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暴露于敌草胺的土壤中微生物特性和群落结构的改变。

Alteration of microbial properties and community structure in soils exposed to napropamide.

作者信息

Guo Hua, Chen Guofeng, Lv Zhaoping, Zhao Hua, Yang Hong

机构信息

Department of Applied Chemistry, College of Science, Nanjing Agricultural University, Nanjing 210095, China.

出版信息

J Environ Sci (China). 2009;21(4):494-502. doi: 10.1016/s1001-0742(08)62298-6.

DOI:10.1016/s1001-0742(08)62298-6
PMID:19634425
Abstract

The effect of pesticide napropamide (N,N-diethyl-2-(1-naphthalenyloxy) propanamide) on soil microorganisms for long-term (56 d) was assessed by monitoring changes in soil microbial biological responses. Soils were treated with napropamide at 0, 2, 10, 20, 40, and 80 mg/kg soil and sampled at intervals of 1, 3, 7, 14, 28, 42, and 56 d. The average microbial biomass C declined in napropamide-treated soils as compared to control. The same trend was observed on microbial biomass N after napropamide application. We also determined the basal soil respiration (BSR) and observed a high level in soils treated with napropamide during the first 7 d of experiment. But with the passage of incubation time, BSR with napropamide decreased relatively to control. Application of napropamide at 2-80 mg/kg soil had inhibitory effects on the activity of urease and invertase. Activity of catalase was enhanced during the initial 7 d of napropamide application, but soon recovered to the basal level. The depressed enzyme activities might be due to the toxicity of napropamide to the soil microbial populations. To further understand the effect of napropamide on microbial communities, a PCR-DGGE-based experiment and cluster analysis of 16S rDNA community profiles were performed. Our analysis revealed an apparent difference in bacterial-community composition between the napropamide treatments and control. Addition of napropamide apparently increased the number of bands during the 7-14 d of incubation. These results imply that napropamide-induced toxicity was responsible for the disturbance of the microbial populations in soil.

摘要

通过监测土壤微生物生物学响应的变化,评估了农药敌草胺(N,N-二乙基-2-(1-萘氧基)丙酰胺)对土壤微生物的长期(56天)影响。土壤分别用0、2、10、20、40和80毫克/千克土壤的敌草胺处理,并在1、3、7、14、28、42和56天的间隔时间取样。与对照相比,敌草胺处理的土壤中微生物生物量碳平均下降。施用敌草胺后,微生物生物量氮也观察到相同趋势。我们还测定了基础土壤呼吸(BSR),并观察到在实验的前7天,敌草胺处理的土壤中基础土壤呼吸水平较高。但随着培养时间的推移,与对照相比,敌草胺处理的基础土壤呼吸相对下降。在2-80毫克/千克土壤中施用敌草胺对脲酶和转化酶的活性有抑制作用。在施用敌草胺的最初7天内,过氧化氢酶的活性增强,但很快恢复到基础水平。酶活性的降低可能是由于敌草胺对土壤微生物种群的毒性。为了进一步了解敌草胺对微生物群落的影响,进行了基于PCR-DGGE的实验和16S rDNA群落图谱的聚类分析。我们的分析揭示了敌草胺处理组和对照组之间细菌群落组成的明显差异。在培养的7-14天内,添加敌草胺明显增加了条带数量。这些结果表明,敌草胺诱导的毒性是土壤中微生物种群受到干扰的原因。

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