Study on the inhibition and control effect of compound amendment on cadmium pollution in rice and soil

doi:10.14088/j.cnki.issn0439-8114.2021.14.008

Abstract

Abstract: Three local rice varieties, Maba Younian, Jinnong Simiao and Meixiangzhan 2, were selected as the research objects in Zhongshan city. Experiments were carried out in the field to study the resistance and control effects of compound amendments on cadmium pollution in rice and soil. The results showed that the compound amendments could significantly reduce the cadmium content in rice plants, and the compound amendments could significantly passivate the soil available cadmium; The cadmium content of rice was different between varieties and parts of rice, and Maba Younian had stronger passivation effect on available cadmium in rhizosphere soil than Meixiangzhan 2, which led to the lower cadmium content in all parts of Maba Younian than Meixiangzhan 2. The distribution of Cd content in different parts of rice plant was as follows： Root > stem leaf > brown rice > rice husk. When the local use amount of compound amendment was 900 kg/hm², the cadmium content in brown rice of rice could be reduced to the limit of the national standard 0.2 mg/kg.

Key words: rice, cadmium pollution, compound amendment, soil, passivation effect

CLC Number:

LI Xiao-peng, ZHOU Jia-cheng, CHEN Nan, MA Shi-zhu, FENG Dong-yi, LIN Jun-jie, ZHANG Yu-shan. Study on the inhibition and control effect of compound amendment on cadmium pollution in rice and soil[J]. HUBEI AGRICULTURAL SCIENCES, 2021, 60(14): 46-50.

