Effects of different passivation treatments and foliar blocking agents on remediation of Cd-contaminated rice fields

doi:10.14088/j.cnki.issn0439-8114.2023.03.021

Abstract

Abstract: Field experiments were carried out in the Cd polluted area of Zhichanghe Town of Songzi City, Jingzhou City, Hubei Province, and analyze the effects of different passivation treatments and foliar blocking agents on soil pH, available Cd and Cd content in brown rice were analyzed. The results showed that different treatments could increase soil pH （0.16%~6.06%） to some extent and decrease the content of available Cd in soil. Compared with the control, the content of available Cd in soil decreased by 3.57%~33.33%. Foliar blocking agents had no significant effect on soil pH and available Cd content, but could effectively inhibit Cd transport in rice and reduce Cd content in brown rice. Soil conditioner and heavy metal passivator could regulate soil pH properly and reduce the content of available Cd in soil, and then reduce the absorption of Cd by rice. 3 750 mL/hm² foliar blocking agents +1 200 kg/hm² soil conditioner +1 200 kg/hm² heavy metal passivator had the best treatment effect. The Cd content in brown rice was the lowest, and the Cd content in soil and brown rice decreased by 33.33% and 44.95%, respectively.

Key words: soil, heavy metal passivator, Cd-contaminated rice fields, conditioners, foliar blocking agents

CLC Number:

WANG Jin-wen, GU Zhu-yu, PI Jie, TANG Dong-hai, ZHOU Zhi-yuan, ZHANG Jian-yun. Effects of different passivation treatments and foliar blocking agents on remediation of Cd-contaminated rice fields[J]. HUBEI AGRICULTURAL SCIENCES, 2023, 62(3): 130-134.

