Abstract

Abstract. The invasion of aquifer microbial communities by aboveground microorganisms, a phenomenon known as community coalescence, is likely to be exacerbated in groundwaters fed by stormwater infiltration systems (SISs). Here, the incidence of this increased connectivity with upslope soils and impermeabilized surfaces was assessed through a meta-analysis of 16S rRNA gene libraries. Specifically, DNA sequences encoding 16S rRNA V5-V6 regions from free-living and attached aquifer bacteria (i.e., water and biofilm samples) were analysed upstream and downstream of a SIS and compared with those from bacterial communities from watershed runoffs and surface sediments from the SIS detention and infiltration basins. Significant bacterial transfers were inferred by the SourceTracker Bayesian approach, with 23 % to 57 % of the aquifer bacterial biofilms being composed of taxa from aboveground sediments and urban runoffs. Sediments from the detention basin were found more significant contributors of taxa involved in the buildup of these biofilms than soils from the infiltration basin. Inferred taxa among the coalesced biofilm community were predicted to be high in hydrocarbon degraders such as Sphingobium and Nocardia. The 16S rRNA-based bacterial community structure of the downstream-SIS aquifer waters showed lower coalescence with aboveground taxa (8 % to 38 %) than those of biofilms and higher numbers of taxa predicted to be involved in the N and S cycles. A DNA marker named tpm enabled the tracking of bacterial species from 24 genera including Pseudomonas, Aeromonas and Xanthomonas, among these communities. Several tpm sequence types were found to be shared between the aboveground and aquifer samples. Reads related to Pseudomonas were allocated to 50 species, of which 16 were found in the aquifer samples. Several of these aquifer species were found to be involved in denitrification but also hydrocarbon degradation (P. aeruginosa, P. putida and P. fluorescens). Some tpm sequence types allocated to P. umsongensis and P. chengduensis were found to be enriched among the tpm-harbouring bacteria, respectively, of the aquifer biofilms and waters. Reads related to Aeromonas were allocated to 11 species, but only those from A. caviae were recovered aboveground and in the aquifer samples. Some tpm sequence types of the X. axonopodis phytopathogen were recorded in higher proportions among the tpm-harbouring bacteria of the aquifer waters than in the aboveground samples. A significant coalescence of microbial communities from an urban watershed with those of an aquifer was thus observed, and recent aquifer biofilms were found to be significantly colonized by runoff-opportunistic taxa able to use urban C sources from aboveground compartments.

Highlights

  • Urbanization exerts multiple pressures on natural habitats and on aquatic environments (Konrad and Booth, 2005; McGrane, 2016; Mejía and Moglen, 2009)

  • Bacterial communities were dominated by Proteobacteria, Bacteroidetes and Actinobacteria (WS = 95 % of total reads, detention basin (DB) = 84 %, infiltration basin (IB) = 71 %, AQ_bio = 99 %; aquifer waters (AQ_wat) = 59 %), but 10 other phyla with relative abundances greater than 0.5 % were detected (Fig. 2a and Table S4)

  • Alphadiversity estimates showed that aquifer samples harboured a microbiome with a significantly lower richness (AQ_bio: Sobs = 278 OTUs ±106; AQ_wat: Sobs = 490 OTUs ±333) and a less diverse bacterial community (AQ_bio: H’ = 2.9 ± 0.3 and AQ_wat: H’ = 4.3 ± 0.7) than the ones of the upper compartments (Sobs−WS = 1288 OTUs ±232; Sobs−DB = 1566 OTUs ±245, Sobs−IB = 1503 OTUs ±177 and H’WS = 5.0 ± 0.5; H’DB = 5.4 ± 0.5 and H’IB = 5.7 ± 0.4) (ANOVA, p

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Summary

Introduction

Urbanization exerts multiple pressures on natural habitats and on aquatic environments (Konrad and Booth, 2005; McGrane, 2016; Mejía and Moglen, 2009). The densification of urban areas, combined with the conversion of agricultural and natural lands into urban land use, led to the replacement of vegetation and open fields by impervious urban structures (i.e., roads, rooftops, sidewalks and parking lots) (Barnes et al, 2001) These impervious structures reduce the infiltration capacity of soils. They exacerbate the speed and volume of stormwater runoff that favour soil erosion and flooding events and affect adversely natural groundwater recharge processes (Booth, 1991; Shuster et al, 2005) Due to these consequences, stormwater infiltration systems (SISs) or managed aquifer recharge (MAR) systems have been developed over the last decades and are gaining more interest in developed countries (Pitt et al, 1999). Stormwater represents a major source of nonpoint pollution, and its infiltration into the ground may have adverse ecological and sanitary impacts (Chong et al, 2013; Pitt et al, 1999; Vezzaro and Mikkelsen, 2012)

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