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The interaction between abiotic photodegradation and microbial decomposition under ultraviolet radiation

机译:紫外线辐射下非生物光降解与微生物分解之间的相互作用

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Elevated ultraviolet (UV) radiation has been demonstrated to stimulate litter decomposition. Despite years of research, it is still not fully understood whether the acceleration in litter degradation is primarily attributed to abiotic photodegradation or the combined effects of abiotic photodegradation and microbial decomposition. In this study, we used meta-analysis to synthesize photodegradation studies and compared the effects of UV radiation on litter decomposition between abiotic and biotic conditions. We also conducted a microcosm experiment to assess the effects of UV radiation on litter biodegradability and microbial activity. Overall, our meta-analysis found that under abiotic photodegradation, UV radiation reduced the remaining litter mass by 1.44% (95% CI: 0.85% to 2.08%), did not affect the remaining lignin and increased the dissolved organic carbon (DOC) concentration by 14.01% (1.49-23.67%). Under combined abiotic photodegradation and microbial decomposition, UV radiation reduced the remaining litter mass and lignin by 1.60% (0.04-3.58%) and 16.07% (9.27-24.23%), respectively, but did not alter DOC concentration. UV radiation had no significant impact on soil microbial biomass carbon (MBC), but it reduced microbial respiration by 44.91% (2.26-78.62%) and altered the composition of the microbial community. In addition, UV radiation reduced nitrogen (N) immobilization by 19.44% (4.77-37.92%). Our microcosm experiment further indicated that DOC concentration and the amount of respired C in UV-treated litter increased with UV exposure time, suggesting that longer UV exposure resulted in greater biodegradability. Overall, our study suggested that UV exposure could increase litter biodegradability by increasing the microbial accessibility of lignin, as well as the labile carbon supply to microbes. However, the remaining litter mass was not different between the abiotic and biotic conditions, most likely because the positive effect of UV radiation on litter biodegradability was offset by its negative effect on microbial activity. Our results also suggested that UV radiation could alter the N cycle during decomposition, primarily by inhibiting N immobilization.
机译:紫外线(UV)辐射升高已证明可促进垃圾分解。尽管进行了多年的研究,但垫料降解的加速是主要归因于非生物光降解还是非生物光降解与微生物分解的综合作用,仍然尚不完全清楚。在这项研究中,我们使用荟萃分析来合成光降解研究,并比较了紫外线辐射对非生物和生物条件下垫料分解的影响。我们还进行了微观实验,以评估紫外线辐射对垃圾可降解性和微生物活性的影响。总体而言,我们的荟萃分析发现,在非生物光降解下,紫外线辐射使残留的垃圾质量降低了1.44%(95%CI:0.85%至2.08%),不影响残留的木质素并增加了可溶性有机碳(DOC)浓度减少了14.01%(1.49-23.67%)。在非生物光降解和微生物分解的综合作用下,紫外线辐射分别使剩余的凋落物质量和木质素减少了1.60%(0.04-3.58%)和16.07%(9.27-24.23%),但没有改变DOC的浓度。紫外线辐射对土壤微生物生物量碳(MBC)没有显着影响,但它使微生物呼吸减少了44.91%(2.26-78.62%),并改变了微生物群落的组成。此外,紫外线辐射使固氮(N)降低了19.44%(4.77-37.92%)。我们的缩影实验进一步表明,紫外线处理的垃圾中的DOC浓度和呼吸C的含量随紫外线暴露时间的增加而增加,表明更长的紫外线暴露导致更大的生物降解性。总体而言,我们的研究表明,紫外线暴露可以通过增加木质素的微生物可及性以及对微生物的不稳定碳供应来提高垃圾的生物降解性。但是,剩余的垃圾质量在非生物和生物条件之间没有差异,这很可能是因为紫外线辐射对垃圾生物降解性的正面影响被其对微生物活性的负面影响所抵消。我们的研究结果还表明,紫外线辐射可主要通过抑制固氮作用来改变分解过程中的氮循环。

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