Legacy and replacement PFAS are of increasing public and regulatory concern.
Easy access is needed for health research on replacements for toxic legacy PFAS.
This database will display and summarize current PFAS health and toxicology studies.
Per– and polyfluoroalkyl substances (PFAS) confer waterproof, greaseproof, and non-stick properties when added to consumer products. They are also used for industrial purposes including in aqueous film forming foams for firefighting. PFAS are ubiquitous in the environment, are widely detected in human biomonitoring studies, and are of growing regulatory concern across federal, state, and local governments. Regulators, scientists, and citizens need to stay informed on the growing health and toxicology literature related to PFAS.
The goal of this systematic evidence map is to identify and organize the available health and toxicology related literature on a set of 29 PFAS of emerging and growing concern.
Search and study eligibility
We will search the electronic database PubMed for health or toxicological studies on 29 PFAS of emerging concern. Eligible studies must contain primary research investigating the link between one or more of the PFAS of interest and a health effect, toxicological, or biological mechanistic endpoint.
Study appraisal and synthesis methods
Title and abstract screening and full text review will require a single reviewer for inclusion to the next level and two independent reviewers for exclusion. Study quality will not be conducted for this evidence mapping. Study characteristics will be extracted and coded from the included studies and checked for accuracy by a second reviewer. The extracted and coded information will be visualized in a publicly available, interactive database hosted on Tableau Public. Results of the evidence mapping will be published in a narrative summary.
ADME/PK/TKabsorption, distribution, metabolism, excretion, pharmacokinetic or toxicokinetic propertiesAFFFaqueous film forming foamAIartificial intelligenceATSDRAgency for Toxic Substances and Disease RegistryCOIconflict of interestEPAUS Environmental Protection Agencyhpfhours post-fertilizationMCLmaximum contaminant levelNJDWQINew Jersey Drinking Water Quality InstituteNTPNational Toxicology ProgramPECOpopulations, exposures, comparators, and outcomesPFASper- and polyfluoroalkyl substancesPFBSperfluorobutane sulfonic acidPFOAperfluorooctanoic acidPFOSperfluorooctanesulfonic acidPNDpostnatal dayPPARperoxisome proliferator activated receptorpptpart per trillionQCquality control
PFASPer- and polyfluoroalkyl substancesSystematic evidence mapToxicology
Over the past few decades per- and polyfluoroalkyl substances (PFAS) contamination has grown into a serious global health threat. PFAS are a large class of synthetic chemicals that contain an alkyl chain with at least one fully fluorinated carbon atom. Although the class is broad, they are related in their extreme persistence in our environment and are often referred to as “forever chemicals”. PFAS are also highly mobile in the environment and some have been found to bioaccumulate, or build up, in humans and animals.
Best known for their original use in producing the fluoropolymer Teflon and the stain-resistant coating Scotchgard, these chemicals are now used in a wide range of consumer and industrial products where grease or water proofing is desired, or surfactant action is a benefit. These products include food packaging and non-stick cookware, cosmetics, waterproof and stain-proof textiles and carpet, aqueous film forming foam (AFFF) to fight Class B fires, and as part of metal plating processes.
Widespread use of PFAS has resulted in the ubiquitous presence of these chemicals in the environment including in rivers, soil, air, house dust, food and drinking water from surface water and groundwater sources. Virtually all Americans have multiple PFAS at detectable levels in the blood serum (CDC, 2018). Unfortunately, PFAS have been linked to many harmful health effects, including cancer, immune system dysfunction, liver damage, developmental and reproductive harm, and hormone disruption (ATSDR, 2018).
