Department of Integrative Biology, University of Texas at San Antonio, San Antonio, Texas, USA.
Microbiol Spectr. 2024 Nov 5;12(11):e0424623. doi: 10.1128/spectrum.04246-23. Epub 2024 Sep 30.
Wastewater discharge is a global threat to freshwater resources. Streams, in particular, are receiving waterbodies that are directly impacted chemically and biologically due to effluent discharge. However, it is largely unknown how wastewater serves as a subsidy or a stressor to aquatic biodiversity, particularly microbiota, over space. Nutrient-diffusing substrata (NDS) were deployed; NDS release nutrients through diffusion into the water column into a wastewater-dependent stream across three reaches. We used N, P, and N + P treatments for the measurement of single nutrient and co-nutrient limitation, and a no-nutrient control. Both algal and total biofilm biomass was measured and the 16S ribosomal RNA genes via targeted amplicon sequencing was used to assess bacterial/archaeal community diversity. Data indicated that total organic matter in biofilms differs spatially with the greatest organic matter (OM) concentrations in the confluence downstream of wastewater inputs. Biofilm OM concentrations were greatest in P and N + P treatments in the confluence site relative to control or N-only treatments. This indicates heterotrophic microbial communities-likely bacteria that dominate stream biofilms-are P-limited in this ecosystem even with upstream wastewater inputs. In conjunction, bacteria/archaeal communities differed the greatest among nutrient treatments versus spatially and had several indicator taxa belonging to spp. in N treatments relative to controls. Collectively with historical water quality data, we conclude that this wastewater-fed stream is primarily N-enriched but potentially P-limited, which results in significant shifts in biofilm bacterial communities and likely their overall biomass in this urban watershed.
Streams in arid and semi-arid biomes are often dependent on their flow from municipal sources, such as wastewater effluent. However, wastewater has been shown to contain high concentrations of nutrients and chemical pollutants that can potentially harm aquatic ecosystems and their biota. Understanding if and the type of microorganisms that respond to pollution sources, specifically effluent from wastewater treatment facilities, in regions where flow is predominantly from treatment facilities, is critical for developing a predictive monitoring approach for eutrophication or other ecological degradation states for freshwaters.
废水排放是对淡水资源的全球性威胁。溪流尤其受到影响,因为废水中的化学物质和生物物质会直接流入溪流。然而,人们对废水如何成为水生生物多样性(尤其是微生物群落)的补贴或胁迫源,在空间上还知之甚少。我们部署了营养扩散基质(NDS);NDS 通过扩散将营养物质释放到水柱中,进入一条依赖废水的溪流的三个河段。我们使用 N、P 和 N + P 处理来测量单一养分和共养分限制,并设置无养分对照。我们测量了藻类和总生物膜生物量,并通过靶向扩增子测序来评估细菌/古菌群落多样性。数据表明,生物膜中的总有机物质在空间上有所不同,在废水输入下游的汇流处有机物质浓度最大。与对照或仅 N 处理相比,在汇流处,生物膜中的有机物质浓度在 P 和 N + P 处理中最高。这表明,即使有上游废水输入,该生态系统中以异养微生物为主的溪流生物膜中的微生物群落可能受到磷的限制。同时,与空间相比,细菌/古菌群落在养分处理之间的差异最大,并且在 N 处理中相对于对照有几个属于 spp.的指示类群。结合历史水质数据,我们得出结论,这条受废水影响的溪流主要富含有机氮,但可能受到磷的限制,这导致生物膜细菌群落发生重大变化,并可能导致其在这个城市流域中的总体生物量发生变化。
在干旱和半干旱生物群系中,溪流通常依赖于来自城市水源的流量,例如废水。然而,已经表明,废水中含有高浓度的营养物质和化学污染物,这些物质可能会对水生生态系统及其生物区系造成伤害。了解在以处理设施为主的水流地区,哪些微生物对污染来源(特别是来自废水处理设施的废水)做出响应,以及响应的类型,对于开发一种预测性监测方法来监测富营养化或其他淡水生态退化状态至关重要。