Wirsching Johannes, Pagel Holger, Ditterich Franziska, Uksa Marie, Werneburg Martina, Zwiener Christian, Berner Doreen, Kandeler Ellen, Poll Christian
Department of Soil Biology, Institute of Soil Science and Land Evaluation, University of Hohenheim, Stuttgart, Germany.
Department of Soil Physics, Institute of Soil Science and Land Evaluation, University of Hohenheim, Stuttgart, Germany.
Front Microbiol. 2020 Aug 27;11:2107. doi: 10.3389/fmicb.2020.02107. eCollection 2020.
The objective of our study was to test whether limited microbial degradation at low pesticide concentrations could explain the discrepancy between overall degradability demonstrated in laboratory tests and their actual persistence in the environment. Studies on pesticide degradation are often performed using unrealistically high application rates seldom found in natural environments. Nevertheless, biodegradation rates determined for higher pesticide doses cannot necessarily be extrapolated to lower concentrations. In this context, we wanted to (i) compare the kinetics of pesticide degradation at different concentrations in arable land and (ii) clarify whether there is a concentration threshold below which the expression of the functional genes involved in the degradation pathway is inhibited without further pesticide degradation taking place. We set up an incubation experiment for four weeks using 14C-ring labeled 2-methyl-4-chlorophenoxyacetic acid (MCPA) as a model compound in concentrations from 30 to 20,000 μg kg soil. To quantify the abundance of putative microorganisms involved in MCPA degradation and their degradation activity, tfdA gene copy numbers (DNA) and transcripts (mRNA) were determined by quantitative real-time PCR. Mineralization dynamics of MCPA derived-C were analyzed by monitoring 14CO production and 14C assimilation by soil microorganisms. We identified two different concentration thresholds for growth and activity with respect to MCPA degradation using tfdA gene and mRNA transcript abundance as growth and activity indices, respectively. The tfdA gene expression started to increase between 1,000 and 5,000 μg MCPA kg dry soil, but an actual increase in tfdA sequences could only be determined at a concentration of 20,000 μg. Accordingly, we observed a clear shift from catabolic to anabolic utilization of MCPA-derived C in the concentration range of 1,000 to 5,000 μg kg. Concentrations ≥1,000 μg kg were mainly associated with delayed mineralization, while concentrations ≤1,000 μg kg showed rapid absolute dissipation. The persistence of pesticides at low concentrations cannot, therefore, be explained by the absence of functional gene expression. Nevertheless, significant differences in the degradation kinetics of MCPA between low and high pesticide concentrations illustrate the need for studies investigating pesticide degradation at environmentally relevant concentrations.
我们研究的目的是检验在低农药浓度下微生物降解受限是否能解释实验室测试中显示的总体可降解性与其在环境中的实际持久性之间的差异。农药降解研究通常使用自然环境中很少出现的高得离谱的施用量。然而,针对较高农药剂量测定的生物降解率不一定能外推至较低浓度。在此背景下,我们希望:(i)比较耕地中不同浓度下农药降解的动力学;(ii)阐明是否存在一个浓度阈值,低于该阈值,降解途径中涉及的功能基因的表达会受到抑制,且不会发生进一步的农药降解。我们以14C环标记的2-甲基-4-氯苯氧乙酸(MCPA)作为模型化合物,在土壤浓度为30至20,000μg/kg的条件下进行了为期四周的培养实验。为了量化参与MCPA降解的假定微生物的丰度及其降解活性,通过定量实时PCR测定了tfdA基因拷贝数(DNA)和转录本(mRNA)。通过监测土壤微生物产生的14CO2和同化的14C来分析MCPA衍生碳的矿化动态。我们分别以tfdA基因和mRNA转录本丰度作为生长和活性指标,确定了关于MCPA降解的生长和活性的两个不同浓度阈值。tfdA基因表达在1,000至5,000μg MCPA/kg干土之间开始增加,但只有在浓度为20,000μg时才能确定tfdA序列的实际增加。因此,我们观察到在1,000至5,000μg/kg的浓度范围内,MCPA衍生碳从分解代谢利用向合成代谢利用发生了明显转变。浓度≥1,000μg/kg主要与矿化延迟相关,而浓度≤1,000μg/kg则显示出快速的绝对消散。因此,低浓度农药的持久性不能用功能基因表达缺失来解释。然而,低农药浓度和高农药浓度下MCPA降解动力学的显著差异表明,需要开展在环境相关浓度下研究农药降解的工作。