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[Preprint]. 2021 Mar 26:2021.03.18.21253604. [Version 1] doi: 10.1101/2021.03.18.21253604

A rapid assessment of wastewater for genomic surveillance of SARS-CoV-2 variants at sewershed scale in Louisville, KY

J L Fuqua 1,2,*, EC Rouchka 3,4, S Waigel 5, K Sokoloski 2,6, D Chung 2,6, W Zacharias 5, M Zhang 7, J Chariker 3,4, D Talley 8, I Santisteban 1,2, A Varsani 9, S Moyer 10,11, R H Holm 12, R A Yeager 12,13, T Smith 12, A Bhatnagar 12
PMCID: PMC8010757  PMID: 33791725

Abstract

In this communication, we report on the genomic surveillance of SARS-CoV-2 using wastewater samples in Jefferson County, KY. In February 2021, we analyzed seven wastewater samples for SARS-CoV-2 genomic surveillance. Variants observed in smaller catchment areas, such as neighborhood manhole locations, were not necessarily consistent when compared to associated variant results in downstream treatment plants, suggesting catchment size or population could impact the ability to detect diversity.


The successful viral detection of severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2) RNA in wastewater at various pooled scales (14) and discovery in the USA of B.1.1.7, B.1.351 and P.1 variants (5), has led to an interest in developing reliable population-level wastewater viral genomic surveillance.

The diversity of SARS-CoV-2 sequences reported to be circulating in the USA, have been determined by sequencing clinical samples; however, these variants can also be surveilled by sequencing wastewater samples (69). As of March 2021, the variants of concern - B.1.1.7, B.1.351, and P.1 have been widely detected in clinical samples from 47 states in the USA. In Kentucky, only five clinical cases have been linked to the presence of these variants (5), which could indicate incomplete surveillance. Broadening the application of genomic surveillance using wastewater in the community could enhance SARS-CoV-2 variant population monitoring.

In this communication, we report on the genomic surveillance of SARS-CoV-2 using wastewater samples in Jefferson County, KY. Samples were collected from manholes and treatment facilities, covering populations of 8,000 to 350,000 people (Table 1). RNA isolated from wastewater samples was used to quantify SARS-CoV-2 and analyze the genetic variation through high-throughput sequencing (See Supplementary Methods). Bioinformatics approaches were used to rapidly identify single nucleotide genetic alterations, which were compared with known variants of interest and concern.

Table 1.

Summary of wastewater SARS-CoV-2 samples sequenced in this study, Louisville, KY

Sample ID Sewershed population Location N1 (Ct) Sequencing BWA Alignment Rate (%)
833 35,956 Street line manhole leading to Treatment Plant #3a 28 28.02
Treatment Plant #1 55,928 Treatment Plant 30 21.09
847 10,739 Street line manhole leading to Treatment Plant #2 29 15.08
849 35,956 Street line manhole leading to Treatment Plant #3a 28 12.61
884 46,659 Street line manhole leading to Treatment Plant #3a 29 23.98
891 8,071 Street line manhole leading to Treatment Plant #2 29 26.03
Treatment Plant #2 349,850 Treatment Plant 31 19.96
a

Treatment Plant #3 samples had SARS-CoV-2 was detected but were below the threshold for individual mutations for review.

In February 2021, we analyzed seven wastewater samples for SARS-CoV-2 genomic surveillance (Figure 1). We did not detect genetic variations indicative of any current variant of concern, beyond the widespread D614G spike protein mutation (Supplementary Methods Tables 25). In all samples, we identified at least four of ten mutations consistent with the presence of the variant of interest B.1.429, and one sample contained seven of ten mutations (Table 2). The B.1.429 variant was confirmed in patient samples in Kentucky in January 2021 (10), and a single patient in the study area was reported to be positive for B.1.1.7 on February 9, 2021 (11). With our current metrics we flagged sites 833, 891, and Treatment plant #2 for potential presence of variant B.1.429 (3/7 sites). Differences in the scale of sample pooling in the community revealed unanticipated inconsistencies in variant representation. Specifically, variants observed in smaller catchment areas, such as neighborhood manhole locations, were not observed in downstream treatment plants, suggesting catchment size or population could impact the ability to detect diversity.

Figure 1. Study sites within Louisville, KY.

Figure 1.

Distribution of the sewershed area, treatment plants and community locations, in Jefferson County with corresponding dates, sampled. SARS-CoV-2 was detected at all sites. Samples that contained at least 50% of the single amino acid mutations for a variant with a nucleotide frequency above a 5 % threshold for individual mutations are flagged for review. This relatively low threshold serves the purpose of identifying geographic (sewershed) areas for heightened public health surveillance. With our current metrics we flagged sites 833, 891, and Treatment plant #2 for potential presence of variant B.1.429.

Table 2.

Summary of B.1.429 specific mutation prevalence by sample

Ref Pos Gene/ORF Ref Allele Alt Allele Variant Desc 833 Treatment Plant #1 847 849 884 891 Treatment Plant #2
1059 ORF1ab1 C T T265I 0.9309 0.8798 0.9823 0.8906 0.9844 0.9773 0.7382
12878 ORF1ab1 A G 14205V 0.2084 0 0 0.0015 0 0.0504 0.9968
14408 ORF1ab2 C T P314L 1 1 0.9975 1 0.909 0.8757 0.8537
17014 ORF1ab2 G T D1183Y 0.049 0.0051 0 0.025 0.0024 0.0026 0.0027
21600 S G T S13I 0 0 0 0 0 0.0025 0
22018 S G T W152C 0.1287 0 0 0 0.002 0.0022 0.0016
22917 S T G L452R 0.1297 0 0 0 0 0 0
23403 S A G D614G 0.9972 1 0.9969 1 0.9969 0.9977 0.9981
25563 ORF3a G T Q57H 0.9893 0.6967 0.9621 0.9987 0.8682 0.7933 0.4046
28887 N C T T205I 0.0422 0.0426 0 0.0017 0 0 0

Given the highly variable viral genome sequence coverage recovered from wastewater samples, there is an urgent need to develop a set of consistent thresholds constituting positive/negative presence of a variant. Monitoring SARS-CoV-2 variants in wastewater may warn of an emerging variant of concern and identify variant dominance occurring when a new variant is introduced in a community. Wastewater genetic monitoring may be particularly useful in the context of limited clinical sample sequencing capacity because a broad perspective on the genetic diversity can be obtained from a few samples. To develop comprehensive epidemiological frameworks required to guide policy, population-level wastewater surveillance of viral genetic diversity should be complemented by clinical sample testing.

Supplementary Material

1

Acknowledgments:

This project was supported by funding from Louisville Metro Public Health and Wellness. Part of this work was performed with assistance of the UofL Genomics Facility, which was supported by NIH/NIGMS KY-INBRE P20GM103436, the J.G. Brown Cancer Center, University of Louisville, and user fees. The following reagent was deposited by the Centers for Disease Control and Prevention and obtained through BEI Resources, NIAID, NIH: Quantitative PCR (qPCR) Control RNA from Heat-Inactivated SARS-Related Coronavirus 2, Isolate USA-WA1/2020, NR 52347.

Footnotes

Ethics: The University of Louisville Institutional Review Board classified this project as Non-Human Subjects Research (NHSR) (reference #: 717950).

Competing Interests: The authors have no conflicts to report related to the submitted work.

References

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Supplementary Materials

1

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