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沼渣施用对花生小麦轮作作物产量及土壤养分和重金属含量的影响
引用本文:秦乃群,马巧云,高敬伟,杨璞,蔡金兰,郝迎春,李艳梅,冀洪策,廖祥政.沼渣施用对花生小麦轮作作物产量及土壤养分和重金属含量的影响[J].中国农学通报,2022,38(8):58-63.
作者姓名:秦乃群  马巧云  高敬伟  杨璞  蔡金兰  郝迎春  李艳梅  冀洪策  廖祥政
作者单位:1.邓州市农业技术推广中心,河南邓州 474100;2.北京杂交小麦工程技术研究中心,北京 100097
基金项目:河南省财政厅、农业厅关于下达2016粮油绿色高产高效创建补助资金的通知(20160118)
摘    要:为研究沼渣施用对花生小麦轮作作物产量及土壤养分和重金属含量的影响,试验共设置6种施肥处理,每个处理都施750 kg/hm2复合肥为底肥,1.5×104 kg/hm2 (A1)、3.0×104 kg/hm2 (A2)、4.5×104 kg/hm2 (A3)、6.0×104 kg/hm2 (A4)、7.5×104 kg/hm2 (A5)、对照CK不施沼渣(A6),分析了不同处理作物产量、籽粒重金属含量、土壤养分和重金属含量。试验结果表明:施沼渣的花生产量比对照增产幅度为4.74%~9.03%,处理A2、A3、A4、A5的产量比对照A6增产差异显著(P<0.05),施沼渣的小麦产量比对照增产幅度为3.08%~7.38%,处理A2、A3、A4、A5的产量比对照A6增产差异显著(P<0.05),处理A2的花生和小麦产量都比对照A6的增产差异显著,且沼肥用量最低,是适宜的沼肥用量;与不施肥相比,沼肥显著增加了土壤养分含量,土壤有机质、全氮、有效磷、速效钾含量变幅分别为56.80~107.23 g/kg、0.26%~0.45%、93.77~128.67 mg/kg、218.33~329.67 mg/kg;花生籽仁和小麦籽粒中均未检测出Hg和As,Pb、Cd和Cr含量的变幅分别为0.023~0.07、0.11~0.23、0.015~0.062 mg/kg,均低于《食品安全国家标准食品中污染物限量》(GB 2762—2017)的标准;不同处理土壤Hg、Pb、Cd、Cr和As含量分别为0.046~0.061、23.4~29.7、0.09~0.22、71.1~89.5、12.0~14.4 mg/kg,远低于国家《土壤环境质量 农用地土壤污染风险管控标准(试行)》(GB 15618—2018)标准值。

关 键 词:产量  沼渣  花生小麦轮作  土壤养分  重金属  
收稿时间:2021-11-08

Effects of Biogas Residue Application on Nutrient and Heavy Metal Content in Soil and Yield of Crops Under Peanut-wheat Rotation
QIN Naiqun,MA Qiaoyun,GAO Jingwei,YANG Pu,CAI Jinlan,HAO Yingchun,LI Yanmei,JI Hongce,LIAO Xiangzheng.Effects of Biogas Residue Application on Nutrient and Heavy Metal Content in Soil and Yield of Crops Under Peanut-wheat Rotation[J].Chinese Agricultural Science Bulletin,2022,38(8):58-63.
Authors:QIN Naiqun  MA Qiaoyun  GAO Jingwei  YANG Pu  CAI Jinlan  HAO Yingchun  LI Yanmei  JI Hongce  LIAO Xiangzheng
Institution:1.Dengzhou Agricultural Technology Extension Center, Dengzhou, Henan 474100;2.Beijing Engineering Research Center for Hybrid Wheat, Beijing 100097
Abstract:To study the effects of biogas residue application on nutrient and heavy metal content in soil and yield of crops under peanut-wheat rotation, field experiments were carried out including six fertilizer treatments, i.e., 1.5×104 kg/hm2 (A1), 3.0×104 kg/hm2 (A2), 4.5×104 kg/hm2 (A3), 6.0×104 kg/hm2 (A4), 7.5×104 kg/hm2 (A5) and no biogas residue treatment (CK, A6), with the application of 750 kg/hm2 compound fertilizer as basal fertilizer in each treatment. The grain yield of crops, the heavy metal content in grains, and the soil nutrient and heavy metal content were determined respectively. The results showed that the yield of peanut using biogas residue increased by 4.74% to 9.03% compared with that of the control, the yield of A2, A3, A4 and A5 was significantly higher than that of control (A6) (P<0.05); the yield of wheat using biogas residue increased by 3.08%-7.38% compared with that of the control, the yield of A2, A3, A4 and A5 was significantly higher than that of control (A6) (P<0.05); treatment A2 had significantly higher yield of peanut and wheat compared with that of A6, and the lowest biogas residue using amount, so it was the appropriate application amount of biogas residue. Compared with no biogas residue application, the addition of biogas residue significantly increased soil nutrients’ content, the content variation range of soil organic matter, total nitrogen, available phosphorus, available potassium was 56.80-107.23 g/kg, 0.26%-0.45%, 93.77-128.67 and 218.33-329.67 mg/kg, respectively. Hg and As were not detected in peanut or wheat grains, and the content of Pb, Cd and Cr changed in the range of 0.023-0.07, 0.11-0.23 and 0.015-0.062 mg/kg, respectively, all lower than The National Food Safety Standard Maximum Levels of Contaminants in Foods (GB 2762—2017). The soil content of Hg, Pb, Cd, Cr and As was 0.046-0.061, 23.4-29.7, 0.09-0.22, 71.1-89.5 and 12.0-14.4 mg/kg, respectively, all were lower than The Soil Environmental Quality - Agricultural Land Soil Pollution Risk Control Standard (Trial) (GB 15618—2018).
Keywords:yield  biogas residue  peanut-wheat rotation  soil nutrient  heavy metal  
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