Characteristic of heavy metal contents in agricultural wastes and agricultural risk assessment

被引:0
|
作者
Wei Y. [1 ]
Qiu S. [1 ]
Zhang J. [1 ]
Chen Q. [1 ]
Chen L. [2 ]
Tu T. [1 ]
Dai T. [1 ]
机构
[1] Institute for Quality & Safety and Standards of Agricultural Products Research, Jiangxi Academy of Agricultural Sciences, Nanchang
[2] Institute of Applied Agricultural Microorganism, Jiangxi Academy of Agricultural Sciences, Nanchang
关键词
Agricultural wastes; Heavy metal; Pollution index; Risk assessment;
D O I
10.11975/j.issn.1002-6819.2019.14.027
中图分类号
学科分类号
摘要
In order to understand the pollution status of heavy metals of main agricultural wastes in Jiangxi province and evaluate its long-time use safety of the agricultural wastes reusable products (for example, organic fertilizer), rice straw samples, paddy soil samples, vegetable waste samples, vegetable soil samples, pig manure samples and cow manure samples were collected in 9 countries of Jiangxi provinces. Eight kinds of heavy metals (Cr, Ni, Cu, Zn, As, Cd, Hg and Pb) contents in the samples were determined by ICP-MS and AFS, and then risk assessments were carried out. The results showed that the concentrations and standard exceeding rates of heavy metals in plant wastes were significantly lower than those in animal wastes, such as the levels of Cu and Zn in animal wastes were 10 to 100 times of those in plant wastes. Besides, the standard exceeding rates of Zn, Cu and As in pig manures were 86.1%, 83.3% and 13.9%, respectively, and the standard exceeding rates of Zn and Cu in pig manures were both 16.7%. Only the concentrations of Cd in rice straw samples exceed the limit standard (4.2%), and the concentrations of Cd, Zn and Ni in vegetable waste samples exceed the limit standards, the standard exceeding rates ranged from 3.6% to 7.1%. The order of heavy metal contents in plant wastes were Zn>>Cr>Ni>Cu>As, Pb, Cd>Hg, while that in animal wastes were Zn>Cu>>Ni>As, Pb, Cr>Cd>Hg. According to the Nemero composite pollution indexes, the comprehensive pollution levels in agricultural wastes of Jiangxi province were: pig manures>cow manures>vegetable wastes>rice straw, their composite pollution indexes were 3.32, 1.20, 0.34 and 0.29, respectively. Pig manures were seriously polluted, and cow manures were slightly polluted, and vegetable wastes and rice straw were at safety levels. If these agricultural wastes were served as organic fertilizer raw materials respectively, which were applied to greenhouse soil for a long-term, accumulation rates of heavy metals and their safe service lives in greenhouse soil were calculated. Accumulation rates of most heavy metals in greenhouse soil with animal manures were higher than that of plant wastes, especially of Zn and Cu. By using pig manure organic fertilizer, the levels of Cu, Cd and Zn in the greenhouse soil will be out of the limit standards after 8.4 years, 15.3 years and 23.9 years, respectively. By using cow manure organic fertilizer, the level of Cu in the greenhouse soil will exceed the limit standard after 23.3 years, the level of Cd in the greenhouse soil will exceed the limit standard after about 29 years by using vegetable wastes organic fertilizer or rice straw organic fertilizer. Obviously, the main risk factors of agricultural utilization of pig manure organic fertilizer are Cu, Cd and Zn, the risk factors of agricultural utilization of cow manure organic fertilizer is Cu, the risk factors of agricultural utilization of plant waste organic fertilizer is Cd. It should be strictly restricted the contents of heavy metals in agricultural wastes when used as raw materials of organic fertilizer. The application safety of organic fertilizers made by agricultural wastes remains long-term monitoring. © 2019, Editorial Department of the Transactions of the Chinese Society of Agricultural Engineering. All right reserved.
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页码:212 / 220
页数:8
相关论文
共 26 条
  • [1] Zuo X., A Research on the Development and Utilization of the Agricultural Residues as New Sources Energy in China, (2015)
  • [2] Du P., Han X., Gao J., Et al., Potential analysis on high efficient utilization of waste vegetable resources in China, China Vegetables, 7, pp. 15-20, (2015)
  • [3] Geng W., Hu L., Cui J., Et al., Biogas energy potential for livestock manure and gross control of animal feeding in region level of China, Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 29, 1, pp. 171-179, (2013)
  • [4] Liu X., Li S., Temporal and spatial distribution of nutrient resource from livestock and poultry feces and its returning to cropland, Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 34, 2, pp. 1-15, (2018)
  • [5] Sager M., Trace and nutrient elements in manure, dung and compost samples in Austria, Soil Biology and Biochemistry, 39, 6, pp. 1383-1390, (2007)
  • [6] Li J., Hou Y., Hua Q., Et al., Variation of soil nutrient and heavy metal concentrations in greenhouse soils, Soils, 37, 6, pp. 626-629, (2005)
  • [7] Li Y., Li W., Wu J., Et al., Contribution of additives Cu to its accumulation in pig feces: Study in Beijing and Fuxin of China, Journal of Environmental Sciences, 19, 5, pp. 610-615, (2007)
  • [8] Kornegay E.T., Hedges J.D., Martens D.C., Et al., Effect of soil and plant mineral levels following application of manures of different copper levels, Plant Soil, 45, pp. 151-162, (1976)
  • [9] Nichohon F.A., Smith S.R., Alloway B.J., Et al., An inventory of heavy metal inputs to agricultural soil in England and Wales, Science of the Total Environment, 311, pp. 205-219, (2003)
  • [10] Luo L., Ma Y.B., Zhang S., Et al., An inventory of trace element inputs to agricultural soils in China, Journnl of Environmental Management, 90, 8, pp. 2524-2530, (2009)