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广西典型岩溶地区农田土壤重金属生态风险阈值研究OA北大核心

Study on ecological risk threshold of farmland soil in typical karst regions of Guangxi:A case study of Cadmium

中文摘要英文摘要

镉(Cd)是一种对人体有害的非必需元素,也是农田土壤首要污染物,其在土壤-作物系统中生态风险阈值评估具有重要意义.文章系统采集了广西典型岩溶地区102组水稻作物及其根系土壤,利用Bur Ⅲ分布拟合了广西典型岩溶区农田土壤中Cd的物种敏感性分布曲线(SSD),推导出能够保护95%水稻的土壤Cd安全阈值.结果表明,研究区土壤全量Cd超标率90.2%,而水稻籽实Cd仅有8.82%样品超过《食品中污染物限量》(GB 2762-2022)的限值.利用物种敏感性分布法,推导出土壤pH在5.5~6.5、6.5~7.5和7.5~8.5下,保护95%水稻不超标的土壤Cd安全阈值分别为0.22 mg·kg-1,1.08 mg·kg-1和6.4 mg·kg-1,评价结果的推导值正确率随着pH的升高由23.5%显著提高到92.1%.研究结果可以被认为是更准确的评估阈值,为广西典型岩溶地区Cd污染稻田安全生产提供科学的参考依据.

Cadmium(Cd)is a non-essential element harmful to human health and is a primary pollutant in agricultural soils.It is important to assess the ecological risk threshold of Cd in soil-crop systems.Previous studies have demonstrated that soils in the karst regions of Southwest China are anomalously enriched in Cd due to geogenic processes.Therefore,it is imperative to propose an effective method for accurately evaluating ecological risk threshold of Cd in agricultural soils within karst regions.Rice is the most widely cultivated cereal crop in Daxin County and is also the crop with the highest Cd exposure in the human diet.In this study,102 sets of rice crops and their rhizosphere soils were systematically collected from typical karst regions in Guangxi Province.With the use of the Bur Ⅲdistribution,the species sensitivity distribution(SSD)curves for Cd in agricultural soils of typical karst regions in Guangxi were fitted,and a soil Cd safety threshold was established to protect 95% of rice crops. The results show that 90.2% of Cd in soil samples exceeded the screening value established by The National Environmental Quality Standard for Soil(GB 15618-2018).However,the Cd content in rice grains cultivated in those fields was quite low,and only 8.82% of the samples surpassing the Limit of Contaminants in Food(GB 2762-2022).This suggests a spatial mismatch in the Cd levels between the soil and the rice grains.Specifically,there are three primary scenarios:(ⅰ)the soil exceeds the Cd limit,but the rice remains safe;(ⅱ)both the soil and the rice exceed the Cd limit;and(ⅲ)the soil is within safe Cd levels,yet the rice exceeds the limit.In the study area,higher soil pH values correspond to reduced mobility of Cd,resulting in lower absorption and transfer of Cd by rice grains.Although the soil Cd form is mainly dominated by the content of bioavailable state,the soil pH is mainly weakly alkaline,which inhibits the absorption of soil Cd by plants.Under conditions where soil pH remains unchanged,changes in the soil will not pose a threat to food safety.This is one of the key reasons for the low Cd concentration in rice grown in high Cd soil.The existing standards of soil environmental quality are insufficient for the accurate evaluation of the level of Cd pollution in the soil of the study area.Given this,it is essential to establish the benchmark of soil environmental quality that can reflect the actual conditions.Therefore,using SSD,this study calculated the safety threshold for soil Cd to protect 95% of rice grains and evaluated the actual Cd pollution level in the study area.Based on SSD,the derived soil Cd safety thresholds for protecting 95% of rice grains under soil pH conditions of 5.5-6.5,6.5-7.5 and 7.5-8.5 are 0.22 mg·kg-1,1.08 mg·kg-1,and 6.4 mg·kg-1,respectively.Compared with the limits of soil environmental quality stipulated by GB15618-2018,it is evident that the national standard is overly lenient for acidic soil(5.5<pH 6.5)but overly stringent for neutral(6.5<pH<7.5)and alkaline(pH>7.5)soils.The derived value accuracy of evaluation results significantly increased from 23.5% to 92.1% with increasing pH values.In contrast,the screening value accuracy specified by national standards dropped from 47.1%to 6.3%.Therefore,the research results can be considered as more accurate evaluation thresholds,providing a scientific reference for safe production in Cd-contaminated rice paddies in typical karst regions of Guangxi.

黄春阳;黄娟;钟晓宇;李杰;李明钰

广西地质调查院,广西南宁 530023广西地质调查院,广西南宁 530023广西地质调查院,广西南宁 530023广西地质调查院,广西南宁 530023广西地质调查院,广西南宁 530023

环境科学

岩溶地区土壤重金属生态风险阈值Cd

karst regionsoilheavy metalecological risk thresholdCadmium

《中国岩溶》 2025 (1)

79-88,10

全国土壤现状调查及污染防治国家专项(GZTR20060115,GZTR20070107,GZTR20080110)关于广西土地质量地球化学学评价2013年度工作方案的批复(桂国土资函[2013]1728号)关于下达2014年度广西土地质量地球化学评价项目任务书的函(桂国土资函[2014]877号广西科技基地和人才专项广西地矿局院士工作站(桂科AD17129052)广西自然科学基金项目(2016GXNSFBA380106)2018年度广西土地质量地球化学评价(桂国土资函[2018]69号)广西关键矿产资源深部勘查人才小高地(桂组通字[2019]85号)

10.11932/karst2024y032

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