有机添加剂对苯酚氧化酶、过氧化物酶、脲酶和氮矿化的影响:一项实验室培养研究

Emma E. Leaseburg, Li-guo Lei, L. Fink
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引用次数: 0

摘要

减缓气候变化和提高农业系统肥力需要采用更可持续的肥料管理做法。利用再生有机材料,如动物和绿色废物,可以通过改变细胞外酶活性来促进土壤碳稳定,同时为植物生长提供必要的氮(N)。本研究的目的是量化堆肥类型(牛粪、绿肥、不同比例的绿肥和牛粪混合物以及无机肥料)对(1)酶活性(酚氧化酶、过氧化物酶和脲酶)和(2)矿化氮在30°C实验室孵育下为期8周的影响。50%牛粪与50%绿肥混合处理(2.45 μmol h−1 g−1)和30%牛粪与70%绿肥混合处理(3.21 μmol h−1 g−1)的土壤氧化酶(酚氧化酶和过氧化物酶)活性最低。绿肥处理的土壤酚氧化酶活性最高(3.52 μmol h−1 g−1),70%牛粪+ 30%绿肥处理的土壤过氧化物酶活性最高(5.68 μmol h−1 g−1)。各有机肥处理土壤总净矿化氮含量差异不显著,但显著低于无机肥处理土壤总净矿化氮含量。这些结果表明,有机改良剂和混合改良剂在提供植物速效氮方面的作用相似,但对木质素降解酶活性的影响不同,这可能导致土壤有机碳循环和长期碳储量的差异,这取决于使用哪种有机改良剂。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Effects of Organic Amendments on Phenol Oxidase, Peroxidase, Urease, and Nitrogen Mineralization: A Laboratory Incubation Study
Mitigating climate change and enhancing fertility in agricultural systems require the adoption of more sustainable fertilizer management practices. Applications of recycled organic materials, such as animal and green wastes, can promote soil carbon stabilization via changing extracellular enzyme activities while providing the necessary nitrogen (N) for plant growth. The goals of this study were to quantify the effects of compost type (cow manure, green manures, mixtures of green and cow manure at various proportions, and inorganic fertilizers) on (1) enzyme activity (phenol oxidase, peroxidase, and urease), and (2) mineralized N under laboratory incubation at 30 °C over an eight-week period. The lowest oxidative enzyme activities (phenol oxidase and peroxidase) were found in the soil treated with a mixture of 50% cow manure and 50% green manure (2.45 μmol h−1 g−1) and a mixture of 30% cow manure and 70% green manure (3.21 μmol h−1 g−1) compared to all other fertilizer treatments. The highest phenol oxidase activity was found in soils amended with green manures (3.52 μmol h−1 g−1), while the highest peroxidase activity was found in soils amended with a mixture of 70% cow manure and 30% green manure (5.68 μmol h−1 g−1). No significant differences were found in total net mineralized N content among all organic fertilizer treatments, but these were significantly lower than total net mineralized N in soil treated with inorganic fertilizers. These results indicate similar effects of organic amendments and mixtures in providing plant-available N, but different effects on lignin-degrading enzyme activities, which may lead to differences in soil organic carbon cycling and long-term C storage depending on which organic amendment is utilized.
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