Mechanistic Changes During Phytoremediation of Perchlorate Under Different Root-Zone Conditions

植物修复 高氯酸盐 硝酸盐 化学 生物反应器 根际 环境化学 DNS根区域 园艺 环境科学 土壤水分 重金属 土壤科学 生物 离子 有机化学 细菌 遗传学
作者
Valentine A. Nzengung,Holger Penning,W. L. O'Niell
出处
期刊:International Journal of Phytoremediation [Taylor & Francis]
卷期号:6 (1): 63-83 被引量:32
标识
DOI:10.1080/16226510490439990
摘要

ABSTRACT Two types of hydroponic bioreactors were used to investigate the mechanisnistic changes during phytoremediation of perchlorate under different root-zone conditions. The bioreactors included: (1) an aerobic ebb-and-flow system planted with six willow trees, and (2) individual willow trees grown in sealed root-zone bioreactors. Rhizosphere probes were used to monitor for the first time during phytoremediation of perchlorate, diurnal swings in oxidation-reduction potential (EH), dissolved oxygen (DO), and pH. Radiolabeled (36Cl-labeled) perchlorate was used as a tracer in a subset of the sealed bioreactor experiments to quantify the contribution of phytodegradation and rhizodegradation mechanisms. Rhizodegradation accounted for the removal of 96.1 ± 4.5% (± 95% CI) of the initial perchlorate dose in experiments conducted in sealed hydroponic bioreactors with low DO and little or no nitrate N. Meanwhile, the contribution of rhizodegradation decreased to 76 ± 14% (±95% CI) when nitrate (a competing terminal electron acceptor) was provided as the nitrogen source. Slower rates of phytoremediation by uptake and phytodegradation were observed under high nitrate concentrations and aerobic conditions, which allowed perchlorate to persist in solution and resulted in a higher fraction uptake by the plant. Specifically, the rate of removal of perchlorate from bulk solution ranged from 5.4 ± 0.54 to 37.1 ± 2.25 mg/L/d (±SE) in the absence of nitrate to 1.78 ± 0.27 to 0.46 ± 0.02 mg/L/d (±SE) at high nitrate concentration. The results of this study indicate that the root-zone environment of plants can be manipulated to optimize rhizodegradation and to minimize undesirable processes such as uptake, temporal phytoaccumulation, and slow phytodegradation during phytoremediation of perchlorate. Rhizodegradation is desired because contaminants resident in plant tissue may remain an ecological risk until completely phytodegraded.
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