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首页> 外文期刊>Soil & Sediment Contamination >Biostimulation and phytoremediation treatment strategies of gasoline-nickel co-contaminated soil.
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Biostimulation and phytoremediation treatment strategies of gasoline-nickel co-contaminated soil.

机译:汽油-镍共污染土壤的生物刺激和植物修复处理策略。

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This study investigated the potential effect of poultry dung (biostimulation) and stubborn grass (Sporobolus pyramidalis) (phytoremediation) on microbial biodegradation of gasoline and nickel uptake in gasoline-nickel-impacted soil. In addition, the potential stimulatory effects of nickel on hydrocarbon utilization were investigated over a small range of nickel concentrations (2.5-12.5 mg/kg). The results showed that an increase in nickel concentration increased hydrocarbon degraders in soil by a range of 8.4-17.2% and resulted in a relative increase in gasoline biodegradation (57.5-62.4%). Also, under aerobic conditions, total petroleum hydrocarbons' (TPH) removal was 62.4% in the natural gasoline-nickel microcosm (natural attenuation), and a maximum of 78.5%, 85.7%, and 95.8% TPH removal was obtained in phytoremediation, biostimulation, and a combination of biostimulation- and phytoremediation-treated microcosms, respectively. First-order kinetics described the biodegradation of gasoline and nickel uptake very well. Half-life times obtained were 28.88, 18.24, 14.44, and 8.56 days for gasoline degradation under natural attenuation, phytoremediation, biostimulation, and combined biostimulation and phytoremediation treatment methods, respectively. The results indicate that these remediation methods have promising potential for effective remediation of soils co-contaminated with petroleum hydrocarbons and heavy metals.
机译:这项研究调查了家禽粪便(生物刺激)和顽固的草(Sporobolus pyramidalis)(植物修复)对汽油-镍影响土壤中汽油和镍吸收的微生物生物降解的潜在影响。此外,还研究了镍在很小的镍浓度范围内(2.5-12.5 mg / kg)对碳氢化合物利用的潜在刺激作用。结果表明,镍浓度的增加使土壤中的碳氢化合物降解量增加了8.4-17.2%,并导致汽油生物降解相对增加(57.5-62.4%)。同样,在有氧条件下,天然汽油-镍缩影(自然衰减)中的总石油烃(TPH)去除率为62.4%,在植物修复,生物刺激中TPH去除率最高为78.5%,85.7%和95.8%。 ,以及经过生物刺激处理和植物修复处理的微观世界的组合。一级动力学很好地描述了汽油和镍吸收的生物降解。在自然衰减,植物修复,生物刺激以及生物刺激和植物修复联合处理方法下,汽油降解的半衰期分别为28.88、18.24、14.44和8.56天。结果表明,这些修复方法具有有效修复被石油烃和重金属共同污染的土壤的潜力。

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