Département des Sciences Biologiques, Université de Montréal, Montreal, QC, Canada.
Groupe de Recherche Interuniversitaire en Limnologie et environnement aquatique (GRIL), Montreal, QC, Canada.
Mol Ecol. 2021 Oct;30(19):4771-4788. doi: 10.1111/mec.16100. Epub 2021 Aug 12.
Agricultural pollution with fertilizers and pesticides is a common disturbance to freshwater biodiversity. Bacterioplankton communities are at the base of aquatic food webs, but their responses to these potentially interacting stressors are rarely explored. To test the extent of resistance and resilience in bacterioplankton communities faced with agricultural stressors, we exposed freshwater mesocosms to single and combined gradients of two commonly used pesticides: the herbicide glyphosate (0-15 mg/L) and the neonicotinoid insecticide imidacloprid (0-60 μg/L), in high or low nutrient backgrounds. Over the 43-day experiment, we tracked variation in bacterial density with flow cytometry, carbon substrate use with Biolog EcoPlates, and taxonomic diversity and composition with environmental 16S rRNA gene amplicon sequencing. We show that only glyphosate (at the highest dose, 15 mg/L), but not imidacloprid, nutrients, or their interactions measurably changed community structure, favouring members of the Proteobacteria including the genus Agrobacterium. However, no change in carbon substrate use was detected throughout, suggesting functional redundancy despite taxonomic changes. We further show that communities are resilient at broad, but not fine taxonomic levels: 24 days after glyphosate application the precise amplicon sequence variants do not return, and tend to be replaced by phylogenetically close taxa. We conclude that high doses of glyphosate - but still within commonly acceptable regulatory guidelines - alter freshwater bacterioplankton by favouring a subset of higher taxonomic units (i.e., genus to phylum) that transiently thrive in the presence of glyphosate. Longer-term impacts of glyphosate at finer taxonomic resolution merit further investigation.
农业施肥和施药污染对淡水生物多样性是一种常见的干扰。细菌浮游生物群落是水生食物网的基础,但它们对这些潜在相互作用的胁迫的反应很少被探索。为了测试面对农业胁迫时细菌浮游生物群落的抗性和恢复力程度,我们将淡水中营养物背景高或低的微宇宙暴露于两种常用农药:除草剂草甘膦(0-15 mg/L)和新烟碱类杀虫剂噻虫啉(0-60 μg/L)的单一和组合梯度中。在 43 天的实验中,我们使用流式细胞术跟踪细菌密度的变化,使用 Biolog EcoPlates 跟踪碳底物的利用,使用环境 16S rRNA 基因扩增子测序跟踪分类多样性和组成。我们表明,只有草甘膦(在最高剂量 15 mg/L 时),而不是噻虫啉、营养物或它们的相互作用,可显著改变群落结构,有利于包括根瘤菌属在内的变形菌门成员。然而,整个过程中都没有检测到碳底物利用的变化,这表明尽管分类发生了变化,但存在功能冗余。我们进一步表明,群落具有广泛的恢复力,但在精细的分类水平上没有恢复力:草甘膦施用 24 天后,精确的扩增子序列变体不会恢复,并且往往被系统发育上相近的分类群所取代。我们的结论是,高剂量的草甘膦 - 但仍在可接受的监管指导范围内 - 通过有利于一组更高的分类单元(即属到门)来改变淡水细菌浮游生物,这些单元在草甘膦存在下暂时繁盛。需要进一步调查草甘膦在更精细的分类分辨率下的长期影响。