The most well-known and well-studied PFAS are perfluorooctanoic acid (PFOA) and perfluorooctane sulfonic acid (PFOS) (ATSDR, 2018). Due to increasing concern over the harm these chemicals cause to human health, wildlife, and the environment, the U.S. Environmental Protection Agency initiated the PFOA Stewardship Program in 2006 (US EPA, 2006). Through the program, the major PFAS manufacturing companies committed to phasing out PFOA, its precursor chemicals and related higher homologue chemicals from production in the US by 2015; however, PFOA and PFOS are still produced internationally and consumer products containing PFOA and related-PFAS may still be imported into the US (US EPA, n.d.) This, in combination with their extreme persistence in the environment, ensures that their legacy remains.
The scientific literature on PFAS has increased exponentially in the last decade, which has resulted in a greater understanding of the potential adverse health effects associated with PFOA and PFOS exposure (Grandjean, 2018). For PFOA and PFOS this has resulted in increasingly stricter health thresholds proposed by various agencies (Cordner et al., 2019). In 2016 the EPA issued lifetime drinking water health advisories of 70 ppt for PFOA and PFOS, individually or combined (US EPA, 2016b, US EPA, 2016c). Recently several states (e.g. MN, NH, NJ, VT, MI) have proposed drinking water regulatory or guideline levels below 70 ppt (Cordner et al., 2019; MDHHS, 2019; NHDES, 2019).
For various reasons, including uncertainties in data and biological significance, the EPA did not select the most sensitive health effects currently associated with PFOA and PFOS when generating their 2016 health advisories. There is evidence that both altered mammary gland development for PFOA (Macon et al., 2011; Tucker et al., 2015; White et al., 2011) and immunotoxicity for PFOS (Dong et al., 2009; Grandjean and Budtz-Jorgensen, 2013; Guruge et al., 2006; Peden-Adams et al., 2008) can occur at levels an order of magnitude or lower than the health effects selected by the EPA. Since the EPA issued its 2016 advisories, the National Toxicology Program (NTP) released a report concluding that both PFOA and PFOS are presumed to constitute immune hazards to humans (NTP, 2016). And most recently, the New Jersey Drinking Water Quality Institute (NJDWQI) and the Agency for Toxic Substances and Disease Registry (ATSDR) have either acknowledged or attempted to account for these more sensitive health effects in generating their proposed health standards (ATSDR, 2018; NJDWQI, 2017; NJDWQI, 2018). As a result, both NJDWQI and ATSDR have proposed significantly more protective (5–10 times lower) health thresholds for PFOA and PFOS than the EPA health advisories (ATSDR, 2018; NJDWQI, 2017; NJDWQI, 2018).
The expansion of research on PFAS has also resulted in increasing concern over the rising use of and exposure to replacements for legacy PFAS. Most legacy PFAS, including PFOA and PFOS, are “long-chain” chemicals, meaning their molecular structure contains a chain of six (for perfluoroalkyl sulfonic acids) or seven (for perfluoroalkyl carboxylic acids) or more carbon atoms. While there is less toxicity data on shorter-chain and other alternative PFAS replacing long-chain PFAS, evidence is growing quickly that indicates they collectively pose similar threats to human health and the environment; which, combined with similar concerns over the environmental fate and persistence, have led independent scientists and other professionals from around the globe to express concern about the continued and increasing production and release of PFAS (Blum et al., 2015; Scheringer et al., 2014).
Due to the health concerns related to PFAS exposure and concerns over their environmental fate and persistence, there have been various efforts at the local, state and federal level to regulate PFAS. For example, severe contamination of drinking water with both legacy and alternative PFAS in communities across the nation, has led to considerable efforts at the state-level to set enforceable drinking water maximum contaminant levels (MCLs). It is expected that efforts to regulate PFAS in drinking water (as well as in ground and surface waters, air, consumer products, etc.) will continue over the coming years. Staying abreast of the current PFAS health effects literature is a major barrier for setting effective regulations to protect human and environmental health. Further, as additional communities learn of their own PFAS contamination, there is a desire from citizens and citizen-led groups to know more about these chemicals and how they may impact the health of their communities.
