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GA3与EDTA强化黑麦草修复Pb污染土壤及其解毒机制

吴秋玲1,王文初2,何闪英1**   

  1. (1浙江工商大学环境科学与工程学院/浙江省固体废物处理与资源化重点实验室, 杭州 310012; 2台州市环境保护局, 浙江台州 310800)
  • 出版日期:2014-10-18 发布日期:2014-10-18

Enhancement of GA3 and EDTA on Lolium perenne to remediate Pb contaminated soil and its detoxification mechanism.

WU Qiu-ling1, WANG Wen-chu2, HE Shan-ying1   

  1. (1College of Environmental Science and Engineering, Zhejiang Provincial Key Laboratory of Solid Waste Treatment and Recycling, Zhejiang Gongshang University, Hangzhou 310012, China; 2Environmental Protaction Agency of Taizhou, Taizhou 310800, Zhejiang, China)
  • Online:2014-10-18 Published:2014-10-18

摘要: 采用盆栽土培方法研究了生长调节剂GA3和重金属螯合剂EDTA强化黑麦草修复Pb外源浓度分别为250和500 mg·kg-1的污染土壤以及黑麦草Pb解毒机制.结果表明: 细胞壁沉积和液泡区室化在黑麦草地上部分Pb的解毒中起重要作用.EDTA单独使用提高了植物体内Pb的浓度和Pb在细胞可溶组分和细胞器组分中的比例,增强了Pb对植物的毒害作用,从而使植物生物量显著下降(P<0.05).叶面喷洒低浓度GA3(1或10 μmol·L-1)显著促进黑麦草对Pb的富集,但Pb在细胞器组分中的比例降低,缓解了Pb对植物细胞的伤害,从而促进了黑麦草的生长(P<0.05),其中1 μmol·L-1 GA3作用最显著.100 μmol·L-1 GA3降低了黑麦草体内Pb浓度,但Pb在细胞可溶组分和细胞器组分中的比例提高,使黑麦草的生物量明显低于对照.低浓度GA3可在一定程度上缓解Pb和/或EDTA对黑麦草的毒害,生物量表现为低浓度GA3 单独>低浓度GA3+EDTA>EDTA单独使用.低浓度GA3和EDTA联用时的协同作用强化了黑麦草对Pb的富集,其中,在外源Pb浓度为500 mg·kg-1处理组中,EDTA+1 μmol·L-1 GA3使黑麦草地上部分Pb浓度和提取效率分别达到1250.6 mg·kg-1和1.1%.因此,1 μmol·L-1 GA3与EDTA联用在强化Pb污染土壤植物修复中具有很好的应用潜力.

Abstract: A pot experiment was conducted to study the effects of plant growth regulator GA3 and metal chelate EDTA on enhancing the remediation of Pb contaminated soil, and the detoxification mechanism of Lolium perenne grown on Pb contaminated soil at 250 and 500 mg·kg-1. The results showed that cell wall deposition and vacuolar compartmentalization played important roles in the detoxification of Pb in L. perenne shoot. The addition of EDTA alone increased Pb concentration in plants and Pb proportions in soluble fraction and organelles fraction, and enhanced the toxicity of Pb to plant, leading to the significant reduction of the plant biomass (P<0.05). Foliar spray of lower concentration of GA3(1 μmol·L-1 or 10 μmol·L-1) alone significantly increased Pb accumulation by L. perenne (P<0.05), but Pb proportions in soluble and organelles fraction were decreased, which alleviated the adverse effects of Pb on plant, thus improving the growth of plants (P<0.05), with 1 μmol·L-1 GA3 being the most effective. In contract, the addition of 100 μmol·L-1 GA3 decreased Pb concentration in L. perenne, but increased the proportions of Pb in soluble fraction and organelles fraction, resulting in the reduction of plant biomass. Lower concentration of GA3 might alleviate the adverse effects of Pb and/or EDTA on plant, since the biomass amounts in the different treatments were in order of GA3 alone of lower concentration > GA3 of lower concentration+EDTA > EDTA alone. The combination application of low concentration of GA3 and EDTA showed a synergistic effect on the Pb accumulation in L. perenne (P<0.05). Especially, Pb concentration in shoot and Pb extraction efficiency reached 1250.6 mg·kg-1 and 1.1%, respectively, under the treatment of EDTA+1 μmol·L-1 GA3 on the Pb 500 mg·kg-1 soil. Therefore, the application of 1 μmol·L-1 GA3 along with EDTA appeared to be a potential approach for phytoremediation of Pb contaminated soil.