Predicting coliform presence in private wells as a function of well characteristics, parcel size and leachfield soil rating

https://doi.org/10.1016/j.scitotenv.2020.143701Get rights and content

Highlights

  • 1163 wells in Gaston County, North Carolina tested for coliform bacteria between October 2017 and October 2019

  • Coliform bacteria were found in 329 samples, including 290 drilled and 39 bored wells.

  • Increased likelihood of wells near one another to test positive for coliform in northeast Gaston County

  • Bored wells and well age are strong predictors of biological contamination.

Abstract

Public water systems must be tested frequently for coliform bacteria to determine whether other pathogens may be present, yet no testing or disinfection is required for private wells. In this paper, we identify whether well age, type of well, well depth, parcel size, and soil ratings for a leachfield can predict the probability of detecting coliform bacteria in private wells using a multivariate logistic regression model. Samples from 1163 wells were analyzed for the presence of coliform bacteria between October 2017 and October 2019 across Gaston County, North Carolina, USA. The maximum well age was 30 years, and bored wells (median age = 24 years) were older than drilled wells (median age = 19 years). Bored wells were shallower (mean depth = 18 m) compared to drilled wells (mean depth = 79 m). We found coliform bacteria in 329 samples, including 290 of 1091 drilled wells and 39 of 72 bored wells. The model results showed bored wells were 4.76 times more likely to contain bacteria compared to drilled wells. We found that the likelihood of coliform bacteria significantly increased with well age, suggesting that those constructed before well standards were enforced in 1989 may be at a higher risk. We found no significant association between poorly rated soils for a leachfield, well depth, parcel size and the likelihood of having coliform in wells. These findings can be leveraged to determine areas of concern to encourage well users to take action to reduce their risk of drinking possible pathogens in well water.

Section snippets

Background

Water contaminated with pathogens can cause illness if ingested without appropriate treatment (Wallender et al., 2014; Beer et al., 2015; Benedict et al., 2017). Illnesses that result from consuming pathogenic contaminated water includes acute gastrointestinal illness, acute respiratory illness, and neurologic illnesses (Benedict et al., 2017). Waterborne diseases may even lead to early death (Cortese and Parashar, 2009; Morgan et al., 2015). For example, Chaudhry et al. (2015) found that the

Well sampling and testing

Gaston County Department of Health and Human Services (GC DHHS) in partnership with the University of North Carolina at Charlotte (UNCC) organized free well water sampling across Gaston County to evaluate groundwater quality and protect human health (Dye and Zarate-Bermudez, 2018; Lan et al., 2020; Owusu et al., 2020a; Owusu et al., 2020b). Student teams from UNC Charlotte visited every permitted private well in Gaston County, North Carolina (Fig. 1), from October 2017 to October 2019. The

Descriptive statistics

The maximum well age in the data was 30 years and this reflects the period when Gaston County enforced standards on well construction from 1989. Pre-1989 wells were not sampled for this study. Samples were obtained from 1091 drilled wells and 72 bored wells. As shown in Fig. 2A, we found well age for bored wells (median well age = 24 years) were significantly (p < 0.05) older than drilled wells (median age = 19 years).

The median well depth was 70.1 m. We found well depths for bored wells

Discussion

Coliform bacteria were reported in 290 of 1091 drilled wells and 39 of 72 bored wells. Coliform bacteria were more likely to occur in older wells. A high proportion of bored wells that were positive for coliform bacteria were found in the northwestern part of Gaston County. Compared to bored wells, drilled wells that were positive for coliform bacteria were closer to each other. In some instances, out of more than nine samples within a 1-km area in the northeastern parts of the county, 60% of

Conclusions

We found evidence of groundwater contamination with regards to the U.S. EPA standards for the presence of coliform bacteria in water. We used GIS techniques to map possible spatial patterns of positive coliform samples and learned of the increased likelihood of wells near one another to test positive for coliform bacteria, suggesting common contamination sources, particularly in the northeastern part of the county. We then used multivariate logistic regression to investigate possible causes of

CRediT authorship contribution statement

CO conceived the idea of modeling the presence of Coliform bacteria in private wells in Gaston County, North Carolina. CO designed the overall study, prepared the data with technical support from ED, GS, DV, KB and RP. The first draft of the manuscript was written by CO, and all authors provided extensive inputs on different versions of the manuscripts. All authors read and approved the final manuscript.