The ATSDR Draft Toxicological Profile for Perfluoroalkyls provides estimates concerning the volume of available human and experimental animal studies through May 2016 for PFOA (Fig. 2-1; n = 271), PFOS (Fig. 2-2; n = 218) and 12 additional PFAS (Fig. 2-3; n = 127) (ATSDR, 2018). Though helpful, the figures provided by ATSDR do not allow the end-user much flexibility in sorting, filtering, or deeply exploring the available evidence. Additionally, ATSDR Fig. 2-3 presents the evidence for 12 PFAS of emerging interest, but it is not possible to determine how the identified studies are distributed among the chemicals, which limits its utility to state agencies proposing regulatory values for individual PFAS beyond PFOA and PFOS.
To this end, we will use systematic evidence mapping methodology to improve citizen, scientific and regulatory access to current evidence regarding the health effects associated with exposure to PFAS. Systematic evidence maps collate and characterise evidence available on a broad research topic. They distill a potentially vast, heterogeneous evidence base into a (computationally) accessible, comparable and easily updated format using transparent and reproducible methodology. Systematic evidence maps take the form of searchable databases of references and meta-data, including data extracted and coded from each individual included study. This format removes the barriers associated with manually assessing large volumes of data by affording end users a broad overview of the evidence base, allowing fast identification of emerging trends, including the presence of evidence gaps and evidence clusters (James et al., 2016). As such, systematic evidence maps do not attempt to synthesise or integrate evidence in answer to any one specific research question, but rather provide users with the means of exploring the evidence according to their own varied research interests – identifying trends which might form the basis of future syntheses or further research.
Here, we propose to create a systematic evidence map that transparently and systematically surveys the available health and toxicological evidence associated with PFAS exposure. The result will be an online, interactive, interrogable, and user-friendly database (Miake-Lye et al., 2016). Given the pace at which the evidence base appears to be growing, it would seem that now is a good time to establish a systematically and transparently created interactive database, such as the one proposed in this protocol. A database concerning the health effects of “short-chain PFAS” has been previously suggested, but to our knowledge has not yet been produced (Bowman, 2015).
The objectives of this systematic evidence map are to:1.
Identify and organize the available scientific research on the physiological health effects of a set of 29 PFAS (see Table 1), individually or combined, as measured in human, animal, or ex vivo/in vitro models.
Table 1. List of PFAS included in systematic evidence map
|NEtFOSAA||2-(N-ethyl-perfluorooctane sulfanamido) acetic acid||2991-50-6|
|NMeFOSAA||2-(N-Methyl-perfluorooctane sulfanamido) acetic acid||2355-31-9|
|GenX||Hexafluoropropylene Oxide (HFPO) Dimer Acid||13252-13-6|
|6:2 Cl-PFESA||6:2 chlorinated polyfluorinated ether sulfonic acid||73606-19-6|
|8:2 Cl-PFESA||8:2 chlorinated polyfluorinated ether sulfonic acid||83329-89-9|
|Nafion BP2||Nafion Byproduct 2||749836-20-2|
|6:2 FTSA||h,1h,2h,2h-Perfluorooctanesulfonic acid||27619-97-2|
|8:2 FTSA||2-(Perfluorooctyl)ethane-1-sulfonic acid||39108-34-4|
|HFPO-TA||Hexafluoropropylene Oxide (HFPO) Trimer Acid||13252-14-7|
Present the literature in a user-friendly, online, interactive database that will connect end-users directly to referenced primary studies.3.
Identify data gaps and research needs, and publish a narrative summary of the systematic map.
The protocol described here, serves to document decisions made a priori regarding the conduct of the systematic evidence mapping.
This protocol has been prepared in accordance with the ENVINT PRISMA-SM-P report (available at (Elsevier, 2017)) and based on guidance from the Collaboration for Environmental Evidence (Collaboration for Environmental Evidence, 2018). The protocol has been registered at Zenodo (Pelch et al., 2019).
