmentalScience and Pollution Research, 22, 3183-3190.
Zhang, J., Lu, F., Zhang, H., Shao, L., Chen, D. and He, P. (2015) Multiscale visualization of the structural and characteristic changes of sewage sludge biochar oriented towards potential agronomic and environmental implication. Scientific Reports 5, 1-8.
Zhao, Y., Zhao, L., Mei, Y., Li, F. and Cao, X. (2017). Release of nutrients and heavy metals from biochar-amended soil under environmentally relevant conditions. Environmental Science and Pollution Research, 25, 2517-2527.
Zhou, D., Liu, D., Gao, F., Li, M. and Luo, X. (2017). Effects of biochar-derived sewage sludge on heavy metal adsorption and immobilization in soils. International Journal of Environmental Research and Public Health, 14, 1-15.