Wastewater monitoring is an approach to identify the presence or abundance of pathogens within a population. The objective of this scoping review (ScR) was to identify and characterize research on human pathogens and antimicrobial resistance detected in untreated human wastewater and sludge. A search was conducted up to March 2023 and standard ScR methodology was followed. This ScR included 1,722 articles, of which 56.5% were published after the emergence of COVID-19. Viruses and bacteria were commonly investigated, while research on protozoa, helminths, and fungi was infrequent. Articles prior to 2019 were dominated by research on pathogens transmitted through fecal–oral or waterborne pathways, whereas more recent articles have explored the detection of pathogens transmitted through other pathways such as respiratory and vector-borne. There was variation in sampling, samples, and sample processing across studies. The current evidence suggests that wastewater monitoring could be applied to a range of pathogens as a public health tool to detect an emerging pathogen and understand the burden and spread of disease to inform decision-making. Further development and refinement of the methods to identify and interpret wastewater signals for different prioritized pathogens are needed to develop standards on when, why, and how to monitor effectively.

  • A wide range of pathogens can be detected in wastewater.

  • 56.5% of studies were published since 2020.

  • Viruses were the most commonly investigated pathogen type followed by bacteria.

  • Earlier studies focused on pathogens transmitted through fecal–oral or waterborne pathways.

  • Additional research is needed to determine which pathogens are conducive to wastewater monitoring and where, when, and how it should be implemented.

The recent coronavirus disease 2019 (COVID-19) pandemic demonstrated that the risk of the emergence and rapid spread of new human health threats can only be combatted by innovative public health tools including strengthened surveillance networks and the integration of rapidly evolving tools, such as wastewater monitoring, into traditional surveillance systems (Mao et al. 2020; Baker et al. 2022).

Wastewater monitoring or surveillance is an approach to identify the presence or abundance of pathogens, biological or chemical indicators of disease, drug and substance use patterns, and other signals within a population over time and may inform public health decision-making (Mao et al. 2020; Sims & Kasprzyk-Hordern 2020). For the surveillance of human diseases, a wastewater monitoring approach can provide a less biased and cost-effective measure of disease prevalence as wastewater data are not dependent on human behavior and health system capacity (Safford et al. 2022; Kilaru et al. 2023). Wastewater monitoring has historically been used to identify pathogens transmitted through water and fecal-oral routes (Kilaru et al. 2023). However, wastewater monitoring has gained momentum globally with innovative research and developments in surveillance for respiratory pathogens during the COVID-19 pandemic (Tlhagale et al. 2022; Boehm et al. 2023). The potential to use wastewater to monitor a wide range of pathogens remains unclear (Kilaru et al. 2023). Therefore, the aim of this scoping review (ScR) was to identify and characterize the current evidence on human pathogens and antimicrobial resistance detected in untreated human wastewater and sludge.

Review type, protocol, and team

An ScR uses systematic methodology to identify and map relevant evidence on an existing or emerging topic (Arksey & O'Malley 2005; Levac et al. 2010; Tricco et al. 2016; Peters et al. 2020a). While similar in the structure and rigor of systematic reviews, their purpose is to identify and map the landscape of the literature and determine possible gaps in the literature (Arksey & O'Malley 2005; Levac et al. 2010; Tricco et al. 2016; Peters et al. 2020a).

To ensure transparency, reproducibility, and consistency during all stages of the ScR, a protocol was created prior to conducting the ScR (Supplementary 1). The protocol includes a list of definitions, inclusion/exclusion criteria, search strategy, title and abstract screening forms, and the data characterization form. A few small deviations were made to the original protocol and are outlined in Supplementary 1. This ScR adheres to the Joanna Briggs Institute methodology for ScRs (Peters et al. 2020b) and was prepared in accordance with the PRISMA extension for ScRs (PRISMA-ScR) (Tricco et al. 2018). A multidisciplinary team with expertise in evidence synthesis, epidemiology, infectious diseases, wastewater, and public health created the protocol and executed the ScR.