2.1. Information sources
PFAS (Table 1) were prioritized for inclusion in this systematic evidence map due to their inclusion in the ATSDR Draft Toxicological Profile for Perfluoroalkyls (ATSDR, 2018), their presence in US EPA Method 537.1 (Shoemaker and Tettenhorst, 2018), because they were reported to be detected in blood in the GenX exposure study (NC State Center for Human Health and the Environment, 2018a; NC State Center for Human Health and the Environment, 2018b), or because they were suggested to be of interest by members of the NGO community (personal communication). Because PFOA and PFOS have been recently reviewed by US EPA (US EPA (United States Environmental Protection Agency), 2016a, US EPA, 2016c), ATSDR (ATSDR, 2018), and NTP (NTP, 2016), they were not prioritized for incorporation in this systematic evidence map.
The peer-reviewed published literature will be identified by searching PubMed electronic database with no date or language restrictions. If a search update is needed, the PubMed search will be repeated but limited to studies published since the date of the last search using the “date-create” field in the PubMed Advanced Search Builder. The number of studies retrieved from searching will be tracked in a study flow diagram (e.g. Fig. 1), which will also track how the studies progress through the review. Any studies identified from sources other than PubMed (e.g. identified by hand searching included studies or relevant reviews) will be marked as “Identified from other sources” on the study flow diagram.
2.2. Search strategy
The Pubmed search will include names and synonyms for 29 PFAS of emerging interest. Specific search terms can be found in Appendix 1. There will be no search limitations based on health outcome or other aspects of study design or conduct. Furthermore, the search will be conducted without limit on publication year or language.
Search terms were identified for the PFAS of interest by searching the CASRN for each chemical, the common abbreviation, and full chemical names, which have been identified as synonyms for the chemical in PubChem. The search logic for GenX and PFBS are adapted from the recent EPA GenX and PFBS Draft Toxicity Assessments (US EPA, 2018a, US EPA, 2018b). The search logic for PFAS in general has been adapted from the search logic used in the NTP monograph (NTP, 2016). When possible, the search will also include CASRN and relevant search terms for associated salts (see Table 2).
Table 2. Populations, Exposures, Comparators, and Outcomes (PECO) Statement.
|Populations||Any human, animal (whole organism including experimental and observational studies), or ex vivo/in vitro models utilizing organs, tissues, cell lines, or cellular components (e.g. cell-free receptor binding assays).|
|Exposures||Exposure to at least one of the PFAS or the associated salts listed in Table 1 (e.g. perfluorobutane sulfonic acid (PFBS; CASRN 375-73-5) and potassium perfluorobutane sulfonate (K + PFBS; CASRN 29420-49-3)). Exposures may include, for example: biomarkers of exposure, modeling of potential exposures, and/or administered exposures. Mixtures of PFAS will also be included and listed as PFASmix. There are no limitations on the timing, route, level, or determination of estimated exposure.|
|Comparators||Humans, animals, organs, tissues, cell lines, or cellular components exposed to a lower level of a PFAS than the more highly exposed subjects or treatment groups, or vehicle-only treatment.|
|Outcomes||Any health outcome or type of biological response measured in the exposed population.|
2.3. Eligibility criteria
Study eligibility is based on the PECO statement provided in Table 2.
To be included in this systematic evidence map, studies must contain primary research investigating the link between one or more of the PFAS of interest and a health effect, toxicological, or biological mechanistic endpoint. Epidemiological, animal, and in vitro and mechanistic evidence will be included. Studies that do not contain health, toxicological, or mechanistic information on the PFAS of interest will be excluded at the title and abstract level and will not be further data extracted.
Studies that investigate aspects of PFAS other than health outcomes will be tagged and categorized as to the nature of the evidence and may be made available upon request or as a downloadable list on the TEDX website (www.tedx.org). This includes studies on environmental detection, environmental fate and transport, biomonitoring, detection in wildlife, reports on the absorption, distribution, metabolism, excretion, pharmacokinetic or toxicokinetic properties (ADME/PK/TK), in silico and read across analyses, reviews, and systematic reviews of the PFAS of interest. Though they will be tagged and collated, studies that lack health outcome endpoints will not proceed past title and abstract screening.
