| 349 | 2 | 53 |
| 下载次数 | 被引频次 | 阅读次数 |
以江西某铜矿区产生的酸性矿山废水(AMD)为对象,探究了8种植物对其的净化效果。结果表明:8种植物均能显著提升AMD的pH,从初始pH的5提升至6.5~7.2,其中八宝景天对AMD的pH提升效果最佳。AMD中重金属去除方面,狗牙根对Cu、Cd的去除率最高,分别达到95%和92%,紫花苜蓿对Pb的去除率达到97%。黑麦草对Cu、Cd的富集效果显著,富集量分别高达31 228.75、708.72 mg/kg;八宝景天对Pb的富集量最高,为667.71mg/kg。8种植物中,香薷草对Pb、黑麦草对Cd、紫花苜蓿对Cu具有较好的转运能力。本研究为酸性复合重金属污染水体的植物修复提供了数据支撑。
Abstract:Acid mine drainage(AMD) is characterized by a low pH value and a high concentration of heavy metal ions, which poses a severe threat to the surrounding ecological environment. In this study, the AMD generated from a waste rock dump of a copper mine in Jiangxi province was taken as the research object, and the purification effects of eight restoration plants, namely Festuca arundinacea, Cynodon dactylon, Lolium perenne, Medicago sativa,Sedum spectabile, Elsholtzia ciliata, Solanum nigrum, and Ophiopogon japonicus, on AMD were comparatively investigated. The research results show that all eight restoration plants can significantly increase the pH value of AMD, raising it from the initial pH of 5 to the range of 6.5–7.2. Among them, Sedum spectabile has the most remarkable effect on increasing the pH value. In terms of heavy metal removal, different plants exhibit significant differences. Cynodon dactylon has the highest removal rates for Cu and Cd, reaching 95% and 92% respectively.Medicago sativa has a Pb removal rate as high as 97%, and Elsholtzia ciliata, Solanum nigrum and Medicago sativa also show good Pb-removal effects. Regarding the heavy-metal enrichment capacity, Lolium perenne has a Cu enrichment amount of 31 228.75 mg/kg, showing a significant advantage in Cu enrichment. In terms of Cd enrichment, Lolium perenne, Cynodon dactylon, and Medicago sativa rank among the top three, with Lolium perenne having an extremely high Cd enrichment amount of 708.72 mg/kg. Sedum spectabile has the highest Pb enrichment amount, which is 667.71 mg/kg. In addition, Elsholtzia ciliata, Medicago sativa and Lolium perenne have relatively high translocation factors for heavy metals Cu, Cd, and Pb. The translocation factor of Elsholtzia ciliata for Pb is significantly higher than that of other plants. The translocation factor of Lolium perenne for Cd is greater than 1, indicating a strong translocation ability. Medicago sativa has a relatively high translocation factor for Cu.This study systematically explores the purification effects, enrichment, and translocation characteristics of the eight restoration plants on heavy metals in AMD. The results can provide strong support for the phytoremediation of acid water bodies contaminating complex heavy metals, offering valuable references for future research and practical applications in this field.
[1] THOMAS G, SHERIDAN C, HOLM P E. A critical review of phytoremediation for acid mine drainage-impacted environments[J]. Science of The Total Environment, 2022,811:152230. DOI:10.1016/j.scitotenv.2021.152230.
[2] LI Z Y, MA Z W, Van Der KUIJP T J, 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.
[3] GAVRILESCU M. Enhancing phytoremediation of soils polluted with heavy metals[J]. Current Opinion in Biotechnology, 2022, 74:21-31.
[4] POURESMAIELI M, ATAEI M, FOROUZANDEH P, et al.Recent progress on sustainable phytoremediation of heavy metals from soil[J]. Journal of Environmental Chemical Engineering, 2022, 10(5):108482. DOI:10.1016/j.jece.2022.108482.
[5]朱剑飞,李铭红,谢佩君,等.紫花苜蓿、黑麦草和狼尾草对Cu、Pb复合污染土壤修复能力的研究[J].中国生态农业学报, 2018, 26(2):303-313.ZHU J F, LI M H, XIE P J, et al. Phytoremediation of single and combined pollution of Cu and Pb by Medicago sativa,Lolium perenne, and Pennisetum alopecuroides[J]. Chinese Journal of Eco-Agriculture, 2018, 26(2):303-313.
[6]葛元英,乔乔,张鹏,等.晋南铬渣堆场主要植物重金属富集特征[J].环境污染与防治, 2020, 42(7):833-837.GE Y Y, QIAO Q, ZHANG P, et al. Heavy metal enrichment characteristics of dominant plants naturally growing on chromium residue dump site in southern Shanxi[J].Environmental Pollution&Control, 2020, 42(7):833-837.
[7] SONG X L, LI C J, CHEN W F. Phytoremediation potential of Bermuda grass(Cynodon dactylon(L.)pers.)in soils co-contaminated with polycyclic aromatic hydrocarbons and cadmium[J]. Ecotoxicology and Environmental Safety, 2022,234:113389. DOI:10.1016/j.ecoenv.2022.113389.