Review question and eligibility criteria

The objective of this ScR was to identify and summarize relevant evidence that addresses the research question: what human pathogen(s) or antimicrobial resistant organisms/antimicrobial resistance genes have been detected through wastewater testing or surveillance of untreated, human wastewater or sludge? The following inclusion criteria were applied:

  • (1)

    Publication date: All

  • (2)

    Language: English and French

  • (3)

    Study design: All

  • (4)

    Country: All

  • (5)

    Document type: Primary research (represents a study where the authors collected and analyzed their own data)

  • (6)

    Pathogens: Human (known to infect and cause diseases in humans). Indicator organisms (bacteria and viruses that are used as surrogates to evaluate the presence of pathogens in water and to monitor water quality) were excluded, except if the study was looking at the presence of antimicrobial resistance genes.

  • (7)

    Type of wastewater: Raw/untreated human wastewater or sludge

Search strategy and verification

A comprehensive search strategy was developed by a Health Canada research librarian in collaboration with the authors and applied in five bibliographic databases: Scopus, Embase, Medline, Global Health, and Europe PMC (Supplementary 1). The initial search was conducted on February 15–17, 2022 and was updated on March 21, 2023.

The reference lists of relevant reviews on the topic were hand-searched to the point of saturation to ensure that the database search captured all relevant primary research. During the search verification process of 18 reviews, an additional 304 articles were identified and added to the search results (Hovi et al. 2012; O'Brien & Xagoraraki 2019; Bhatt et al. 2020; Corpuz et al. 2020; Hassoun-Kheir et al. 2020; Michael-Kordatou et al. 2020; Ali et al. 2021; Mousazadeh et al. 2021; O'Keeffe 2021; Pruden et al. 2021; Saawarn & Hait 2021; Zaatout et al. 2021; Bonanno Ferraro et al. 2022; Chau et al. 2022; Dzinamarira et al. 2022; Huang et al. 2022; Shah et al. 2022; Kilaru et al. 2023). Due to the volume of literature on the topic identified through the database search and a lack of resources, a grey literature search was not conducted.

Review management

Search results were imported into the web-based systematic review software DistillerSR (Version 2023.6.2; Evidence Partners, 2023) and duplicates were removed. If an included preprint was subsequently published after our search date, then the preprint version was manually replaced with the published version in DistillerSR, and extractions were completed on the published version. All stages of the ScR were conducted within DistillerSR, including relevance screening and data characterization.

Relevance screening and data characterization

A relevance screening form was developed to determine if the article was relevant to the review using the inclusion and exclusion criteria. The full text of potentially relevant articles was then procured and reviewed using a data characterization form, which aimed to confirm article relevance and extract data on pertinent information from each study such as study design, wastewater sample, sampling frequency and location, method of detection, and pathogens identified. For antimicrobial resistance, we captured whether the article studied antimicrobial resistant organisms in wastewater and how it was tested. Both forms (50 relevance screening and 10 data characterization) were developed a priori and piloted by all reviewers for clarity and consistency. Modifications were implemented based on reviewer feedback, where necessary, prior to implementation. Two reviewers independently used these forms to screen for relevance and extract data. During both stages, reviewers resolved conflicts by consensus or a third reviewer. Both forms including all definitions and data extracted are outlined in detail in the protocol (Supplementary 1). Excluded studies and the reasons for exclusion are documented in Supplementary 2.

Data analysis and reporting

The completed dataset was exported into Microsoft Excel® for Microsoft 365 MSO (Version 2307 Build 16.0.16626.20198) for data cleaning, categorization, descriptive analysis, and narrative summarization. The complete dataset is available in Supplementary 3.

ScR descriptive statistics

Of the 7,092 unique citations screened for relevance, full articles were procured for 3,343 potentially relevant studies and 1,722 (English = 1,713, French = 9) were considered primary research relevant to the research question (Figure 1). Only two articles were excluded from the ScR on the basis of language: one Chinese and one Spanish.
Figure 1

PRISMA flow diagram of the article through the scoping review process.