Given that this is a systematic evidence map rather than a systematic review, efforts will be made to include non-English language studies if essential information (i.e. chemicals tested and health outcomes assessed) can be obtained from the title and abstract. Non-English studies will be denoted with square brackets on the title. Conference abstracts, presentations, posters, and theses/dissertations will not be included in this systematic evidence map.
2.4. Data management
2.4.1. Management of literature updates and study flow diagram
A study flow diagram will be maintained that describes the number of studies evaluated in each step of the review (Fig. 1). Any search updates or modifications to the protocol will also be noted as amendments to the registered protocol.
Literature search results will be imported to EndNote X6. Duplicate records will be identified using EndNote’s “Find Duplicates” feature based on title and author fields. All records will receive a unique identification number upon import to EndNote X6 that will be maintained throughout the review. Records will then be exported and uploaded to DistillerSR (Evidence Partners; Ottawa, Ontario, Canada). Customized forms in DistillerSR will be used to manually screen studies at the title and abstract level and to extract study details from full-text documents. Extracted information will be exported from DistillerSR to one of three .csv files that can be directly uploaded to Tableau Desktop Professional Edition vs 2018.3 (Tableau; Seattle, WA) for visualization. The three .csv files will represent the three evidence streams: human, animal, and in vitro. The .csv files will also be submitted as supplemental files to the journal with the final report.
The systematic evidence map will be hosted on TEDX’s public profile on Tableau Public, which is available at https://public.tableau.com/profile/the.endocrine.disruption.exchange#!/. A link to the visualization will also be found on the TEDX website along with additional systematic evidence map details including links to the published and registered protocols.
2.5. Selection and data collection processes
Title and abstract screening will be performed in DistillerSR by senior researchers (KEP, AR, TW), none of which have authored peer reviewed articles that would be relevant for inclusion in this systematic evidence map. DistillerSR’s artificial intelligence (AI) text mining functionality may be utilized to prioritize studies for title and abstract screening. Title and abstract screening and full text review will require a single reviewer for inclusion to the next level and two independent reviewers for exclusion. Discrepant screening results will be resolved by discussion. Likewise, full text review, data extraction, and coding will be conducted by a single reviewer with a secondary reviewer confirming the accuracy and completeness of extracted and coded data using DistillerSR’s quality control (QC) feature. We will attempt to contact study authors via email if it is unclear which PFAS was investigated (e.g. missing CASRN or structure, or ambiguous chemical name). Other missing information will be flagged as missing, but study authors will not be contacted. Prior to commencing the search, DistillerSR forms will be piloted by KEP, AR, and TW on a small set of studies to ensure ease and accuracy of data extraction and export for visualization in Tableau.
2.6. Data coding strategy
Data extraction will be conducted on full-text studies using structured forms in DistillerSR. The following information will be collected from all included studies: authors, journal, reference information, year of publication, which evidence streams were investigated (human, animal, or in vitro), conflict of interest statement (COI), funding statement, acknowledgements statement, chemicals evaluated, and the health outcome category (see Table 3). Data specific to each evidence stream will also be collected as outlined in Table 3. All data will be captured at the study level rather than at the level of each individual endpoint. In other words, for each study, data extractors will be instructed to select all responses that apply to each question.
Table 3. Data coding and recording.
