Fractionation of Cd and Zn in Cd-contaminated soils amended by sugarcane waste products from an ethanol production plant |
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Authors: | Pensiri Akkajit Thomas DeSutter Chantra Tongcumpou |
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Affiliation: | 1. Center of Excellence on Hazardous Substance Management (HSM), Chulalongkorn University, Phathumwan, Bangkok, 10330, Thailand 2. International Postgraduate Programs in Environmental Management, Chulalongkorn University, Phathumwan, Bangkok, 10330, Thailand 3. Department of Soil Science, North Dakota State University, 214 Walster Hall, P.O. Box 7680, Fargo, ND, 58108-6050, USA 4. Environmental Research Institute, Chulalongkorn University, Phathumwan, Bangkok, 10330, Thailand
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Abstract: | Purpose Sugarcane waste products (boiler ash, filter cake, and vinasse) from an ethanol production plant were used as soil amendments by adding 3 % (w/w) in single and/or in combination, with a research focus towards stabilization of cadmium (Cd) and zinc (Zn) in contaminated soils. The objective of this laboratory study was to evaluate the effects of adding these sugarcane waste products on bioavailability of Cd and Zn over time (aging) in Cd- and Zn-contaminated agricultural soils of Thailand. Materials and methods Two agricultural contaminated soils of low (<3 mg kg?1) and high (10–15 mg kg?1) Cd concentrations were collected from Tak Province, Northwest Thailand. Fourteen treatments were sampled at 2-week intervals for 84 days for metal bioavailability using BCR extraction procedures (proposed by The Standards, Measurements and Testing Programme of the European Union, SM&T) that determined exchangeable (BCR1), reducible (BCR2), oxidizable (BCR3), and residual (BCR4) fractions, and total concentration was determined using aqua regia digestion and microwave digestion. Results and discussion Cd was potentially bioavailable, predominantly in exchangeable (BCR1) and reducible (BCR2) fractions, while the higher contribution of Zn was more prevalent in refractory fractions (BCR2 and BCR4). Aging had an influence on fractionation of Cd and Zn, most notably in the first two fractions (BCR1 and BCR2) of BCR sequential extraction, which resulted in reduction of exchangeable Cd during the first few weeks of incubation (T?=?0 to 28 days). At the end of pot experiment, the exchangeable Cd fraction in the low Cd (LCdS) soil was reduced from 2.3 to 4.7 % and 9.4 to 39.9 % in low and high Cd (HCdS)-contaminated soils, respectively, as compared to nonamended soils. Conclusions The observed reduction in exchangeable Cd (BCR1) in the amended soils at the 3 % (w/w) application rate, the low total metal concentrations, and the significant amount of essential plant nutrients (N, P, and K) within these waste products highlight the benefits of amending metal-rich soils with them. |
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