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Effects of biochar and wood pellets amendments added to landfill cover soil on microbial methane oxidation: A laboratory column study

机译:垃圾填埋场覆盖土壤中添加的生物炭和木屑颗粒改良剂对微生物甲烷氧化的影响:一项实验室专栏研究

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Alternate landfill covers designed to enhance microbial methane (CH_4) oxidation and reduce the negative impacts of landfill gas emissions on global climate have recently been proposed and investigated. In this study, the use of biochar as a soil amendment is examined in order to assess the feasibility and effectiveness for enhanced CH_4 removal in landfill covers when incorporated under high compaction conditions and relatively low soil moisture. Four different cover configurations were tested in large soil columns for -510 days and potential CH_4 oxidation rates were determined following long-term incubation in small batch assays. Cover designs tested include: a thin biochar layer at 15-18 cm; 2% mixed soil-biochar layer at 20-40 cm; 2% mixed soil-uncharred wood pellets at 20-40 cm; and soil obtained from intermediate cover at an active landfill site. The placement of a thin biochar layer in the cover significantly impacted moisture distribution and infiltration, which in turn affected CH_4 oxidation potential with depth. An increase in CH_4 removal rates was observed among all columns over the 500 day incubation period, with steady-state CH_4 removal efficiencies ranging from ~60 to 90% in the final stages of incubation (inlet load ~80 g CH_4 m~(-2) d~(-1)). The thin biochar layer had the lowest average removal efficiency as a result of reduced moisture availability below the biochar layer. The addition of 2% biochar to soil yielded similar CH_4 oxidation rates in terminal assays as the 2% uncharred wood pellet amendment. CH_4 oxidation rates in terminal assays were positively correlated with soil moisture, which was affected by the materials' water holding capacity. The high water holding capacity of biochar led to higher oxidation rates within the thin biochar layer, supporting the initial hypothesis that biochar may confer more favorable physical conditions for methanotrophy. Ultimate performance was apparently affected by soil type and CH_4 exposure history, with the highest oxidation rates observed in the un-amended field soil with higher initial methanotrophic activity.
机译:最近已提出并研究了旨在提高微生物甲烷(CH_4)氧化并减少垃圾填埋气体排放对全球气候的负面影响的替代垃圾填埋场。在这项研究中,研究了使用生物炭作为土壤改良剂,以评估在高压实条件下和相对较低的土壤湿度下掺入掩埋物中提高CH_4去除率的可行性和有效性。在大土壤柱中测试了四种不同的覆盖结构-510天,并在小批量试验中长期孵育后确定了潜在的CH_4氧化速率。测试的覆盖层设计包括:15-18厘米薄的生物炭层;在20-40厘米处混合2%的土壤-生物炭层;在20-40厘米处混合2%的未烧土的木质颗粒;以及从活跃填埋场的中间覆盖层获得的土壤。覆盖物中薄薄的生物炭层的放置会显着影响水分分布和渗透,继而影响深度的CH_4氧化电位。在500天的温育期内,所有色谱柱的CH_4去除率都有所增加,在培养的最后阶段,稳态CH_4的去除效率在〜60%到90%之间(进样量〜80 g CH_4 m〜(-2 )d〜(-1))。薄的生物炭层具有最低的平均去除效率,这是因为生物炭层下方的水分供应减少。在最终分析中,向土壤中添加2%的生物炭产生的CH_4氧化速率与2%的未烧木屑颗粒修正剂相似。最终测定中的CH_4氧化速率与土壤水分呈正相关,而土壤水分受材料的持水量影响。生物炭的高持水能力导致薄生物炭层内较高的氧化速率,支持了生物炭可能为甲烷氧化提供更有利物理条件的最初假设。最终性能显然受到土壤类型和CH_4暴露历史的影响,在未改良的田间土壤中观察到最高的氧化速率,其初始甲烷氧化活性较高。

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