Funding

This work was supported by the National Center for Environmental Health [CDC-RFA-EH15-1507].

Declaration of competing interest

None.

References (63)

  • Bivand, R. (2009). Spatial dependencies: weighting schemes, statistics and models. R package version...
  • M.A. Borchardt et al.

    Norovirus outbreak caused by a new septic system in a dolomite aquifer

    Groundwater

    (2011)
  • J.P. Cabral

    Water microbiology. Bacterial pathogens and water

    Int. J. Environ. Res. Public Health

    (2010)
  • Centers for Disease Control and Prevention

    Magnitude and Burden of Waterborne Disease in the U.S

  • Centers for Disease Control and Prevention

    Disinfecting Wells After a Disaster

  • Centers for Disease Control and Prevention (CDC)

    Well testing

  • Centers for Disease Control and Prevention (CDC)

    Safer Well Water Through Stronger Public Health Programs

  • J.W. Charrois

    Private drinking water supplies: challenges for public health

    Cmaj

    (2010)
  • S.A. Chaudhry et al.

    Hepatitis E infection during pregnancy

    (2015)
  • M.M. Cortese et al.

    Prevention of rotavirus gastroenteritis among infants and children: recommendations of the Advisory Committee on Immunization Practices (ACIP)

    Mortal. Wkly Rep.

    (2009)
  • E. Delmelle

    Spatial sampling

  • S. Dye et al.

    Benefits of collaboration between a county health department and a local university in North Carolina

    J. Environ. Health

    (2018)
  • J. Fairbrother et al.

    Escherichia coli: on-farm contamination of animals

    Rev. Sci. Tech.

    (2006)
  • A. Getis

    Spatial autocorrelation

  • S. Godfrey et al.

    Microbiological risk assessment and management of shallow groundwater sources in Lichinga, Mozambique

    Water Environment Journal

    (2006)
  • T.R. Gonzales

    The effects that well depth and wellhead protection have on bacterial contamination of private water wells in the Estes Park Valley, Colorado

    J. Environ. Health

    (2008)
  • L. Hamel

    Model assessment with ROC curves

  • F. Hossain et al.

    Spatial pattern of arsenic contamination in shallow wells of Bangladesh: regional geology and nonlinear dynamics

    Stoch. Env. Res. Risk A.

    (2006)
  • R. Hubbard et al.

    Water quality and the grazing animal

    Journal of animal science

    (2004)
  • P.D. Hynds et al.

    Development of a microbial contamination susceptibility model for private domestic groundwater sources

    Water Resour. Res.

    (2012)
  • O.B. Kaplan

    Septic Systems Handbook

    (2014)
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      E. coli are considered indicators of recent faecal contamination as they are found almost exclusively in the gastrointestinal tract of humans and animals, unlike the rest of the TC group, which can exist naturally in soil and water (Croxen et al., 2013; World Health Organization, 2017). Previous studies of TC contamination (i.e., detection rates and concentrations) in private wells have facilitated an improved understanding of groundwater contamination mechanisms and susceptibility factors (Gonzales, 2008; Invik et al., 2017; Owusu et al., 2021), but a limited number have examined the relationship between multiple concurrent susceptibility factors and TC contamination, and still fewer have focused on identifying links between TC and E. coli contamination of groundwater. According to the Ministry of the Environment, Conservation, and Parks (MECP), well water microbial test results of five or fewer colony-forming units (CFU) of TC per 100 mL are indicative of acceptable water quality in the absence of a chlorine residual, as long as zero CFU of E. coli are detected (Ministry of the Environment, Conservation, and Parks, 2021).

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