文章摘要
周雪萍,简桂宏,程细江,梁作恒,李海辉,杨光菲,王进进.珠三角典型重金属污染农田土壤调理剂筛选田间试验研究[J].农业环境科学学报,2024,43(9):1969-1978.
珠三角典型重金属污染农田土壤调理剂筛选田间试验研究
Field screening experiments of soil conditioners for typical heavy metal-polluted farmland in Pearl River Delta
投稿时间:2023-10-23  
DOI:10.11654/jaes.2023-0871
中文关键词: 土壤调理剂  农田土壤  重金属  水稻
英文关键词: soil conditioners  farmland soil  heavy metal  rice
基金项目:国家重点研发计划课题(2023YFD1700103);中山市社会公益与基础研究项目(200826113620079)
作者单位E-mail
周雪萍 广东省中山市南朗街道农业服务中心, 广东 中山 528451  
简桂宏 广东省中山市南朗街道农业服务中心, 广东 中山 528451  
程细江 广东省中山市南朗街道农业服务中心, 广东 中山 528451  
梁作恒 广东省中山市南朗街道农业服务中心, 广东 中山 528451  
李海辉 华南农业大学资源环境学院, 广州 510642  
杨光菲 华南农业大学资源环境学院, 广州 510642  
王进进 华南农业大学资源环境学院, 广州 510642 wangjinjin@scau.edu.cn 
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中文摘要:
      为探究不同土壤调理剂对农田土壤和稻米中重金属含量的影响,筛选适宜的耕地污染修复治理方法,实现精准选用调理剂进行安全生产的目的,本试验分析了市售6种土壤调理剂在4种不同早晚造用量条件下对土壤pH值、土壤重金属总量、土壤有效态Cd含量、稻米重金属含量和稻米产量的影响。结果表明:施用6种调理剂均可提高土壤pH值,6种调理剂对土壤pH值的提升效果排序为金葵子>粤田>营养阻控剂>天象>铁基生物炭>铁改性木本泥炭,pH增幅为3.2%~24.3%。施用6种土壤调理剂不会额外增加土壤中各重金属总量,且均能降低土壤中有效态Cd含量,降低有效态Cd效果排序为粤田(3、2、1、4)>铁基生物炭(3)>天象(2、4、3)>营养阻控剂(1、3)>金葵子(1),降幅达25.0%~58.3%。6种土壤调理剂均能降低早造稻米中Cd含量,降Cd效果排序为天象(2)>天象(1)>天象(3)>铁改性木本泥炭(1)>铁改性木本泥炭(2)>天象(4)>铁基生物炭(4)>粤田(1),降幅为47.8%~67.5%,降低后稻米中Cd含量均低于《食品安全国家标准》(GB 2762—2022)中糙米Cd限量标准0.2 mg·kg-1。施用6种土壤调理剂对水稻产量无显著影响,产量均未低于对照组的90%,满足安全生产要求。针对珠三角典型重金属污染农田,推荐按天象(2)的方式进行处理,即早造每公顷施加2 250 kg天象调理剂、晚造每公顷施加2 250 kg天象调理剂,该方式可显著提高稻田土壤pH值、降低稻田土壤中有效态Cd含量、降低稻米中Cd含量,且不影响稻米产量。
英文摘要:
      To investigate the effects of different soil conditioners on the heavy metal content of soil and rice, screen suitable remediation methods for contaminated farmland, and realize the precise selection of conditioners for safe production, the effects of six commercially available soil conditioners on soil pH, heavy metal content in soil and rice, effective-state Cd content of soil, and rice yield were analyzed under four different early-maturing and late-maturing rice dosage conditions. The results showed that all of the conditioners increased soil pH, and this pH enhancement effect was in the order Jinkuizi > Yuetian > nutrient blockers > Tianxiang > iron-modified biochar > ironmodified woody peat, with the increase ranging from 3.2% to 24.3%. None of the conditioners additionally increased the total amount of each heavy metal in soil samples, and all of them reduced the effective-state Cd content of soil after application, and the order of effectivestate Cd reduction was as follows:Yuetian(3, 2, 1, 4)> iron-modified biochar(3)>Tianxiang(2, 4, 3)> nutrient blockers(1, 3)> Jinkuizi (1), with a reduction of 25.0%-58.3%. All the six conditioners reduced the Cd content in the early-maturing rice, and the Cd reduction effect was in the order Tianxiang(2)>Tianxiang(1)>Tianxiang(3)>iron-modified woody peat(1)>iron-modified woody peat(2)>Tianxiang (4)>iron-modified biochar(4)>Yuetian(1), with a reduction range of 47.8%-67.5%, and the Cd content in the reduced rice was in accord with the relevant standards. There were no significant effects on rice yields after the application of the six soil conditioners, and none of the experimental groups with reduced yields decreased by<90% that of the control group, which satisfied the relevant requirements. For typical heavy metal contaminated farmland in the Pearl River Delta, it is recommended that treatment be carried out according to the method of Tianxiang(2), i.e., applying 2 250 kg of Tianxiang conditioner per hectare during early planting and 2 250 kg of Tianxiang conditioner per hectare during late planting, which can significantly elevate the pH of paddy field soils, reduce the effective Cd content of such soils, and reduce the Cd content of paddy rice without affecting yield.
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