Dominika Celmer‐Repin


2023

DOI bib
Assessment of seasonality and normalization techniques for wastewater-based surveillance in Ontario, Canada
Hadi A. Dhiyebi, Joud Abu Farah, Heather Ikert, Nivetha Srikanthan, Samina Hayat, Leslie M. Bragg, Asim Qasim, Mark Payne, Linda Kaleis, Caitlyn Paget, Dominika Celmer‐Repin, Arianne M. Folkema, Stephen Drew, Robert Delatolla, John P. Giesy, Mark R. Servos, Hadi A. Dhiyebi, Joud Abu Farah, Heather Ikert, Nivetha Srikanthan, Samina Hayat, Leslie M. Bragg, Asim Qasim, Mark Payne, Linda Kaleis, Caitlyn Paget, Dominika Celmer‐Repin, Arianne M. Folkema, Stephen Drew, Robert Delatolla, John P. Giesy, Mark R. Servos
Frontiers in Public Health, Volume 11

Introduction Wastewater-based surveillance is at the forefront of monitoring for community prevalence of COVID-19, however, continued uncertainty exists regarding the use of fecal indicators for normalization of the SARS-CoV-2 virus in wastewater. Using three communities in Ontario, sampled from 2021–2023, the seasonality of a viral fecal indicator (pepper mild mottle virus, PMMoV) and the utility of normalization of data to improve correlations with clinical cases was examined. Methods Wastewater samples from Warden, the Humber Air Management Facility (AMF), and Kitchener were analyzed for SARS-CoV-2, PMMoV, and crAssphage. The seasonality of PMMoV and flow rates were examined and compared by Season-Trend-Loess decomposition analysis. The effects of normalization using PMMoV, crAssphage, and flow rates were analyzed by comparing the correlations to clinical cases by episode date (CBED) during 2021. Results Seasonal analysis demonstrated that PMMoV had similar trends at Humber AMF and Kitchener with peaks in January and April 2022 and low concentrations (troughs) in the summer months. Warden had similar trends but was more sporadic between the peaks and troughs for PMMoV concentrations. Flow demonstrated similar trends but was not correlated to PMMoV concentrations at Humber AMF and was very weak at Kitchener ( r = 0.12). Despite the differences among the sewersheds, unnormalized SARS-CoV-2 (raw N1–N2) concentration in wastewater ( n = 99–191) was strongly correlated to the CBED in the communities ( r = 0.620–0.854) during 2021. Additionally, normalization with PMMoV did not improve the correlations at Warden and significantly reduced the correlations at Humber AMF and Kitchener. Flow normalization ( n = 99–191) at Humber AMF and Kitchener and crAssphage normalization ( n = 29–57) correlations at all three sites were not significantly different from raw N1–N2 correlations with CBED. Discussion Differences in seasonal trends in viral biomarkers caused by differences in sewershed characteristics (flow, input, etc.) may play a role in determining how effective normalization may be for improving correlations (or not). This study highlights the importance of assessing the influence of viral fecal indicators on normalized SARS-CoV-2 or other viruses of concern. Fecal indicators used to normalize the target of interest may help or hinder establishing trends with clinical outcomes of interest in wastewater-based surveillance and needs to be considered carefully across seasons and sites.

DOI bib
Assessment of seasonality and normalization techniques for wastewater-based surveillance in Ontario, Canada
Hadi A. Dhiyebi, Joud Abu Farah, Heather Ikert, Nivetha Srikanthan, Samina Hayat, Leslie M. Bragg, Asim Qasim, Mark Payne, Linda Kaleis, Caitlyn Paget, Dominika Celmer‐Repin, Arianne M. Folkema, Stephen Drew, Robert Delatolla, John P. Giesy, Mark R. Servos, Hadi A. Dhiyebi, Joud Abu Farah, Heather Ikert, Nivetha Srikanthan, Samina Hayat, Leslie M. Bragg, Asim Qasim, Mark Payne, Linda Kaleis, Caitlyn Paget, Dominika Celmer‐Repin, Arianne M. Folkema, Stephen Drew, Robert Delatolla, John P. Giesy, Mark R. Servos
Frontiers in Public Health, Volume 11

Introduction Wastewater-based surveillance is at the forefront of monitoring for community prevalence of COVID-19, however, continued uncertainty exists regarding the use of fecal indicators for normalization of the SARS-CoV-2 virus in wastewater. Using three communities in Ontario, sampled from 2021–2023, the seasonality of a viral fecal indicator (pepper mild mottle virus, PMMoV) and the utility of normalization of data to improve correlations with clinical cases was examined. Methods Wastewater samples from Warden, the Humber Air Management Facility (AMF), and Kitchener were analyzed for SARS-CoV-2, PMMoV, and crAssphage. The seasonality of PMMoV and flow rates were examined and compared by Season-Trend-Loess decomposition analysis. The effects of normalization using PMMoV, crAssphage, and flow rates were analyzed by comparing the correlations to clinical cases by episode date (CBED) during 2021. Results Seasonal analysis demonstrated that PMMoV had similar trends at Humber AMF and Kitchener with peaks in January and April 2022 and low concentrations (troughs) in the summer months. Warden had similar trends but was more sporadic between the peaks and troughs for PMMoV concentrations. Flow demonstrated similar trends but was not correlated to PMMoV concentrations at Humber AMF and was very weak at Kitchener ( r = 0.12). Despite the differences among the sewersheds, unnormalized SARS-CoV-2 (raw N1–N2) concentration in wastewater ( n = 99–191) was strongly correlated to the CBED in the communities ( r = 0.620–0.854) during 2021. Additionally, normalization with PMMoV did not improve the correlations at Warden and significantly reduced the correlations at Humber AMF and Kitchener. Flow normalization ( n = 99–191) at Humber AMF and Kitchener and crAssphage normalization ( n = 29–57) correlations at all three sites were not significantly different from raw N1–N2 correlations with CBED. Discussion Differences in seasonal trends in viral biomarkers caused by differences in sewershed characteristics (flow, input, etc.) may play a role in determining how effective normalization may be for improving correlations (or not). This study highlights the importance of assessing the influence of viral fecal indicators on normalized SARS-CoV-2 or other viruses of concern. Fecal indicators used to normalize the target of interest may help or hinder establishing trends with clinical outcomes of interest in wastewater-based surveillance and needs to be considered carefully across seasons and sites.