Figure 1

PRISMA flow diagram of the article through the scoping review process.

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Articles were published between 1929 and 2023 with 56.5% (972/1,722) published since 2020. The majority of the articles were primary peer-reviewed research articles (1,525/1,722) and originated from Europe (569/1,722), North America (480/1,722), and Asia (413/1,722) (Table 1). The articles utilized observational (1,468/1,722) or experimental (580/1,722) study designs to investigate human pathogens in wastewater, with the majority being longitudinal/surveillance (includes monitoring) study designs (1,299/1,722). Experimental studies included the evaluation of detection methods (277/1,722), evaluation of sampling/sample preparation methods (254/1,722), or controlled or challenge trials (49/1,722), in which the majority analyzed the fate of pathogens through wastewater treatment plants. A small number of relevant primary research also included a risk assessment or predictive model (103/1,722). Many papers encompassed multiple study designs, most often to validate the detection of a pathogen in wastewater under controlled conditions prior to conducting a field study. The pathogen or antimicrobial resistance organism concentration or signal strength was quantified in 61.6% (1,060/1,722) of the studies. Untreated/raw wastewater was sampled in 97.3% (1,675/1,722) of studies, and untreated/raw/primary sludge was sampled in 5.9% (102/1,722) of studies.

Table 1

General characteristics of 1,722 primary research publications on human pathogens found in untreated wastewater

CategoryCount
Type of document  
 Primary peer-reviewed research 1,525 
 Preprint 102 
 Short communications 79 
 Letter to the editor with data 10 
 Conference proceeding abstract with data 
Continenta  
 Europe 569 
 North Americab 480 
 Asia 413 
 Africa 136 
 South America 113 
 Australia/Oceania 51 
Date of publication  
  < 1970 10 
 1970–1979 30 
 1980–1989 44 
 1990–1999 39 
 2000–2009 156 
 2010–2019 471 
 2020–2023 972 
Study designa  
 Observational 1,468 
  Longitudinal/surveillance (includes monitoring) 1,299 
  Cross-sectional 168 
  Case-control 
 Experimental 580 
  Controlled trial 45 
  Challenge trial 
  Evaluation of detection methods 277 
  Evaluation of sampling/sample preparation methods 254 
 Risk assessment/predictive models 103 
Type of wastewater sampleda  
 Untreated/raw wastewater 1,675 
 Untreated/raw/primary sludge 102 
CategoryCount
Type of document  
 Primary peer-reviewed research 1,525 
 Preprint 102 
 Short communications 79 
 Letter to the editor with data 10 
 Conference proceeding abstract with data 
Continenta  
 Europe 569 
 North Americab 480 
 Asia 413 
 Africa 136 
 South America 113 
 Australia/Oceania 51 
Date of publication  
  < 1970 10 
 1970–1979 30 
 1980–1989 44 
 1990–1999 39 
 2000–2009 156 
 2010–2019 471 
 2020–2023 972 
Study designa  
 Observational 1,468 
  Longitudinal/surveillance (includes monitoring) 1,299 
  Cross-sectional 168 
  Case-control 
 Experimental 580 
  Controlled trial 45 
  Challenge trial 
  Evaluation of detection methods 277 
  Evaluation of sampling/sample preparation methods 254 
 Risk assessment/predictive models 103 
Type of wastewater sampleda  
 Untreated/raw wastewater 1,675 
 Untreated/raw/primary sludge 102 

aTotal number sums to >1,722 as some studies were conducted on more than one continent, had more than one type of detection or study design, or sampled more than one type of wastewater.

bNorth America includes the United States, Canada, Mexico, Central America, and the Caribbean.