References

[1] 谢华,刘晓海,陈同斌,等.大型古老锡矿影响区土壤和蔬菜重金属含量及其健康风险[J].环境科学,2008,29(12):3503-3507.
[2] 王蕊,陈明,陈楠,等.基于总量及形态的土壤重金属生态风险评价对比: 以龙岩市适中镇为例[J].环境科学,2017,38(10):4348-4359.
[3] 史海娃,宋卫国,赵志辉.我国农业土壤污染现状及其成因[J].上海农业学报,2008,24(2):122-126.
[4] 顾祝禹,艾克拜尔·伊拉洪,吐尔逊·吐尔洪.电化学方法去除污泥中重金属的研究[J].环境科学学报,2014,34(10):2547-2551.
[5] 曹勤英,黄志宏.污染土壤重金属形态分析及其影响因素研究进展[J].生态科学,2017,36(6):222-232.
[6] 邢洪连,郭华明,王轶,等.河北保定市安新——清苑县土壤重金属形态分布及风险评估[J].水文地质工程地质,2016,43(2):140-146.
[7] 张朝升,陈秋丽,张可方,等.大坦沙污水厂污泥重金属形态及其生物有效性的研究[J].农业环境科学学报,2008,27(3):1259-1264.
[8] 铁梅,宋琳琳,惠秀娟,等.施污土壤重金属有效态分布及生物有效性[J].生态学报,2013,33(7):2173-2181.
[9] 谢志宜,张雅静,陈丹青,等.土壤重金属污染评价方法研究——以广州市为例[J].农业环境科学学报,2016,35(7):1329-1337.
[10] 陈江军,刘波,李智民,等.江汉平原典型场区土壤重金属赋存形态及其影响因素探讨[J].资源环境与工程,2018,32(4):551-556.
[11] 顾祝禹,古丽戈娜·阿布都热西体,艾克拜尔·伊拉洪,等.河东污水处理厂污泥中Cd和Pb形态分析[J].环境工程,2013(31):58-63.
[12] 张海珍,唐宇力,陆骏,等.西湖景区土壤典型重金属污染物的来源及空间分布特征[J].环境科学,2014,34(4):1516-1522.
[13] 郭伟,孙文惠,赵仁鑫,等.呼和浩特市不同功能区土壤重金属污染特征及评价[J].环境科学,2013,34(4): 1561-1567.
[14] 郭平,谢忠雷,李军,等.长春市土壤重金属污染特征及其潜在生态风险评价[J].地理科学,2005,25(1): 108-112.
[15] CHEN X D,LU X W.Contamination characteristics and source apportionment of heavy metals in topsoil from an area in Xi’an City, China[J].Ecotoxicology and environmental safety,2018,151:153-160.
[16] 汤海涛,李卫东,孙玉桃,等.不同叶面肥对轻度重金属污染稻田水稻重金属积累调控效果研究[J].湖南农业科学,2013(1):40-44.
[17] 郝汉舟,陈同斌,靳孟贵,等.重金属污染土壤稳定/固化修复技术研究进展[J].应用生态学报,2011,22(3):816-824.
[18] KHALID S,SHAHID M,NIAZI N K,et al.A comparison of technologies for remediation of heavy metal contaminated soils[J].Journal of geochemical exploration,2017,182(Part B):247-268.
[19] NAWAB J,KHAN S,AAMIR M,et al.Organic amendments impact the availability of heavy metal(loid) s in mine-impacted soil and their phytoremediation by Penisitum americanum and Sorghum bicolor[J].Environmental science and pollution research,2016,23(3):2381-2390.
[20] 任静华,廖启林,范健,等.凹凸棒粘土对镉污染农田的原位钝化修复效果研究[J].生态环境学报,2017,26(12):2161-2168.
[21] 周利军,武琳,林小兵,等.土壤调理剂对镉污染稻田修复效果[J].环境科学,2019,40(11):5098-5106.
[22] 鲍士旦. 土壤农化分析[M].北京:中国农业出版社,2000.
[23] LEE S W,LEE B T,KIM J Y.Human risk assessment for heavy metals and as contamination in the abandoned metal mine areas,Korea[J].Environmental monitoring and assessment,2006,119(1-3):233-244.
[24] 黄莹,李永霞,高甫威,等.小清河表层沉积物重污染区重金属赋存形态及风险评价[J].环境科学,2015,36(6):2046-2053.
[25] 沙乐乐. 水稻镉污染防控钝化剂和叶面阻控剂的研究与应用[D].武汉:华中农业大学,2015.
[26] 廖敏,黄昌勇,谢正苗.pH对镉在土水系统中的迁移和形态的影响[J].环境科学学报,1999,19(1):2-8.
[27] 王宇霞,郝秀珍,苏玉红,等.不同土壤调理剂对Cu、Cr和 Ni复合污染土壤的修复研究[J].土壤,2016, 48(1):123-130.
[28] 王灿,付天岭,龚思同,等.叶面阻控剂对黔中喀斯特地区水稻Cd富集特征的影响[J].浙江农业学报, 2021,33(9):1710-1719.
[29] 李心,林大松,刘岩,等.不同土壤调理剂对镉污染水稻田控镉效应研究[J].农业环境科学学报,2018,37(7):1511-1520.
[30] 靳辉勇,齐绍武,朱益,等.硅酸盐土壤调理剂对蔬菜Cd污染的治理效果[J].中国土壤与肥料,2017(1):149-152.
[31] 曾卉,徐超,周航,等.几种固化剂组配修复重金属污染土壤[J].环境化学,2012,31(9):1368-1374.
[32] 曾咏梅,毛昆明,李永梅.土壤中镉污染的危害及其防治对策[J].云南农业大学学报,2005,20(3):361-362.
[33] 莫文红,李懋学.镉离子对蚕豆根尖细胞分裂的影响[J].植物学通报,1992,9(3):30-34.
[34] YRUELA I,GATZEN G,PICOREL R,et al.Cu(Ⅱ)-inhibitory effect on Photosystem Ⅱ from higher plants: A picosecond time-resolved fluorescence study[J].Biochemistry,1996,35(29):9469-9474.
[35] ROOSENS N,VERBRUGGEN N,MEERTS P,et al.Natural variation in cadmium tolerance and its relationship to metal hyperaccumulation for seven populations of Thlaspi caerulescens from western Europe[J].Plant cell and environment,2010,26(10):1657-1672.
[36] 吴烈善,曾东梅,莫小荣,等.不同土壤调理剂对重金属污染土壤稳定化效应的研究[J].环境科学,2015,36(1):309-313.
[37] 许佳莹,朱练峰,禹盛苗,等.硅肥对水稻产量及生理特性影响的研究进展[J].中国稻米,2012,18(6):18-22.