DOI bib
Wild fish responses to wastewater treatment plant upgrades in the Grand River, Ontario
Kirsten E. Nikel, Gerald R. Tetreault, Patricija Marjan, Keegan A. Hicks, Meghan Fuzzen, Nivetha Srikanthan, Emily K. McCann, Hadi A. Dhiyebi, Leslie M. Bragg, Pam Law, Dominika Celmer‐Repin, Sonya Kleywegt, Jessie Cunningham, Thomas Clark, Mark E. McMaster, Mark R. Servos, Kirsten E. Nikel, Gerald R. Tetreault, Patricija Marjan, Keegan A. Hicks, Meghan Fuzzen, Nivetha Srikanthan, Emily K. McCann, Hadi A. Dhiyebi, Leslie M. Bragg, Pam Law, Dominika Celmer‐Repin, Sonya Kleywegt, Jessie Cunningham, Thomas Clark, Mark E. McMaster, Mark R. Servos
Aquatic Toxicology, Volume 255

Municipal wastewater treatment plant (WWTP) effluent is one of several point sources of contaminants (nutrients, pharmaceuticals, estrogens, etc.) which can lead to adverse responses in aquatic life. Studies of WWTP effluent impacts on rainbow darter (Etheostoma caeruleum) collected downstream of WWTPs in the Grand River, Ontario have reported disruption at multiple levels of biological organization, including altered vitellogenin gene expression, lower levels of in vitro steroid production, and high frequency of intersex. However, major upgrades have occurred at treatment plants in the central Grand River over the last decade. Treatment upgrades to the Waterloo WWTP were initiated in 2009 but due to construction delays, the upgrades came fully on-line in 2017/2018. Responses in rainbow darter have been followed at sites associated with the outfall consistently over this entire time period. The treatment plant upgrade resulted in nitrification of effluent, and once complete there was a major reduction in effluent ammonia, selected pharmaceuticals, and estrogenicity. This study compared several key responses in rainbow darter associated with the Waterloo WWTP outfall prior to and post upgrades. Stable isotopes signatures in fish were used to track exposure to effluent and changed dramatically over time, corresponding to the effluent quality. Disruptions in in vitro steroid production and intersex in the darters that had been identified prior to the upgrades were no longer statistically different from the upstream reference sites after the upgrades. Although annual variations in water temperature and flow can potentially mask or exacerbate the effects of the WWTP effluent, major capital investments in wastewater treatment targeted at improving effluent quality have corresponded with the reduction of adverse responses in fish in the receiving environment.

DOI bib
Wild fish responses to wastewater treatment plant upgrades in the Grand River, Ontario
Kirsten E. Nikel, Gerald R. Tetreault, Patricija Marjan, Keegan A. Hicks, Meghan Fuzzen, Nivetha Srikanthan, Emily K. McCann, Hadi A. Dhiyebi, Leslie M. Bragg, Pam Law, Dominika Celmer‐Repin, Sonya Kleywegt, Jessie Cunningham, Thomas Clark, Mark E. McMaster, Mark R. Servos, Kirsten E. Nikel, Gerald R. Tetreault, Patricija Marjan, Keegan A. Hicks, Meghan Fuzzen, Nivetha Srikanthan, Emily K. McCann, Hadi A. Dhiyebi, Leslie M. Bragg, Pam Law, Dominika Celmer‐Repin, Sonya Kleywegt, Jessie Cunningham, Thomas Clark, Mark E. McMaster, Mark R. Servos
Aquatic Toxicology, Volume 255

Municipal wastewater treatment plant (WWTP) effluent is one of several point sources of contaminants (nutrients, pharmaceuticals, estrogens, etc.) which can lead to adverse responses in aquatic life. Studies of WWTP effluent impacts on rainbow darter (Etheostoma caeruleum) collected downstream of WWTPs in the Grand River, Ontario have reported disruption at multiple levels of biological organization, including altered vitellogenin gene expression, lower levels of in vitro steroid production, and high frequency of intersex. However, major upgrades have occurred at treatment plants in the central Grand River over the last decade. Treatment upgrades to the Waterloo WWTP were initiated in 2009 but due to construction delays, the upgrades came fully on-line in 2017/2018. Responses in rainbow darter have been followed at sites associated with the outfall consistently over this entire time period. The treatment plant upgrade resulted in nitrification of effluent, and once complete there was a major reduction in effluent ammonia, selected pharmaceuticals, and estrogenicity. This study compared several key responses in rainbow darter associated with the Waterloo WWTP outfall prior to and post upgrades. Stable isotopes signatures in fish were used to track exposure to effluent and changed dramatically over time, corresponding to the effluent quality. Disruptions in in vitro steroid production and intersex in the darters that had been identified prior to the upgrades were no longer statistically different from the upstream reference sites after the upgrades. Although annual variations in water temperature and flow can potentially mask or exacerbate the effects of the WWTP effluent, major capital investments in wastewater treatment targeted at improving effluent quality have corresponded with the reduction of adverse responses in fish in the receiving environment.