Zheng Xiaochen, Zou Dongsheng, Wu Qingdan, Wang Hua, Li Shuhui, Liu Fen, Xiao Zhihua
College of Resources and Environment, Hunan Agricultural University, Changsha, Hunan 410128, PR China; Key Laboratory for Rural Ecosystem Health in Dongting Lake Area of Hunan Province, Changsha 410128, PR China.
College of Resources and Environment, Hunan Agricultural University, Changsha, Hunan 410128, PR China; Key Laboratory for Rural Ecosystem Health in Dongting Lake Area of Hunan Province, Changsha 410128, PR China.
Waste Manag. 2022 Aug 1;150:75-89. doi: 10.1016/j.wasman.2022.06.033. Epub 2022 Jul 6.
Anaerobic digestion and composting are attracting increasing attention due to the increased production of animal manure. It is essential to know about the fate and bioavailability of heavy metals (HMs) for further utilisation of animal manure. This review has systematically summarised the migration of HMs and the transformation of several typical HMs (Cu, Zn, Cd, As, and Pb) during anaerobic digestion and composting. The results showed that organic matter degradation increased the HMs content in biogas residue and compost (with the exception of As in compost). HMs migrated into biogas residue during anaerobic digestion through various mechanisms. Most of HMs in biogas residue and compost exceeded relevant standards. Then, anaerobic digestion increased the bioavailable fractions proportion in Zn and Cd, decreased the F4 proportion, and raised them more than moderate environmental risks. As (III) was the main species in the digester, which extremely increased As toxicity. The increase of F3 proportion in Cu and Pb was due to sulphide formation in biogas residue. Whereas, the high humus content in compost greatly increased the F3 proportion in Cu. The F1 proportion in Zn decreased, but the plant availability of Zn in compost did not reduce significantly. Cd and As mainly converted the bioavailable fractions into stable fractions during composting, but As (V) toxicity needs to be concerned. Moreover, additives are only suitable for animal manure treated with slightly HM contaminated. Therefore, it is necessary to combine more comprehensive methods to improve the manure treatment and make product utilisation safer.
由于动物粪便产量增加,厌氧消化和堆肥正受到越来越多的关注。了解重金属(HMs)的归宿和生物有效性对于动物粪便的进一步利用至关重要。本综述系统总结了厌氧消化和堆肥过程中重金属的迁移以及几种典型重金属(铜、锌、镉、砷和铅)的转化。结果表明,有机物降解增加了沼渣和堆肥中的重金属含量(堆肥中的砷除外)。厌氧消化过程中,重金属通过各种机制迁移到沼渣中。沼渣和堆肥中的大多数重金属超过了相关标准。然后,厌氧消化增加了锌和镉中生物可利用部分的比例,降低了F4比例,并使其环境风险增加到中度以上。三价砷是消化器中的主要形态,极大地增加了砷的毒性。铜和铅中F3比例的增加是由于沼渣中形成了硫化物。而堆肥中高腐殖质含量大大增加了铜中F3比例。锌中F1比例降低,但堆肥中锌对植物的有效性没有显著降低。镉和砷在堆肥过程中主要将生物可利用部分转化为稳定部分,但需要关注五价砷的毒性。此外,添加剂仅适用于轻度受重金属污染的动物粪便处理。因此,有必要结合更全面的方法来改善粪便处理,使产品利用更安全。