1. Key Laboratory of Prevention, Control and Remediation of Soil Heavy Metal Pollution in Hunan Province, Ministry of Agriculture Key Laboratory of Agriculture Environment in Middle Reach Plain of Yangtze River, Hunan Academy of Agriculture Sciences, Changsha 410125, China; 2. Changsha Technology Innovation Center for Phytoremediation of Heavy Metal Contaminated Soil, Changsha 410125, China
Abstract:To explore the effects of iron-based silicon on the bioavailability and transformation of cadmium (Cd) and arsenic (As) in soil, laboratory long-term flooding cultivation culture adsorption experiment were carried out with Cd/As mild co-contaminated soil. Different proportions of Fe-Si materials and various iron-silicon salt (FS) components in combination with humic acid (FSC) and metal oxide (FSCa) were studied in the Cd-As soil. The morphological changes of Cd and As in the soil treated with the above complex agents were evaluated. The results showed that the ratio of iron to silicon was increased by 10%, the soil pH value was decreased by 0.35. Under F2-S8 treatment, ionized Cd in the soil was decreased by 71%. F10-S0 treatment reduced As ion state by 59.9%, and the content of ionized Cd and As were inversely proportional to the application ratios of iron salts and silicates. The intersection of Cd and As passivation rates between F4-S6 and F6-S4 was found to be between 25%~30%. Soluble Cd was the main compound of total Cd in soil, representing approximately 58%; As was mainly present in Fe-Al oxidation state and Ca binding state, accounting for 40% and 23% of total As, respectively. The ratios of iron to silicon from about 5.0:5.0 or 5.5:4.5 could effectively convert Al-bound As and Fe-Al oxide-bound As to Ca-bound As and residue state As. Meanwhile, soluble Cd can be converted into carbonate state Cd and Fe-Mn oxides state Cd. In conclusion, the bioavailability of Cd and As in soil can be simultaneously reduced by iron-based silicon compounds.
Li Z, Ma Z, Kuijp T, et al. A review of soil heavy metal pollution from mines in China:pollution and health risk assessment[J]. Science of The Total Environment, 2014,468-469:843-853.
[2]
朱智伟,陈铭学,牟仁祥,等.水稻镉代谢与控制研究进展[J]. 中国农业科学, 2014,47(18):3633-3640. Zhu Z W, Chen M X, Mou R X, et al. Advances in research of cadmium metabolism and control in rice plants[J]. Scientia Agricultura Sinica, 2014,47(18):3633-3640.
[3]
肖细元,陈同斌,廖骁勇,等.中国主要含砷矿产资源的区域分布与砷污染问题[J]. 地理研究, 2008,27(1):201-212. Xiao X Y, Chen T B, Liao X Y, et al. Regional distribution of arsenic contained minerals and arsenic pollution in China[J]. Geographical Research, 2008,27(1):201-212.
[4]
全国土壤污染状况调查公报[R]. 北京:中华人民共和国环境保护部,中华人民共和国国土资源部, 2014. The nationwide survey communique of soil pollution[R]. Beijing:Ministry of Environmental Protection of the People 's Republic of China, Ministry of Land and Resources of the People 's Republic of China, 2014-04-17.
[5]
王英杰,邹佳玲,杨文弢,等.组配改良剂对稻田系统Pb、Cd和As生物有效性的协同调控[J]. 环境科学, 2016,37(10):4004-4010. Wang Y J, Zou J L, Yang W T, et al. Synergetic control of bioavailability of Pb, Cd and As in rice paddy system by combined amendments[J]. Chinese Journal of Environmental Science, 2016, 37(10):4004-4010.
[6]
贺玉龙.镉砷在土壤中的赋存形态及生物有效性研究[J]. 绿色科技, 2019,10(5):108-109,112. He Y L. Preliminary study on the disposal of hazardous wastes produced by enterprise[J]. Journal of Green Science and Technology, 2019,10(5):108-109,112.
[7]
王一志,曹雪莹,谭长银,等.不同土壤pH对红壤稻田镉形态及水稻镉积累的影响[J]. 湖南师范大学自然科学学报, 2017,40(1):10-16. Wang Y Z, Cao X Y, Tan C Y, et al. Effects of different soil pH on cadmium fractions and cadmium accumulation in rice[J]. Journal of Natural Science of Hunan Normal University, 2017,40(1):10-16.
[8]
Tessier A, Campbell P G C, Bisson M. Sequential extraction procedure for the speciation of particulate trace metals[J]. Analytical Chemistry, 1979,51(7):844-851.
