首页> 美国卫生研究院文献>Applied and Environmental Microbiology >Microbial degradation and humification of the lawn care pesticide 24-dichlorophenoxyacetic acid during the composting of yard trimmings.
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Microbial degradation and humification of the lawn care pesticide 24-dichlorophenoxyacetic acid during the composting of yard trimmings.

机译:庭院堆肥过程中草坪护理农药24-二氯苯氧基乙酸的微生物降解和腐殖化作用。

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摘要

The fate of the widely used lawn care herbicide 2,4-dichlorophenoxyacetic acid (2,4-D) during the composting of yard trimmings consisting of primarily leaves and grass is an important unexplored question. In this study, we determined the extent of 2,4-D mineralization, incorporation into humic matter, volatilization, and sorption during the composting of yard trimmings. Yard trimmings (2:1 [wt/wt] leaves-grass) were amended with 14C-ring-labeled 2,4-D (17 mg/kg of dry weight) and composted in a temperature-controlled laboratory scale compost system. During composting, thermophilic microbes were numerically dominant, reaching a maximum of 2 x 10(11)/g. At the end of composting, 46% of the organic matter (OM) present in the yard trimmings was lost and the compost was stable, with an oxygen uptake rate of 0.09 mg of O2 per g of OM per h, and was well humified (humification index, 0.39). Mineralization of the OM temporally paralleled mineralization of 2,4-D. In the final compost, 47% of the added 2,4-D carbon was mineralized, about 23% was complexed with high-molecular-weight humic acids, and about 20% was not extractable (humin fraction). Less than 1% of the added 14C was present in water expressed from the finished compost, suggesting a low potential for leaching of 2,4-D. Very little volatilization of 2,4-D occurred during composting. It is of interest that our results indicate active mineralization of 2,4-D at composting temperatures of 60 degrees C because microbial 2,4-D degradation at thermophilic temperatures has not been previously documented.
机译:在主要由树叶和草组成的院子装饰堆肥过程中,广泛使用的草坪护理除草剂2,4-二氯苯氧基乙酸(2,4-D)的命运是一个尚未探索的重要问题。在这项研究中,我们确定了堆场装饰物堆肥过程中2,4-D矿化的程度,掺入腐殖质,挥发和吸收的程度。用14C环标记的2,4-D(17 mg / kg干重)修正围场装饰物(2:1 [wt / wt]的草叶),并在温度控制的实验室规模的堆肥系统中堆肥。在堆肥过程中,嗜热微生物在数量上占优势,最高可达2 x 10(11)/ g。在堆肥结束时,堆场装饰物中存在的有机物(OM)损失了46%,堆肥稳定,每g OM每小时的摄氧量为0.09 mg O2,并且被很好地腐化(谦卑指数0.39)。 OM的矿化作用在时间上与2,4-D的矿化作用平行。在最终堆肥中,添加的2,4-D碳中有47%被矿化,约23%与高分子量腐殖酸络合,约20%不可提取(腐殖质分数)。不到14%的添加14C存在于最终堆肥表达的水中,这表明2,4-D浸出的可能性很低。堆肥过程中2,4-D的挥发很少。有趣的是,我们的结果表明,在60摄氏度的堆肥温度下2,4-D会主动矿化,因为以前没有文献记载在高温下微生物2,4-D降解。

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