References 38

[1]	马瑾,潘根兴,万洪富,等.珠江三角洲典型区域土壤重金属污染探查研究[J].土壤通报,2004,35(5):636-638.
[2]	罗小玲,郭庆荣,谢志宜,等.珠江三角洲地区典型农村土壤重金属污染现状分析[J].生态环境学报,2014,23(3): 485-489.
[3]	蔡文华,胡曙光,苏祖俭,等.2014年广东省居民重点食品中金属污染物的健康风险评估[J].环境与健康杂志, 2016,33(6):536-540.
[4]	邹富桢. 无机—有机混合改良剂对酸性多金属污染土壤的修复效应[D].广州:华南农业大学,2016.
[5]	李江遐,吴林春,张军,等.生物炭修复土壤重金属污染的研究进展[J].生态环境报,2015,24(12):2075-2081.
[6]	陈昱,梁媛,郑章琪,等.老化作用对水稻秸秆生物炭吸附Cd(Ⅱ)能力的影响[J].环境化学,2016,35(11): 2337-2343.
[7]	王红岩. 硅肥以及水钠锰矿负载型稻壳生物炭对水稻砷和镉的共同阻控作用[D].北京:中国地质大学,2016.
[8]	罗思颖,周卫军,曹胜,等.钾硅钙微孔矿物肥对稻田土壤及稻谷镉污染的阻控效果[J].湖南农业科学,2016(6): 30-32.
[9]	杜文慧,王京津,朱维琴,等.中轻度污染菜地土壤中重金属阻控剂组合优化研究[J].杭州师范大学学报(自然科学版),2016,15(3):260-266.
[10]	王瑶瑶,郝毅,张洪,等.珠三角地区大米中的镉砷污染现状及治理措施[J].中国农学通报,2019,35(12): 63-72.
[11]	唐行灿. 生物炭修复重金属污染土壤的研究[D].山东泰安:山东农业大学,2013.
[12]	任露陆,吴文成,陈显斌,等.碳酸钙与氢氧化钙修复重金属污染土壤效果差异研究[J].环境科学与技术,2016, 39(5):22-27.
[13]	蒙冬柳,宋波.沸石在重金属污染土壤修复中的应用进展[J].吉林农业,2011(3):200-200.
[14]	梁媛,王晓春,曹心德.基于磷酸盐、碳酸盐和硅酸盐材料化学钝化修复重金属污染土壤的研究进展[J].环境化学,2012,31(1):16-25.
[15]	徐燕玲,陈能场,徐胜光,等.低镉累积水稻品种的筛选方法研究—品种与类型[J].农业环境科学学报,2009(7): 1346-1352.
[16]	HAN Y L, SHENG Z, LIU G D, et al.Cloning, characterization and cadmium inducibility of metallothionein in the testes of the mudskipper Boleophthalmus pectinirostris[J]. Ecotoxicol Environ Saf,2015,119:1-8.
[17]	SUI F Q, ZHAO D K, ZHU H T, et al.Map-based cloning of a new total loss-of-function allele of OsHMA3 causes high cadmium accumulation in rice grain[J]. J Exp Bot,2019,70(10):2857-2871.
[18]	吴启堂,陈卢,王广寿.水稻不同品种对Cd吸收累积的差异和机理研究[J].生态学报,1999,19(1):104-107.
[19]	范洪黎,王旭,周卫.不同镉积累型苋菜(Amaranthus mangostanus L.)根际低分子量有机酸与镉吸收的关系[J].中国农业科学,2007,40(12):2727-2733.
[20]	肖清铁,王经源,郑新宇,等.水稻根系响应镉胁迫的蛋白质差异表达[J].生态学报,2015,35(24):8276-8283.
[21]	TAKAHASHI R, ISHIMARU Y, SENOURA T, et al.The OsNRAMP1 iron transporter is involved in Cd accumulation in rice[J].J Exp Bot,2011,62(14):4843-4850.
[22]	ISHIKAWA S, ISHIMARU Y, IGURA M, et al.Ion-beam irradiation, gene identification, and marker-assisted breeding in the development of low-cadmium rice[J].Proc Natl Acad Sci USA,2012,109(47):19166-19171.
[23]	MA F F, ZHAO B W, DIAO J R.Adsorption of cadmium by biochar produced from pyrolysis of corn stalk in aqueous solution[J].Water Sci Technol,2016,74(6):1335-1345.
[24]	WU C X, LI Y G, CHEN M J, et al.Adsorption of cadmium on degraded soils amended with maize-stalk-derived biochar[J]. J Environ Res Public Health,2018,15(11):2331.
[25]	ZHU L, TONG L H, ZHAO N, et al.Key factors and microscopic mechanisms controlling adsorption of cadmium by surface oxidized and aminated biochars[J]. J Hazard Mater,2020,382:121002.
[26]	张凤. 生物炭和负载铁生物炭对镉、砷的吸附钝化效应与反应机制[D].长沙:湖南师范大学,2016.
[27]	GRAY C W, DUNHAM S J, DENNIS P G, et al.Field evaluation of in situ remediation of a heavy metal contaminated soil using lime and red-mud[J].Environ Pollut,2006,142(3):530-539.
[28]	张茜,徐明岗,张文菊,等.磷酸盐和石灰对污染红壤与黄泥土中重金属铜锌的钝化作用[J].生态环境,2008, 17(3):1037-1041.
[29]	朱颖. 生物炭和石灰石对大冶市农田土壤镉的原位钝化修复[D].武汉:华中农业大学,2017.
[30]	MA J F.Role of silicon in enhancing the resistance of plants to biotic and abiotic stresses[J]. Soil science and plant nutrition,2004,50(1):11-18.
[31]	IWASAKI K, MAIER P, FECHT M, et al.Effects of silicon supply on apoplastic manganese concentrations in leaves and their relation to manganese tolerance in cowpea (Vigna unguiculata (L.) Walp.)[J]. Plant and soil, 2002,238: 281-288.
[32]	SHI X H, ZHANG C C, WANG H, et al.Effect of Si on the distribution of Cd in rice seedlings[J]. Plant and soil,2005,272(1/2):53-60.
[33]	杨超光,豆虎,梁永超,等.硅对土壤外源镉活性和玉米吸收镉的影响[J].中国农业科学,2005,38(1):116-121.
[34]	王晨,王海燕,赵琨,等.硅对镉、锌、铅复合污染土壤中黑麦草生理生化性质的影响[J].生态环境,2008,17(6):2240-2245.
[35]	杨肖娥,杨明杰.镉从农业土壤向人类食物链的迁移[J].广东微量元素科学,1996,3(7):1-13.
[36]	刘霞,刘树庆,唐兆宏.潮土和潮褐土中重金属形态与土壤酶活性的关系[J].土壤学报,2003,40(4):581-587.
[37]	杨秀敏,任广萌,李立新,等.土壤pH值对重金属形态的影响及其相关性研究[J].中国矿业,2017,26(6):79-83.
[38]	TESSIER A, CAMPBELL P G C, BISSON M. Sequential extraction procedure for the speciation of particulate trace metal[J]. Analytical chemistry,1979,51(7):844-851.