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Effect of activated carbon and biochars on the bioavailability of polycyclic aromatic hydrocarbons in different industrially contaminated soils

机译:活性炭和生物炭对不同工业污染土壤中多环芳烃生物利用度的影响

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摘要

Coal production negatively affects the environment by the emission of polycyclic aromatic hydrocarbons (PAHs). Two soils (KOK and KB) from a coking plant area was investigated and their total PAH concentration was 40 and 17 mg/kg for the sum (a) 16 US EPA PAHs, respectively. A third soil was sampled from a bitumen plant area and was characterized by 9 mg/kg a16 US EPA PAHs. To reduce the freely dissolved concentration (C-free) of the PAHs in the soil pore water, active carbon (AC) and two biochars pyrolysed from wheat straw (biochar-S) and willow (biochar-W) were added to the soils at 0.5-5 % (w/w), each. The AC performed best and reduced the C-free by 51-98 % already at the lowest dose. The biochars needed doses up to 2.5 % to significantly reduce the C-free by 44-86 % in the biochar-S and by 37-68 % in the biochar-W amended soils. The high black carbon (BC) content of up to 2.3 % in the Silesian soils competed with the sorption sites of the carbon amendments and the performance of the remediation was a consequence of the contaminant's source and the distribution between the BC and the AC/biochars. In contrast, the carbon amendment could best reduce the C-free in the Lublin soil where the BC content was normal (0.05 %). It is therefore crucial to know the contaminant's source and history of a sample/site to choose the appropriate carbon amendment not only for remediation success but also for economic reasons.
机译:煤炭生产会通过排放多环芳烃(PAHs)对环境造成负面影响。研究了来自焦化厂地区的两种土壤(KOK和KB),它们的总PAH浓度分别为(a)16种美国EPA PAHs,分别为40和17 mg / kg。从沥青种植区取样了第三种土壤,并以9 mg / kg a16 US EPA PAHs为特征。为了降低土壤孔隙水中多环芳烃的自由溶解浓度​​(无碳),向土壤中添加了活性炭(AC)和从麦秸(biochar-S)和柳树(biochar-W)热解的两种生物炭。每个0.5-5%(w / w)。 AC表现最佳,并且在最低剂量下已经将无C减少了51-98%。生物炭需要的剂量最高为2.5%,才能在生物炭S中显着减少无C的44-86%,在生物炭W改良的土壤中降低37-68%。在西里西亚土壤中高达2.3%的高黑碳(BC)含量与碳改良剂的吸附位相竞争,并且修复的性能是污染物来源以及BC和AC /生物炭之间分布的结果。相反,碳改性剂可以最好地降低BC含量正常(0.05%)的鲁布林土壤中的无C值。因此,至关重要的是要了解污染物的来源和样本/地点的历史,不仅要考虑到修复成功,还要出于经济原因,选择适当的碳修正。

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