Wastewater sampling

The wastewater sampling details of the 1,722 included studies can be found in Table 2 and are described briefly below. The sampling of wastewater occurred in multiple locations including urban communities (1,350/1,722), small rural communities (<10,000 people, 85/1,722), buildings or facilities (372/1,722), and airplane/ship/other transport vehicles (12/1,722). Of the building or facility sample locations, the majority were hospitals (225/372) and universities/colleges (88/372), followed by residential buildings (20/372), schools/daycares/nurseries (18/372), retirement/nursing homes (17/372), retail/shopping (14/372), workplace/offices/factories (13/371), airports/bus terminals (11/372), quarantine/isolation centers (10/372), worker accommodations (9/372), prisons (6/372), hotels/hostels (4/372), and homeless shelters (4/372). For the sampling point, 73.2% (1,261/1,722) of studies obtain their samples from a wastewater treatment plant. Other sampling points included facilities/institutes (372/1,722), sewers (215/1,722), pumping stations (67/1,722), and open drains/canals (66/1,722). Composite (681/1,722), grab (470/1,722), and passive (72/1,722) sampling were the main methods used to collect wastewater samples. The sampling strategies were longitudinal sampling (1,440/1,722) or one-time detection (235/1,722). The most commonly reported sampling frequencies were weekly (278/1,722), one-time (265/1,722), and monthly (222/1,722). The study period was most often 1–2 years (368/1,722) followed by 1–3 months (360/1,722). Polymerase chain reaction (PCR) (1,085/1,722) and culture/biochemical identification (500/1,722) were the most frequently used methods of initially detecting pathogens in wastewater. PCR was also the most commonly used secondary or confirmatory detection method (435/1,722), followed by gel electrophoresis (325/1,722) and Sanger sequencing (326/1,722).

Table 2

Wastewater sampling details of 1,722 primary research publications on human pathogens found in untreated wastewater

