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Promotion of oil hydrocarbon degradation in fine-grained marsh soils under aerobic and denitrifying conditions

机译:在好氧和反硝化条件下促进细粒沼泽土壤中石油烃的降解

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The goal of the laboratory studies was to prove oil hydrocarbon degradation in fine-grained inarsh soils under denitrifying conditions and to compare it with the degradation under aerobic conditions. In order to accelerate the bioremediation processin soils with redox potentials < + 200 mV (pH 7) the use of different additives and oxidizing agents was tested. Fine-grained soil materials from marsh soils was treated with KNO_3, fertilizers or a mixture of both for the hydrocarhon degradation underanoxic denitrifying conditions as well as the addition of hydrogen peroxide or an oil binder to improve the soil structure to promote aerobic hydrocarbon degradation. During the incubation period, soil respiration (CO_2-production) was measured nearly every day, the content of hydrocarbons as well as the number of microbial hydrocarbon degraders (aerobic, anaerobic), NH_4~+-N, NO_3~--N and total N was measured at the beginlfing of the test and after two and four weeks. There were several indicators forthe hydrocarbon degradation under denitrifying conditions: high denitrification rates, an increase in colonization with denitrifying bacteria, higher respiratory quotients and higher degradation rates compared to the reference. At the end of the test period the oil binder treated soil had the highest degradation rate, but there were severe differences in the degradation rate between the first and second fortnight of all treatments. Our investigation suggests that combined KNO_3 and fertilizer treatmentis the most promising treatment to accelerate biological hydrocarbon degradation in fine-grained inarsh soils and should be tested in the near future in biopiles.
机译:实验室研究的目的是要证明反硝化条件下细粒inarsh土壤中石油烃的降解,并将其与有氧条件下的降解进行比较。为了加速氧化还原电位<+ 200 mV(pH 7)的土壤中的生物修复过程,测试了使用不同的添加剂和氧化剂。用KNO_3,肥料或二者的混合物处理沼泽土壤中的细粒土壤材料,以在缺氧反硝化条件下进行水碳素降解,并添加过氧化氢或油性粘合剂以改善土壤结构,促进好氧碳氢化合物的降解。在孵化期间,几乎每天都要测量土壤呼吸(CO_2的产生),碳氢化合物的含量以及微生物碳氢降解物(好氧,厌氧),NH_4〜+ -N,NO_3〜--N和总微生物的数量。在测试开始时以及两到四个星期后测量N。与参考相比,反硝化条件下碳氢化合物的降解有几个指标:反硝化率高,反硝化细菌定植增加,呼吸商更高和降解率更高。在测试期结束时,经油粘合剂处理的土壤降解速率最高,但是在所有处理的第一个和第二个两周之间,降解速率存在严重差异。我们的研究表明,将KNO_3和肥料处理相结合是最有希望的处理方法,可以促进细粒不肥土壤中生物碳氢化合物的降解,并应在不久的将来在生物堆中进行测试。

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