|Data category||Data captured|
|Bibliographic information||●authors●year of publication●journal●title●reference information●study URL●COI statement●authors’ acknowledgments statement●funding source|
|Evidence stream||Evidence stream is defined by the type of subject or population being exposed to the chemical.|
●Human epidemiological studies●Animal (including experimental and observational whole animal studies)●In vitro (includes mechanistic studies in humans and other species, ex vivo, and cell free)
|Health effects studied||Health outcomes will be tagged as follows (these headings were derived from the MedLinePlus ontology, which is available with definitions from the Unified Medical Language Systems Database (US NLM (United States National Library of Medicine), 2016):|
●Blood, heart, and circulation●Bones, joints, and muscles●Brain and nerves●Cancers●Digestive system●Ear, nose, and throat●Endocrine system●Eyes and vision●Female reproductive system●Genetics/birth defects●Immune system●Injuries and wounds●Kidneys and urinary system●Lungs & Breathing●Male reproductive system●Mental health and behavior●Metabolic problems●Mouth and teeth●Mortality●Pregnancy and reproduction●Sexual health issues●Skin, hair, and nails
|Chemicals studied||Data will be collected on the 29 PFAS listed in Table 1. If PFAS other than those listed in Table 1 are studied in included studies, they will be permanently added to the list of options so that they might be tracked for any future updates or expansions to this systematic evidence map. Mixtures of PFAS or ∑PFAS presented in a study will be categorized as PFASmix in addition to the component PFAS.|
|Human study elements||Study type:|
●Case control●Cohort●Cross-sectional●Ecological/communityStudy location:
●US (list US state abbreviation)●Non-US●The city, state, and/or country of study location will be captured as free textExposure type:
●General population●Known or suspected point source pollution●OccupationalStudy population sex:
●The study N will be collected as free text for the total number of study participants (e.g. all cases and controls)Timing of exposure assessment:
●The timing of exposure according to study authors will be captured as free text and will also be further categorized as:●Preconception●Pregnancy●birth-1 years of age●>1–3 years of age●>3–12 years of age●>12–20 years of age●>20 years of ageExposure assessment:
●The exposure assessment method as described by the study authors will be captured as free text and will also be further categorized as follows, with controlled additions allowed as needed:●Adipose tissue●Amniotic fluid●Breast milk●Cord blood●Distance to source●Drinking water concentration●Hair●Nails●Serum●Urine●Whole bloodExposure level:
●Minimum reported exposure●Maximum reported exposure●Reported units of measured exposuresTiming of outcome assessment:
●The timing of outcome assessment according to study authors will be captured as free text and will also be further categorized as:●Pregnancy●Birth −1 years of age●>1–3 years of age●>3–12 years of age●>12–20 years of age●>20 years of age
|Animal study elements||Animal subjects:|
●Species – species will be categorized as follows, with controlled additions allowed as needed:○Daphnia○Monkey○Mouse○Rat○Frog○Fish●Strain – will be captured as free textStudy population sex:
●The study N will be collected as free text for the range of N from different experimental groups assessed throughout the studyTiming of exposure:
●The timing of exposure according to study authors will be captured as free text and will also be further categorized as:●For rodents:○Gestational○Postnatal (for rodents postnatal day (PND)0-PND14)○Developmental (gestational+postnatal)○Juvenile (for rodents PND15–40)○Adult (for rodents PND41+)●For zebrafish:○Embryonic (hpf 0–72)○Larval (hpf 72–30 days)○Adult (>30 days)●For other model systems:○Will develop as needed with expert consultationRoute of exposure:
●The exposure assessment method as described by the study authors will be categorized as follows, with controlled additions allowed as needed:●Inhalation●Intraperitoneal injection●Embryonic injection (e.g. zebrafish, xenopus)●Subcutaneous: injection●Subcutaneous: mini osmotic pump●Subcutaneous: silastic capsule●Oral: drinking water●Oral: gavage●Oral: feed/diet/treat●In treatment water (e.g. zebrafish, xenopus)●Dermal●OcularExposure assessment:
●When relevant (i.e. observational animal studies), the exposure assessment method as described by the study authors will be categorized as follows, with controlled additions allowed as needed:●Adipose tissue●Amniotic fluid●Breast milk●Cord blood●Feces●Hair●Nails●Serum●Urine●Whole blood●Whole organismExposure/dose range:
