Beijing Key Laboratory of Biodiversity and Organic Farming, College of Resources and Environmental Science, China Agricultural University, Beijing, 100193, China.
Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing, 100081, People's Republic of China.
Environ Pollut. 2020 Aug;263(Pt A):114552. doi: 10.1016/j.envpol.2020.114552. Epub 2020 Apr 10.
Heavy metal contamination in protected-field vegetable production has aroused widespread concern and manure is considered to be one of the contamination sources. Little is known about its long-term effects on heavy metal pollution in uncontaminated soils. A 15-year protected-field vegetable production experiment was carried out with three manure treatments (chicken manure: cattle manure = 3:1) with high (HMAR), medium (MMAR) and low (LMAR) application rates to evaluate the long-term risks of heavy metal pollution. It was found that continuous and high manure application rates significantly increased the total concentrations of soil Cd, Zn, Cr, and Cu rather than Pb, Ni or As. The high application rate of manure also increased soil available heavy metals although the soil organic matter was increased as well. Though total soil Cd under the HMAR exceeded the threshold of national soil standard, Cd content in tomato and fennel still complied with the food safety requirements of vegetables. Generally, the accumulation rates of soil Zn, Cu, and Cr with 1 t⋅ha of manure application in three treatments were ranked by HMAR < MMAR < LMAR. Based on the results of the ratio of heavy metal accumulation risk (RAR), Zn, Cu, and Cr under HMAR and Cd and Zn under MMAR would exceed their soil threshold values within 100 years and RAR could be a useful indicator for monitoring the long-term risk of soil heavy metal pollution. Recommended manure application rates to guarantee a 100-year period of clean production were 44, 74, and 63 t⋅ha⋅yr for Zn, Cu, and Cr, respectively. Measurements should be taken to minimize the risk of heavy metals (Cd, Zn, Cr, and Cu) pollution sourced from manure to ensure food safety and 'cleaner' protected-field vegetable production.
重金属污染在保护地蔬菜生产中引起了广泛关注,而粪肥被认为是污染的来源之一。然而,对于未污染土壤中重金属污染的长期影响,人们知之甚少。本研究开展了一项为期 15 年的保护地蔬菜生产试验,采用鸡粪:牛粪=3:1 的三种粪肥处理(高(HMAR)、中(MMAR)和低(LMAR)施肥率),评估重金属污染的长期风险。结果表明,连续高粪肥施用量显著增加了土壤 Cd、Zn、Cr 和 Cu 的总量,而不是 Pb、Ni 或 As。高粪肥施用量还增加了土壤有效态重金属,尽管土壤有机质也增加了。尽管 HMAR 下的土壤总 Cd 含量超过了国家土壤标准的阈值,但番茄和茴香中的 Cd 含量仍符合蔬菜的食品安全要求。一般来说,三种处理中每公顷施用 1 吨粪肥时,土壤 Zn、Cu 和 Cr 的积累率按 HMAR<MMAR<LMAR 排序。基于重金属积累风险比(RAR)的结果,HMAR 下的 Zn、Cu 和 Cr 以及 MMAR 下的 Cd 和 Zn 在 100 年内可能会超过其土壤阈值,RAR 可以作为监测土壤重金属污染长期风险的有用指标。为了保证 100 年的清洁生产,推荐的粪肥施用量分别为 Zn、Cu 和 Cr 44、74 和 63 t·ha·yr。应采取措施最大限度地减少粪肥来源重金属(Cd、Zn、Cr 和 Cu)污染的风险,以确保食品安全和“清洁”的保护地蔬菜生产。