[9]
朱利楠,化党领,杨金康,等.不同改良剂对微碱性土壤镉形态及小麦吸收的影响[J]. 中国环境科学, 2020,40(8):3559-3566. Zhu L N, Hua D L, Yang J K, et al. Effects of different amendments on chemical speciation and uptake by winter wheat in slightly alkaline soil contaminated by Cadmium[J]. China Environmental Science, 2020,40(8):3559-3566.
[10]
吴川,安文慧,薛生国,等.土壤-水稻系统砷的生物地球化学过程研究进展[J]. 农业环境科学学报, 2019,38(7):1429-1439. Wu C, An W H, Xue S G, et al. Arsenic biogeochemical proceeding in the soil- rice system[J]. Journal of Agro-Environment Science, 2019,38(7):1429-1439.
[11]
官迪,吴家梅,刘昭兵,等.外源硫化钠对土壤-水稻体系中镉迁移积累的影响[J]. 农业环境科学学报, 2021,40(7):1460-1469. Guan D, Wu J M, Liu Z B, et al. Effects of exogenous sodium sulfide on cadmium migration and accumulation in soil and rice plant systems[J]. Journal of Agro-Environment Science, 2021,40(7):1460-1469.
[12]
郭娟,罗小丽,姚爱军,等.模拟酸雨条件下铁硅材料和生物炭对土壤镉砷形态及生物有效性的影响[J]. 农业环境科学学报, 2018,37(7):1495-1502. Guo J, Luo X L, Yao A J, et al. Effects of iron-silicon material and biochar on soil Cd and As speciation and vegetable uptake under simulated acid rain condition[J]. Journal of Agro-Environment Science, 2018,37(7):1495-1502.
[13]
郜礼阳,邓金环,唐国强,等.不同温度桉树叶生物炭对Cd2+的吸附特性及机制[J]. 中国环境科学, 2018,38(3):1001-1009. Gao L Y, Deng J H, Tang G Q, et al. Adsorption characteristics and Mechanism of Cd2+ on biochar with different pyrolysis temperatures produced from eucalyptus leaves[J]. China Environmental Science, 2018,38(3):1001-1009.
[14]
Yuan C L, Qiao J T, Li F B, et al. Community dynamics of As (V) reducing and As (III)-oxidizing genes during a wet-dry cycle in paddy soil amended with organic matter, gypsum, or iron oxide[J]. Journal of Hazardous Materials, 2020,393:122485.
[15]
Wang X Q, Yu H Y, Li F B, et al. Enhanced immobilization of arsenic and cadmium in a paddy soil by combined applications of woody peat and Fe(NO3)3:Possible mechanisms and environmental implications[J]. Science of the Total Environment, 2019,649:535-543.
[16]
蒋毅,刘雅,辜娇峰,等.三元复合调理剂对土壤镉砷赋存形态和糙米镉积累的调控效应[J]. 环境科学, 2021,42(13):173-185. Jiang Y, Liu Y, Gu J F, et al. Regulation control of a tribasic amendment on the chemical fractions of Cd and As in paddy soil and their accumulation in rice[J]. Environmental Scicence, 2021,42(13):173-185.
[17]
Wu J Z, Huang D, Liu X M, et al. Remediation of As (III) and Cd (II) co-contamination and its mechanism in aqueous systems by a novel calcium-based magnetic biochar[J]. Journal of Hazardous Materials, 2018,348:10-19.
[18]
王芳婷,陈植华,包科,等.pH值对海陆交互相土壤镉纵向迁移转化的影响[J]. 中国环境科学, 2021,41(1):335-341. Wang F T, Chen Z H, Bao K, et al. Effects of pH on vertical migration of cadmium in the sea land interaction zone[J]. China Environmental Science, 2021,41(1):335-341.
[19]
李英,商建英,黄益宗,等.镉砷复合污染土壤钝化材料研究进展[J/OL]. 土壤学报, 2021,(4):1-12[2021-08-24]. http://kns.cnki.net/kcms/detail/32.1119.P.20201022.1110. 002.html. Li Y, Shang J Y, Huang YZ, et al. Research progress on passivation materials for cadmium arsenic co-contamination in soil[J]. Acta Pedologica Sinica,http://kns.cnki.net/kcms/detail/32.1119.P.20201022. 1110. 002.html.
[20]
鲁如坤.土壤农业化学分析方法[M]. 北京:中国农业科技出版社, 1999:80-82. Lu R K. Methods for agricultural chemical analysis of soil[M]. Beijing:China Agricultural Science and Technology Press, 1999:80-82.
[21]
Herreweghe S V, Swennen R, Vandecasteele C, et al. Solid phase speciation of arsenic by sequential extraction in standard reference materials and industrially contaminated soil samples[J]. Environment Pollution, 2003,122:323-342.