CategoryCount
Sampling locationa  
 Urban community 1,350 
 Buildings or facilities 372 
 Urban/rural community – not specified 140 
 Small rural community 85 
 Not reported 20 
 Airplane/ship/other transport vehicle 12 
Sampling pointa  
 Wastewater treatment plant 1,261 
 Facility/institute 372 
 Sewer 215 
 Not reported 86 
 Pumping station 67 
 Open drains/canal 66 
 Sewage outlet/discharge 19 
 Septic tank/truck 17 
 Airplane/ship lavatory tank 12 
 Entry point to sewage lagoon or septic ponds 
 Storage tank/pit latrine 
Sample collection methoda  
 Composite sample 681 
 Not reported 674 
 Grab sample 470 
 Passive sample 72 
 Otherb 
Sampling strategya  
 Longitudinal 1,440 
 One-time detection 235 
 Not applicable (e.g., experiment) 157 
Sampling period  
  < 1 month 263 
 1–3 months 365 
 4–6 months 257 
 7–11 months 317 
 1–2 years 376 
 3+ years 81 
 Not reported 63 
Sampling frequencya  
 Oncec 265 
 Daily 99 
 2–3 times a week 154 
 Weekly 278 
 Bi-weekly (every second week) 91 
 Twice a month 32 
 Monthly 222 
 Every two months 36 
 By season or quarter 23 
 Otherd 65 
 Not reported 561 
Initial detection methoda  
  PCR 1,085 
 Culture/biochemical identification 500 
 Immunoassay 57 
 Next-generation or whole genome sequencing 50 
 Microscopy 37 
 Spectrometry 29 
 Other DNA/RNA sequencing (e.g., Sanger) 10 
 Loop-mediated isothermal amplification (LAMP) 
 Not reported 
 Animal studies 
 Othere 
Secondary/confirmatory detection methoda  
  PCR 435 
 Gel electrophoresis 326 
 Other DNA/RNA sequencing (e.g., Sanger) 325 
 Next-generation or whole genome sequencing 301 
 Immunoassay 94 
 Spectrometry 85 
 Culture/biochemical identification 73 
 Hybridization assay 28 
 Microscopy 16 
 Otherf 
CategoryCount
Sampling locationa  
 Urban community 1,350 
 Buildings or facilities 372 
 Urban/rural community – not specified 140 
 Small rural community 85 
 Not reported 20 
 Airplane/ship/other transport vehicle 12 
Sampling pointa  
 Wastewater treatment plant 1,261 
 Facility/institute 372 
 Sewer 215 
 Not reported 86 
 Pumping station 67 
 Open drains/canal 66 
 Sewage outlet/discharge 19 
 Septic tank/truck 17 
 Airplane/ship lavatory tank 12 
 Entry point to sewage lagoon or septic ponds 
 Storage tank/pit latrine 
Sample collection methoda  
 Composite sample 681 
 Not reported 674 
 Grab sample 470 
 Passive sample 72 
 Otherb 
Sampling strategya  
 Longitudinal 1,440 
 One-time detection 235 
 Not applicable (e.g., experiment) 157 
Sampling period  
  < 1 month 263 
 1–3 months 365 
 4–6 months 257 
 7–11 months 317 
 1–2 years 376 
 3+ years 81 
 Not reported 63 
Sampling frequencya  
 Oncec 265 
 Daily 99 
 2–3 times a week 154 
 Weekly 278 
 Bi-weekly (every second week) 91 
 Twice a month 32 
 Monthly 222 
 Every two months 36 
 By season or quarter 23 
 Otherd 65 
 Not reported 561 
Initial detection methoda  
  PCR 1,085 
 Culture/biochemical identification 500 
 Immunoassay 57 
 Next-generation or whole genome sequencing 50 
 Microscopy 37 
 Spectrometry 29 
 Other DNA/RNA sequencing (e.g., Sanger) 10 
 Loop-mediated isothermal amplification (LAMP) 
 Not reported 
 Animal studies 
 Othere 
Secondary/confirmatory detection methoda  
  PCR 435 
 Gel electrophoresis 326 
 Other DNA/RNA sequencing (e.g., Sanger) 325 
 Next-generation or whole genome sequencing 301 
 Immunoassay 94 
 Spectrometry 85 
 Culture/biochemical identification 73 
 Hybridization assay 28 
 Microscopy 16 
 Otherf 

aTotal number sums to >1,722 as some studies were conducted in multiple locations, at different sampling points, over large time periods, using multiple collection methods, sampling strategies, and detection methods.

bOther sampling methods included swabbing (n = 5), tongue depressor attached to a stick (n = 1), and a NanoCeram virus sampler filter (n = 1).

cOne-time detection for the sampling frequency (n = 265) includes 30 experimental studies that took a single sample.

dOther sampling frequencies included multiple times a week (n = 41), every 1–6 weeks (n = 10), multiple times a month (n = 8), every few months (n = 4), yearly (n = 2).

eOther detection methods included the hybridization assay (n = 3), the optical sensor array (n = 1), and the electrochemical genosensor (n = 1).

fOther secondary/confirmatory detection methods included loop-mediated isothermal amplification (n = 4) and animal studies (n = 3).

Human pathogens

Pathogens detected in wastewater

The detection of human pathogens in untreated wastewater or sludge was described in 99.3% (1,709/1,722) of studies. Of these, pathogens were reported at the genus or species level (1,655/1,709), family level (85/1,709), and at a higher taxonomic rank (14/1,709). Across these studies, 551 pathogens were described at the genus or species level, belonging to 142 distinct microbial families. There were also 10 additional microbial families studied without further taxonomic ranking being provided. A full list of pathogens found in wastewater is available in Supplementary 4.

Viruses were the most commonly investigated pathogen type (68.8%; 1,176/1,709), followed by bacteria (26.4%; 451/1,709), protozoa (4.6%; 78/1,709), helminths (1.4%; 23/1,709), and fungi (0.5%; 9/1,709) (Figure 2). The top 10 pathogens in each pathogen type are shown in Figure 2. Within each pathogen type, most of the research was conducted on fewer than 10 pathogens. One experimental study described the persistence of a prion protein in wastewater (Maluquer de Motes et al. 2012).
Figure 2

Breakdown of the number of studies for the top 10 pathogens investigated within each pathogen category.