[8] WANG X, FANG L C, BEIYUAN J Z, et al. Improvement of alfalfa resistance against Cd stress through rhizobia and arbuscular mycorrhiza fungi co-inoculation in Cd-contaminated soil[J]. Environmental Pollution, 2021, 277:116758. DOI:10.1016/j.envpol.2021.116758.
[9] ZHAO X F, LEI M, WEI C H, et al. Assessing the suitable regions and the key factors for three Cd-accumulating plants(Sedum alfredii, Phytolacca americana, and Hylotelephium spectabile)in China using MaxEnt model[J]. Science of The Total Environment, 2022, 852:158202. DOI:10.1016/j.scitotenv.2022.158202.
[10]金勇,付庆灵,郑进,等.超积累植物修复铜污染土壤的研究现状[J].中国农业科技导报, 2012, 14(4):93-100.JIN Y, FU Q L, ZHENG J, et al. Research status on phytoremediation of copper contaminated soil with hyperaccumulator[J]. Journal of Agricultural Science and Technology, 2012, 14(4):93-100.
[11]李振飞,李书钦,童立志,等.龙葵对典型酸性矿山废水重金属的处理效果研究[J].环境工程技术学报, 2025, 15(1):268-278.LI Z F, LI S Q, TONG L Z, et al. Study on the treatment of heavy metals in typical acidic mine drainage by Solanum nigrum L.[J]. Journal of Environmental Engineering Technology, 2025, 15(1):268-278.
[12] ZHANG S S, SUN J H, FENG D D, et al. Unlocking the potentials of cyanobacterial photosynthesis for directly converting carbon dioxide into glucose[J]. Nature Communications, 2023, 14(1). DOI:10.1038/s41467-023-39222-w.
[13]胡金朝.重金属污染对不同生境水生植物的毒害机理研究[D].南京:南京师范大学, 2006.HU J C. Research on the toxic mechanism of heavy metal pollution on aquatic plants in different habitats[D]. Nanjing:Nanjing Normal University, 2006.
[14] HU H J, XU K, HE L C, et al. A model for the relationship between plant biomass and photosynthetic rate based on nutrient effects[J]. Ecosphere, 2021, 12. DOI:10.1002/ecs2.3678.
[15] NGUEGANG B, MASINDI V, MAKUDALI T A M, et al.Effective treatment of acid mine drainage using a combination of MgO-nanoparticles and a series of constructed wetlands planted with Vetiveria zizanioides:a hybrid and stepwise approach[J]. Journal of Environmental Management, 2022,310:114751. DOI:10.1016/j.jenvman.2022.114751.
[16] KIISKILA J D, LI K F, SARKAR D, et al. Metabolic response of vetiver grass(Chrysopogon zizanioides)to acid mine drainage[J]. Chemosphere, 2020, 240:124961. DOI:10.1016/j.chemosphere.2019.124961.
[17] SKUZA L, SZU?KO-KOCIUBA I, FILIP E, et al. Natural molecular mechanisms of plant hyperaccumulation and hypertolerance towards heavy metals[J]. International Journal of Molecular Sciences, 2022, 23:9335. DOI:10.3390/ijms23169335.
[18] KAMA R, LIU Y, ZHAO S Q, et al. Combination of intercropping maize and soybean with root exudate additions reduces metal mobility in soil-plant system under wastewater irrigation[J]. Ecotoxicology and Environmental Safety, 2023,266:115549. DOI:10.1016/j.ecoenv.2023.115549.
[19] XIE H, MA Y H, WANG Y Y, et al. Biological response and phytoremediation of perennial ryegrass to halogenated flame retardants and Cd in contaminated soils[J]. Journal of Environmental Chemical Engineering, 2021, 9(6):106526.DOI:10.1016/j.jece.2021.106526.
[20]王慧,李长爱,李亚亮,等.高浓度镉(Cd)、铅(Pb)胁迫对铜钱草生长和生理生化参数的影响[J].生态毒理学报, 2025,20(1):440-450.WANG H, LI C A, LI Y L, et al. Effects of high concentrations of cadmium and lead stress on growth, physiological and biochemical parameters in Hydrocotyle vulgaris L.[J]. Asian Journal of Ecotoxicology, 2025, 20(1):440-450.
[21] GHUGE S A, NIKALJE G C, KADAM U S, et al.Comprehensive mechanisms of heavy metal toxicity in plants, detoxification, and remediation[J]. Journal of Hazardous Materials, 2023, 450:131039. DOI:10.1016/j.jhazmat.2023.131039.
基本信息:
DOI:10.20237/j.issn.1007-7545.2025.10.018
中图分类号:X751;X173
引用信息:
[1]郭靖,董颖博,刘俊飞,等.不同植物对酸性矿山废水中重金属的富集能力对比研究[J].有色金属(冶炼部分),2025(10):189-196.DOI:10.20237/j.issn.1007-7545.2025.10.018.
基金信息:
国家重点研发计划项目(2023YFC3207300)
2025-04-03
2025
2025-07-15
2025-07-16
2025
1
2025-09-28
2025-09-28