●Minimum reported exposure/dose●Maximum reported exposure/dose●Reported units of measured exposures/doseTiming of assessment:
●The timing of outcome assessment according to study authors will be captured as free text and will also be further categorized as:●For rodents:○Gestational○Postnatal (for rodents PND0-PND14)○Juvenile (for rodents PND15–40)○Adult (for rodents PND41+)●For zebrafish:○Embryonic (hpf 0–72)○Larval (hpf >72–30 days)○Adult (>30 days +)●For other model systems:○Will develop as needed with expert consultation
|In vitro study elements||Cell species:|
●Cell species will be categorized as follows, with controlled additions allowed as needed:●Chicken●E. coli●Frog●Guinea pig●Hampster●Human●Mouse●Rabbit●Rat●Yeast●ZebrafishCell line name:
●Example cell line names are provided below. Controlled additions to this list will be allowed as needed:●3T3L-1●BG-1●CHO●COS-7●DT40●GH3●H295R●HeLa●HepaRG●HepG2●Ishikawa●MCF-7●MDA-kb2●NIH3T3●PC3●PZFH●U2OS●ZLFCell type:
●Example cell types are provided below. Controlled additions to this list will be allowed as needed:●Leukocytes●Oocytes●Neuronal●Kidney●Breast cancer●Normal breastExposure timing:
●The range of exposure lengths used for the various experiments in a study will be recorded as free-text.Endpoint description:
●In vitro endpoints will be broadly categorized. Examples of broad categories are provided below. Controlled additions to this list will be allowed as needed:●Estrogen related●Androgen related●Thyroid related●Glucocorticoid related●Peroxisome proliferator activated receptor (PPAR) related●Cell and molecular dysfunction (e.g. oxidative stress)Dose range:
●Minimum reported dose●Maximum reported dose●Reported units of measured exposures
2.7. Data mapping method
Studies will be collated by evidence stream, PFAS studied, and health outcome. The systematic evidence map will be hosted on TEDX’s public profile on Tableau Public, which is available at https://public.tableau.com/profile/the.endocrine.disruption.exchange#!/. An example of how the data will be presented in shown in Fig. 2.
The display in Tableau Public will be an interactive evidence map that contains an evidence map as shown in Fig. 2, a list of all included studies, and a filter to limit the display based on evidence stream. In the freely available, online interactive display, it will be possible to filter the data to only see the studies for selected evidence streams, health outcome categories or chemicals. Users will be able to easily identify papers of interest by clicking on one of the colored circles to see a list of only those papers evaluating that specific PFAS and health outcome category. Users will be able to find additional study details (e.g. timing of exposure and outcome assessment, conflict of interest statement, etc.) and read the abstract by hovering over the name of the study in the study list. Further, clicking on a study of interest will take the user directly to the PubMed entry (or the entry on the publisher’s page if the paper is not in PubMed).
2.8. Study quality assessment
Study quality will not be assessed in this systematic evidence map.
2.9. Synthesis of results
Results of this systematic evidence map will be summarized narratively and prepared as a manuscript for peer review. We anticipate discussing the overall results of the literature search (to be described in the study flow diagram, Fig. 1) and providing an analysis of the trends in PFAS publications by year. A list/lists of studies that investigate aspects of PFAS other than health outcomes (i.e. environmental detection, environmental fate and transport, biomonitoring, detection in wildlife, reports on the ADME/PK/TK, in silico and read across analyses, reviews, and systematic reviews) for the 29 PFAS of interest may be made available upon request or as a downloadable list on the TEDX website (www.tedx.org). The human evidence will be discussed in terms of chemicals evaluated to-date, the frequency of use of different study types and locations of the studies, the frequency of use and timing of various exposure assessments, the ranges of reported exposures and the different health outcomes evaluated to-date. The animal evidence will be discussed similarly but separately for observational studies and experimental studies, and will include a discussion on the chemicals studied to-date, the frequency of study of different species, and different experimental aspects including the timing, route, and level of exposure and health outcomes evaluated. The in vitro evidence will be discussed in terms of the chemicals and exposure levels studied to-date, the cell or model systems used, and different types of questions addressed by the in vitro studies.