Figure 2

Breakdown of the number of studies for the top 10 pathogens investigated within each pathogen category.

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Overall, the top eight families studied (five viruses and three bacteria) over time depict a steady increase in wastewater research between the years 2000–2019 with a steep rise in 2020–2023 (Figure 3), mainly driven by SARS-CoV-2 (675/682, Figure 2) within the Coronaviridae family (682/1,709). The Enterobacteriaceae (325/1,709) family includes the frequently studied pathogens Escherichia sp., Klebsiella sp., Salmonella sp., Enterobacter sp., and Citrobacter sp., as shown in Figure 2. Picornaviridae (303/1,709) includes the commonly studied pathogens such as non-polio enteroviruses, polioviruses, and Hepatovirus A (Hepatitis A virus). The Caliciviridae family (163/1,709) included only Norovirus sp. and Sapporo virus (Sapovirus). Pathogens in the family Adenoviridae (127/1,709) were almost exclusively Adenoviruses. The most common species investigated in the Pseudomonadaceae family (113/1,709), Sedoreoviridae family (93/1,709), and Moraxellaceae family (91/1,709) were Pseudomonas sp., Rotaviruses, and Acinetobacter sp., respectively.
Figure 3

Bubble chart of the top eight most frequently studied pathogen families over time.

Figure 3

Bubble chart of the top eight most frequently studied pathogen families over time.

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Studies conducted prior to 2019, the year COVID-19 emerged, focused on pathogen families transmitted primarily through fecal–oral or waterborne pathways such as Enterobacteriaceae, Picornaviridae, and Caliciviridae, as shown in Figure 3. Starting in the early 2000s, research studies started exploring the detection of pathogens that were primarily transmitted through other pathways such as respiratory, vector-borne, sexual, and blood-borne. Aside from SARS-CoV-2 (n = 675), the number of research studies investigating other respiratory pathogens was low and included SARS-CoV-1 (n = 5) and MERS-CoV (n = 1), influenza A & B (n = 22), respiratory syncytial virus (RSV) (n = 9), and measles virus (n = 5). These studies were primarily conducted in 2020–2023, with the exception of one study on influenza A conducted in 2011 and three studies on SARS-CoV-1 conducted in 2005. Over the last 3 years, sporadic publications on vector-borne pathogens in wastewater have been published on chikungunya (n = 1), dengue (n = 2), yellow fever (n = 1), zika (n = 1), tularensis (n = 1), and tick-borne relapsing fever (n = 1). Starting in the late 2000s, several pathogens causing sexually transmitted and blood-borne infections have also been investigated, including herpes simplex viruses (n = 4), Neisseria gonorrhoeae (n = 1), Treponema pallidum (n = 1), and human papillomaviruses (HPV) (n = 13).

Pathogens not detected in wastewater

There were 6.4% (111/1,722) of studies where pathogens being studied were not detected in wastewater or sludge. This included 120 pathogens belonging to 65 distinct microbial families (Supplementary 4). Of these pathogens, 81.1% (99/122) were detected in wastewater or sludge in other studies and 18.9% (23/122) of pathogens were not detected in individual studies when they were looked for, including hantaviruses, Toxoplasma gondii, and simian immunodeficiency virus (SIV).

Antimicrobial resistance

Wastewater detection of antimicrobial resistant organisms or genes was described in 20.6% (355/1,722) of studies. The majority of these studies were conducted in Europe (148/355) and Asia (119/355), followed by North America (45/355), Africa (34/355), Australia/Oceania (34/355), and South America (20/355). Antimicrobial susceptibility was tested phenotypically (109/355), genotypically (96/355), or using both methods (150/355). Escherichia coli (177/355) and Klebsiella pneumoniae (86/355) were the most commonly reported organisms in antimicrobial resistance studies.

