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2024, 03, v.39 259-264
忍冬(L.japonica Thunb.)和钻叶紫菀(Aster subulatus Michx.)对较低浓度镉污染的超富集特征比较研究
基金项目(Foundation): 山东省重点研发计划资助项目(2020CXGC011404)
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摘要:

合适的超富集植物选择对于尾矿重金属污染修复至关重要。针对安丘市石埠子镇废弃矿坑镉(Cd)污染实际,结合忍冬(L.japonica Thunb.)和钻叶紫菀(Aster subulatus Michx.)对重金属Cd的超富集特征比较,分析了30天较低浓度Cd暴露(0.1 mg/kg, 0.3 mg/kg, 0.9 mg/kg)下两种超富集植物的毒性响应和超富集特征。研究表明,两种植物的株高和干重均受到明显影响(P<0.05),但忍冬对Cd的平均TF和BCF(TF_叶=0.494,TF_茎=0.357,BCF_叶=12.014,BCF_茎=8.689,BCF_根=24.424)明显高于钻叶紫菀的平均TF和BCF(TF_茎=0.127,TF_叶=0.205,BCF_叶=3.903,BCF_茎=2.412,BCF_根=19.189)(P<0.05)。这一研究成果对于废弃矿坑较低浓度Cd污染的超富集生态修复植物种类的选择,构建基于超富集植物的尾矿(渣)原位生态修复技术建设具有重要指导意义。

Abstract:

It is very important to realize the ecological remediation of heavy metal pollution in tailings based on the good selection of hyperaccumulators. This paper focuses on the comparative research on the Cd hyperaccumulation characteristics between two hyperaccumulators: L. japonica Thunb. and Aster subulatus Michx. exposed to the Cd pollution in the abandoned mine of Shipuzi, Anqiu. A 30 days exposure experiments were carried out with lower Cd concentrations including 0.1 mg/kg, 0.3 mg/kg, and 0.9 mg/kg. The results showed that the plant height and dry weight were all affected significantly in the two species with p<0.05. The average TF and BCF values of L. japonica Thunb.(TFLeaf=0.494, TFStem=0.357, BCFLeaf=12.014, BCFStem=8.689, BCFRoot=24.424) to different Cd concentration were significantly higher than Aster subulatus Michx.(TFStem=0.127, TFLeaf=0.205, BCFLeaf=3.903, BCFStem=2.412, BCFRoot=19.189) with P<0.05. This research will give some suggestions on the hyperaccumulator selection to the lower concentration Cd pollution in the abandoned mine, and can have important guiding significance for the in situ ecological restoration technology based on the heavy metal hyper accumulation characteristics.

参考文献

[ 1 ] 夏星辉,陈静生.土壤重金属污染治理方法研究进展[J].环境科学,1997,18(3):5.

[ 2 ] 秦世学.土壤镉污染对作物的影响及作物对土壤镉的吸收[J].环境科学丛刊,1983(10):10-22.

[ 3 ] 蒋水华,彭浩,余琦,等.基于生态系统服务价值的尾矿库溃坝短期生态环境损失评估[J].金属矿山,2023(5):213-220.

[ 4 ] 王一华,傅荣恕.中国生物修复的应用及进展[J].山东师范大学学报:自然科学版,2003,18(2):5.

[ 5 ] 韦朝阳,陈同斌.重金属超富集植物及植物修复技术研究进展[J].生态学报,2001,21(7):8.

[ 6 ] Yoshihara T,Suzui N,Ishii S,et al.A kinetic analysis of cadmium accumulation in a Cd hyper-accumulator fern,athyrium yokoscense and tobacco plants[J].Plant Cell & Environment,2014,37(5):1086-1096.

[ 7 ] 刘周莉,何兴元,陈玮.忍冬——一种新发现的镉超富集植物[J].生态环境学报,2013,22(4):666-670.

[ 8 ] 陈伟,蒋文艳,杨玉霞,等.一种新发现的镉超积累植物—钻叶紫菀(Aster subulatus Michx.)[J].生态学报,2023,43(13):5592-5599.

[ 9 ] Liu J,Shang W,Zhang X,et al.Mn accumulation and tolerance in Celosia argentea Linn.:A new Mn-hyperaccumulating plant species[J].Journal of Hazardous Materials,2014,267,136-141.

[10] 郑超,何碧虹,黄金丹.HS240149土壤检测报告[R].浙江九安检测科技有限公司,2024.2.2-2024.2.21

[11] Zayed A,Gowthaman S,Terry N .Phytoaccumulation of trace elements by wetland plants:I.Duckweed[J].Journal of Environmental Quality,1998,27(3),715-721.

[12] Brooks R R,Lee J,Reeves R D,et al.Detection of nickeliferous rocks by analysis of herbarium specimens of indicator plants[J].Journal of Geochemical Exploration,1977,7:49-57.

[13] 毋瑾超.海岛生态修复与环境保护[M].海洋出版社,2013.

[14] 吴志强,顾尚义,李海英,等.重金属污染土壤的植物修复及超积累植物的研究进展[J].环境科学与管理,2007,32(3):6.

[15] 聂亚平,王晓维,万进荣,等.几种重金属(Pb,Zn,Cd,Cu)的超富集植物种类及增强植物修复措施研究进展[J].生态科学,2016(2):9.

[16] 黄明煜.三种入侵植物对土壤重金属Cd,Pb污染的耐性和修复效应研究[D].广州:华南农业大学,2017.

[17] 高见.忍冬的开发利用及栽培技术[J].林业科技通讯,2003(5):44.

[18] 王文卿,陈琼著.南方滨海耐盐植物资源[M],厦门大学出版社,2013,9:398.

[19] 樊博,林丽,曹广民,等.不同演替状态下高寒草甸土壤物理性质与植物根系的相互关系[J].生态学报,2020,40(7):10.

[20] 刘玲,吴龙华,李娜,等.种植密度对镉锌污染土壤伴矿景天植物修复效率的影响[J].环境科学,2009,30(11):5.

基本信息:

DOI:

中图分类号:X173;X53

引用信息:

[1]李甲萌,张雅坤,陈波等.忍冬(L.japonica Thunb.)和钻叶紫菀(Aster subulatus Michx.)对较低浓度镉污染的超富集特征比较研究[J].山东师范大学学报(自然科学版),2024,39(03):259-264.

基金信息:

山东省重点研发计划资助项目(2020CXGC011404)

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