The effects of soil liming and sewage sludge application on dynamics of copper fractions and total copper concentration

被引:5
作者
Malinowska, Elzbieta [1 ]
机构
[1] Siedlce Univ Nat Sci & Humanities, Dept Grassland & Landscape Architecture, B Prusa 14 St, PL-08110 Siedlce, Poland
关键词
Copper mobility; Sewage sludge; Liming; Soil; Zeien and Brummer method; HEAVY-METALS; TRACE-ELEMENTS; SPECIATION; SEDIMENTS; MUNICIPAL; PLANTS; CHINA; FORMS; ZN; CD;
D O I
10.1007/s10661-016-5609-4
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The paper deals with effects of liming and different doses of municipal sewage sludge ( 5, 10, and 15 % of soil mass) on copper speciation in soil. In all samples, pH was determined together with total copper concentration, which was measured with the ICP-AES method. Concentration of copper chemical fractions was determined using the seven-step procedure of Zeien and Brummer. In the soil treated with the highest dose of sludge ( 15 %), there was, compared to the control, a twofold increase in the concentration of copper and a threefold increase in the concentration of nitrogen. Copper speciation analysis showed that in the municipal sewage sludge the easily soluble and exchangeable fractions ( F1 and F2) constituted only a small share of copper with the highest amount of this metal in the organic ( F4) and residual ( F7) fractions. In the soil, at the beginning of the experiment, the highest share was in the organic fraction ( F4), the residual fraction ( F7) but also in the fraction where copper is bound to amorphous iron oxides ( F5). After 420 days, at the end of the experiment, the highest amount of copper was mainly in the organic fraction ( F4) and in the fraction with amorphous iron oxides ( F5). Due to mineralization of organic matter in the sewage sludge, copper was released into the soil with the share of the residual fraction ( F7) decreasing. In this fraction, there was much more copper in limed soil than in non-limed soil.
引用
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页数:9
相关论文
共 35 条
[1]   Heavy metal extractable forms in sludge from wastewater treatment plants [J].
Alvarez, EA ;
Mochón, MC ;
Sánchez, JCJ ;
Rodríguez, MT .
CHEMOSPHERE, 2002, 47 (07) :765-775
[2]   ASSESSMENT OF HEAVY-METAL EQUILIBRIA IN SEWAGE SLUDGE-TREATED SOIL [J].
BEHEL, D ;
NELSON, DW ;
SOMMERS, LE .
JOURNAL OF ENVIRONMENTAL QUALITY, 1983, 12 (02) :181-186
[3]   Total concentrations and speciation of heavy metals in municipal sludge from Changsha, Zhuzhou and Xiangtan in middle-south region of China [J].
Chen, Ming ;
Li, Xiao-ming ;
Yang, Qi ;
Zeng, Guang-ming ;
Zhang, Ying ;
Liao, De-xiang ;
Liu, Jing-jin ;
Hu, Jing-mei ;
Guo, Liang .
JOURNAL OF HAZARDOUS MATERIALS, 2008, 160 (2-3) :324-329
[4]  
Dabrowska L, 2011, ENV NATURAL RESOURCE, V49, P354
[5]  
GAMBUS F, 1998, ACTA AGR SILV A, V36, P9
[6]  
Gawdzik J., 2012, P ECOPOLE, V6, P319, DOI [10.2429/proc.2012.6(1)044, DOI 10.2429/PROC.2012.6(1)044]
[7]   Fractionation studies of trace elements in contaminated soils and sediments: a review of sequential extraction procedures [J].
Gleyzes, C ;
Tellier, S ;
Astruc, M .
TRAC-TRENDS IN ANALYTICAL CHEMISTRY, 2002, 21 (6-7) :451-467
[8]  
Gondek K, 2003, J ECOLOGICAL ENG, V9, P112
[9]  
Gondek K., 2006, ACTA AGROPHYS, V8, P825
[10]   Determination of trace elements bound to soils and sediment fractions - (IUPAC technical report) [J].
Hlavay, J ;
Prohaska, T ;
Weisz, M ;
Wenzel, WW ;
Stingeder, GJ .
PURE AND APPLIED CHEMISTRY, 2004, 76 (02) :415-442