Wastewater and population health

Researchers connected their wastewater findings with population health data in 43.0% (741/1,722) of studies. The majority of these studies correlated wastewater results with clinical surveillance or case data (710/741) for SARS-CoV-2 (471/710), Enteroviruses (63/710), antimicrobial resistant organisms (55/710), or viruses causing acute gastroenteritis (rotaviruses, noroviruses, adenoviruses, sapoviruses, and astroviruses) (49/710).

Public health action

Wastewater detection or monitoring of pathogens was reported to lead to public health action in 3.4% (58/1,722) of studies. This included decisions to commence (43/58) or cease (1/58) public health measures (e.g., additional surveillance, targeted testing, and isolation), implement public health messaging (8/58), and support decision-making (8/58). The majority of these studies were on SARS-CoV-2 (43/58) followed by poliovirus (7/58).

This ScR summarizes the characteristics of the global research on human pathogens and antimicrobial resistance targets found in untreated wastewater and sludge. The results demonstrate that a wide range of pathogens can be detected in wastewater. However, the usefulness of wastewater monitoring for different pathogens is dependent on both the burden of disease in a community, as well as if and how much the pathogen is excreted into wastewater during infection.

In this ScR, there are several notable topic areas that are not underpinned by many studies including certain pathogens, antimicrobial resistance, and some methods for wastewater monitoring. Most studies focused on viral and bacterial pathogens with minimal research on other pathogen types, protozoa, helminths and fungi; the latter are a growing international concern (Benedict et al. 2017; Nnadi & Carter 2021). Some priority fungal pathogens designated by the World Health Organization have been identified in wastewater studies including Candida auris and Nakaseomyces glabratus (Brumfield et al. 2022; World Health Organization 2022; Barber et al. 2023; Rossi et al. 2023). However, this ScR shows that more research is needed to determine if wastewater monitoring is an appropriate method for identifying emerging fungi of international concern. Further syntheses on the identified studies related to antimicrobial resistance may be warranted to understand how and why wastewater has been used to address this important global public health threat.

Tracking antimicrobial resistance burden and trends is an area for which wastewater monitoring could potentially be useful; however, this ScR identified little research on strategies or utility for such monitoring. In theory, monitoring antimicrobial resistance in wastewater could be beneficial for the purpose of identifying multidrug resistant pathogens currently circulating at the population level. Indeed, this is data that has historically been difficult to acquire, and it may provide insights into potential resistance acquirement and dissemination in the environment as sewage can contain a confluence of antimicrobials, human pathogens, resistance genes, and mobile genetic elements (Liguori et al. 2022).

Within the current literature, most of the studies on sampling, sample handling, and extrapolation of wastewater results to the burden of infection in a population were conducted on SARS-CoV-2. For other pathogens, there were few studies that examined the sensitivity of methodologies used to understand the emergence or fluctuations of a pathogen within a population. As the utility of wastewater monitoring is being considered for a broader range of pathogens, research to establish the best practices will need to be conducted. Wastewater samples were the most common for monitoring human pathogens compared to sludge samples. In studies examining both, sludge samples have been described as containing a broader diversity of human pathogens but may also have more inhibitors and other contaminants that change the sample handling and extrapolation of results. Thus, more research is needed into the assay sensitivity, sample processing, and result extrapolation trade-offs for different sample types and how this may influence pathogen detection within a community wastewater catchment (Bibby & Peccia 2013; Peccia et al. 2020). Optimal sampling frequencies may vary depending on the pathogen and characteristics of the outbreak or circulation of the pathogen in the population. Studies conducted on SARS-CoV-2 show that differences in sampling frequencies influenced the characterization of incident COVID-19 cases at the population level (Chan et al. 2023). Daily data were described as the ‘gold standard’ for the trend analysis of SARS-CoV-2 and a minimum of 2–5 samples per week were necessary for capturing trends within the community for SARS-CoV-2 (Chan et al. 2023; Kuroita et al. 2023). For other pathogens, daily and twice weekly sampling approaches are less common in wastewater monitoring, and most studies reported weekly or monthly sampling. An evaluation of the optimal sampling strategy to capture community trends would need to be established for each pathogen and may vary depending on the epidemiologic situation (e.g., outbreak vs. seasonal activity) and the goals of the monitoring system.