[22]
Bolan N, Kunhigrishnan A, Thangaran R, et al. Remediation of heavy metal(loid)s contaminated soils-to mobilize or to immobilize?[J]. Journal of Hazardous Materials, 2013,261(20):725-732.
[23]
Park D R, Pedler J F. Reevaluation of the free ion activity model of trace metal availability to higher plants[J]. Plant Soil.1996,196:223- 228.
[24]
吴和秋,侯钦宣,张英.含铁介质用于修复砷污染土壤研究综述[J]. 中国土壤与肥料, 2018,(2):13-21,66. Wu H Q, Hou Q X, Zhang Y. Review of remedying the arsenic contaminated soil with Fe-based media[J]. Soil and Fertilizer Sciences in China, 2018,(2):13-21,66.
[25]
张弛.铁改性生物质电厂灰对镉砷复合污染土壤钝化修复研究[D]. 河北:河北地质大学, 2019. Zhang C. Study on passivation and repair of cadmium arsenic compound contaminated soil by iron modified biomass power plant ash[D]. HeBei:Hebei University of Geosciences, 2019.
[26]
冀建华,李絮花,刘秀梅,等.硅钙钾镁肥对南方稻田土壤酸性和盐基离子动态变化的影响[J]. 应用生态学报, 2019,30(2):583-592. Ji J H, Li X H, Liu X M, et al. Effects of fertilizer of calcium silicon magnesium potassium on the dynamics of soil acidity and exchangeable base case cation in paddy field of Southern China[J]. Chinese Journal of Applied Ecology, 2019,30(2):583-592.
[27]
贺敏杰,蔡昆争,王维,等.硅素分期施用对土壤镉形态和水稻镉积累的影响[J]. 农业环境科学学报, 2018,37(8):1651-1659. He M J, Cai K Z, Wang W, et al. Effects of split silicon application on the fractions of Cd in soil and its accumulation in rice[J]. Journal of Agro-Environment Science, 2018,37(8):1651-1659.
[28]
郭磊.外源硅影响镉化学形态及其生物有效性的土壤化学机制[D]. 沈阳:沈阳农业大学, 2018. Guo L. The soil chemistry mechanisms of influences on cadmium chemical speciation and bioavailability with exogenous silicon[D]. ShenYang:Shenyang Agriculture University, 2018.
[29]
陈楠,张昊,杨慧敏,等.土壤pH对土壤镉形态及稻米镉积累的影响[J]. 湖南农业大学学报, 2018,44(2):176-182. Chen N, Zhang H, Yang H M, et al. Effects of soil pH on soil cadmium formations and its accumulation in rice[J]. Journal of Hunan Agriculture Unviersity, 2018,44(2):176-182.
[30]
Yu H Y, Ding X B, Li F B, et al. The availabilities of arsenic and cadmium in rice paddy fields from a mining area:the role of soil extractable and plant silicon[J]. Environment Pollution, 2016,215:258-265.
[31]
罗梅,柏宏成,陈亭悦,等.腐殖酸对土壤铅镉吸附、赋存形态及生物可给性的影响[J]. 中国环境科学, 2020,40(3):1191-1202. Luo M, Bai H C, Chen L Y, et al. Effects of humic acids on the adsorption, chemical speciation, and bioaccessibility of soil lead and cadmium[J]. China Environmental Science, 2020,40(3):1191-1202.
[32]
胡敏,李芳柏.土壤微生物铁循环及其环境意义[J]. 土壤学报, 2014,51(4):683-698. Hu M, Li F B. Soil microbe mediated iron cycling and its environmental implication[J]. Acta Pedologica Sinica, 2014,51(4):683-698.
[33]
李志明,丁氏祝,奇奇格,等.施用铁锰对土壤砷形态及水稻吸收砷的影响[J]. 西南农业学报, 2020,33(8):1722-1728. Li Z M, Ding S Z, Qi Q G, et al. Effects of iron and manganese application on soil arsenic fractions and arsenic uptake by rice[J]. Southwest China Journal of Agricultural Science, 2020,33(8):1722- 1728.
[34]
尹雪斐,杨蕊嘉,刘玉玲,等. Cd(Ⅱ)与As(Ⅴ)在土壤铁氧化物和细菌表面上的共吸附研究[J]. 生态环境学报, 2021,30(3):614-620. Yin X F, Yang R J, Liu Y L, et al. Co-adsorption of Cd(Ⅱ) and As(Ⅴ) on soil iron oxide and bacterial surface[J]. Ecology and Environmental Sciences, 2021,30(3):614-620.