Department of Production Technology of Reservoir Fluids, Oil and Gas Institute - National Research Institute, 31-503, Krakow, ul. Lubicz 25 A, Poland.
Department of Production Technology of Reservoir Fluids, Oil and Gas Institute - National Research Institute, 31-503, Krakow, ul. Lubicz 25 A, Poland.
Ecotoxicol Environ Saf. 2020 May;194:110409. doi: 10.1016/j.ecoenv.2020.110409. Epub 2020 Mar 7.
Phytoremediation is a promising "green technique" used to purify contaminated soils. The performed phytoremediation experiments assisted by the fertilization process involving pots of F.arundinacea grown on soils with diverse concentrations and types of contaminations produced the following decreased percentages after 6 months: Pb (25.4-34.1%), Ni (18.7-23.8%), Cd (26.3-46.7%), TPH (49.4-60.1%). Primarily, TPH biodegradation was occurring as a result of basic bioremediation stimulated by adding optimal volumes of biogenic substances and corrections in the soil reaction, while phytoremediation improved this process by 17.4 - 23.1%. The highest drop in a range of 45.6 - 55.5% was recorded for the group of C-C hydrocarbons, with the lowest one for C-C, amounting to 9.1-17.4%. Translocation factor values were: TF<1 and ranged, respectively, for: Pb (0.46-0.53), Ni (0.29-0.33), and Cd (0.21-0.25), which indicate that heavy metals absorbed by Festuca arundinacea they mainly accumulated in the root of the tissue in descending order: Cd <Ni <Pb, showing poor metal translocation from roots to shoots. Co-occurrence of petroleum pollutants (TPH) in contaminated (Pb, Cd, Ni) soils results in reducing their contents in Festuca arundinacea roots. The process of phytoremediation of contaminated soil using F.arundinacea assisted with fertilization was monitored by means of toxicological tests: Microtox SPT (inhibition of the luminescence of V. fischeri), Ostracodtoxkit F (mortality, growth inhibition Heterocypris incongruens) and MARA (growth of 11 microorganisms) and Phytotoxkit F (germination assessment, inhibition root growth: Sorghum saccharatum, Lepidium sativum and Sinapis alba). The sensitivity of toxicological tests used was comparable and increased in the order: MARA<Ostracodtoxkit<Microtox. The performed phytotoxicity tests have indicated variable sensitivity of the tested plants on contaminants occurring in the studied soils, following the sequence: L. Sativum<S. saccharatum<S. alba. The obtained results indicate a decrease in soil toxicity during phytoremediation assisted by the fertilization process using Festuca arundinacea, which correlates with a decrease in the amount of harmful impurities contained in soils subjected to phytoremediation.
植物修复是一种有前途的“绿色技术”,用于净化受污染的土壤。通过施肥过程辅助进行的植物修复实验,在不同浓度和类型污染物的土壤中种植了芦苇盆,6 个月后产生了以下降低百分比:Pb(25.4-34.1%)、Ni(18.7-23.8%)、Cd(26.3-46.7%)、TPH(49.4-60.1%)。最初,由于添加最佳体积的生物物质和土壤反应校正刺激的基本生物修复,TPH 生物降解正在发生,而植物修复通过 17.4-23.1%改善了该过程。记录到范围为 45.6-55.5%的最高降幅是 C-C 碳氢化合物组,而 C-C 的最低降幅为 9.1-17.4%。迁移因子值为:TF<1,分别为:Pb(0.46-0.53)、Ni(0.29-0.33)和 Cd(0.21-0.25),这表明Festuca arundinacea 吸收的重金属主要积累在组织的根部,顺序为:Cd<Ni<Pb,表明重金属从根部向茎部的迁移能力差。受污染(Pb、Cd、Ni)土壤中石油污染物(TPH)的共存会降低其在芦苇根部的含量。使用施肥辅助的 F.arundinacea 对污染土壤进行植物修复的过程通过毒理学测试进行了监测:Microtox SPT(发光菌发光的抑制)、Ostracodtoxkit F(死亡率、生长抑制异形真哲水蚤)和 MARA(11 种微生物的生长)和 Phytotoxkit F(发芽评估,抑制根生长:高粱、生菜和荠)。使用的毒理学测试的灵敏度相当,按以下顺序增加:MARA<Ostracodtoxkit<Microtox。进行的植物毒性测试表明,受污染土壤中存在的污染物对测试植物的敏感性不同,顺序为:生菜<S. saccharatum<S. alba。获得的结果表明,在使用芦苇的施肥辅助植物修复过程中,土壤毒性降低,这与受植物修复的土壤中有害杂质含量的降低有关。