This ScR identified that a limited number of studies were conducted in the Caribbean, Central America, Africa, and the Middle East. Wastewater monitoring may offer the greatest benefit in countries with limited clinical surveillance capacity, especially considering that wastewater has several advantages over sampling individuals and case counting, including its ability to be a cost-effective strategy for the detection and evaluation of the burden of infectious diseases in a population (Ali et al. 2022; Ngwira et al. 2022). Considerations for the application of wastewater monitoring in developing countries include an assessment of the wastewater infrastructure and the design of a sampling strategy to get representative samples (Pandey et al. 2021).

It is our intention that the information synthesized and knowledge gaps discussed in this ScR will be used to support evidence-informed decision-making and further research on this topic. Although we attempted to capture all relevant literature on this topic, it is possible that some research was not captured due to the complexity of the search, publication bias, absence of citation indexing, lack of citations by included papers, or the omission of an extensive grey literature search. Articles published in any language other than English and French were not characterized in this ScR due to translation resource constraints; however, only two studies were excluded on the basis of publication language.

While wastewater testing to monitor pathogens is not a new concept, the success of using wastewater to detect SARS-CoV-2 and estimate community burden during the pandemic has demonstrated the use of wastewater to inform public health responses and provided a unique opportunity to compare the traditional surveillance methods against wastewater monitoring data for a sustained period of time. Outside of SARS-CoV-2, a few studies on enteric pathogens also correlated wastewater signals to clinical surveillance data. These suggest that a multifaceted approach to surveillance that incorporates wastewater signals and other traditional epidemiological metrics (e.g., incidence, hospitalizations, and pharmaceutical sales) would be beneficial for both outbreak situations and routine monitoring of many pathogens, including but not limited to influenza, RSV, and antimicrobial resistance. Recent research on SARS-CoV-2 and mpox has shown that wastewater can be used to monitor the burden and spread of a pathogen in a population fairly quickly and economically, which has the potential to influence case-based surveillance strategies in the future (Sherchan et al. 2023; Tiwari et al. 2023). From a public health preparedness lens, additional research is needed to determine which pathogens are conducive to wastewater monitoring, and where, when, and how monitoring should be implemented.

The authors acknowledge Iryna Artyukh, Adhiba Nilormi, Caroline Larocque Guzman, Melanie Katz, Sydney Jennings, Dima Ayache, and Mavra Qamar for assisting with relevance screening and data characterization. Also, David Champredon and Manon Fleury for their expertise and input into the conceptualization of this project, Natalie Knox and Anil Nichani for their project support and expertise, and the Health Canada library for help in designing the search strategy and article procurement.

T.C. served as the project lead, contributed to the design, performed as a reviewer, and wrote the manuscript. P.R. was the project lead, contributed to the design, performed as a reviewer, and edited the manuscript. K.Y. contributed to the design and manuscript, performed as a reviewer, and edited the manuscript. G.M. served as a reviewer, contributed to and edited the manuscript. A.B. performed as a reviewer and data cleanup, and edited the manuscript. K.P. performed as a reviewer and edited the manuscript. L.W. was responsible for the conceptualization, design and initiation of the project, and also edited the manuscript, supervisor. All authors approved the final version for publication.

All relevant data are included in the paper or its Supplementary Information (Supplementary Files 1–4: https://doi.org/10.17605/OSF.IO/2Y6ZU).

The authors declare there is no conflict.

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