Financial support for this work was provided by the Arkansas Community Foundation, Winslow Foundation, Marisla Foundation and Tides Foundation. TAMW is financially supported by the Centre for Global Eco-Innovation (a programme funded by the European Regional Development Agency) and Yordas Group, a consultancy based at Lancaster University. AR is employed by the Natural Resources Defense Council, a nonprofit environmental advocacy group.
The funders had no role in the design and conduct of the study; collection, management, analysis, and interpretation of the data; preparation, review, or approval of the manuscript; and decision to submit the manuscript for publication.
KEP and CFK conceived the protocol. KEP, AR, TAMW scoped the project and wrote the first draft. KEP, AR, TAMW, CFK reviewed and revised the protocol for submission and in response to reviewer requests.
Thank you to Paul Whaley for helpful conversations about systematic evidence maps, to Michele Dedeo for helpful conversations regarding search terminology, to Michelle Angrish for helpful conversations about health outcome ontologies, and Keshia Rose from Tableau Service Corps for guidance on creating the interactive web browser.
Declaration of Competing Financial Interests
The authors declare they have no actual or potential competing financial interests.
Appendix A. Supplementary data
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Appendix A. Search strings for PubMedDownload : Download Acrobat PDF file (792KB)
PRISMA-P Report (modified) for Systematic Map Protocols Submitted to Environment International
ATSDR (Agency for Toxic Substances and Disease Registry), 2018ATSDR (Agency for Toxic Substances and Disease Registry)Toxicological Profile for Perfluoroalkyls (Draft for Public Comment)Department of Health and Human Services, Public Health Service (2018)https://www.atsdr.cdc.gov/toxprofiles/tp.asp?id=1117&tid=237, Accessed 2nd Nov 2018Google ScholarBlum et al., 2015A. Blum, S.A. Balan, M. Scheringer, X. Trier, G. Goldenman, I.T. Cousins, M. Diamond, T. Fletcher, C. Higgins, A.E. Lindeman, G. Peaslee, P. de Voogt, Z. Wang, R. WeberThe Madrid statement on poly- and perfluoroalkyl substances (PFASs)Environ. Health Perspect., 123 (2015), pp. A107-A111View Record in ScopusGoogle ScholarBowman, 2015J.S. BowmanFluorotechnology is critical to modern life: the FluoroCouncil counterpoint to the Madrid statementEnviron. Health Perspect., 123 (2015), pp. A112-A113Google ScholarCDC (Centers for Disease Control and Prevention), 2018CDC (Centers for Disease Control and Prevention)Fourth National Report on Human Exposure to Environmental Chemicals Updated Tables, March 2018https://www.cdc.gov/exposurereport/pdf/fourthreport_updatedtables_volume1_mar2018.pdf (2018), Accessed 20th Jan 2019Google ScholarCollaboration for Environmental Evidence, 2018Collaboration for Environmental EvidenceGuidelines and Standards for Evidence Synthesis in Environmental Managementwww.environmentalevidence.org/information-for-authors (2018), Accessed 9th Jan 2019Google ScholarCordner et al., 2019A. Cordner, V.Y. De La Rosa, L.A. Schaider, R.A. Rudel, L. Richter, P. BrownGuideline levels for PFOA and PFOS in drinking water: the role of scientific uncertainty, risk assessment decisions, and social factorsJ. Expo. Sci. Environ. Epidemiol., 29 (2019), pp. 157-171CrossRefView Record in ScopusGoogle ScholarDong et al., 2009G.H. Dong, Y.H. Zhang, L. Zheng, W. Liu, Y.H. Jin, Q.C. HeChronic effects of perfluorooctanesulfonate exposure on immunotoxicity in adult male C57BL/6 miceArch. Toxicol., 83 (2009), pp. 805-815CrossRefView Record in ScopusGoogle ScholarElsevier, 2017ElsevierGuidance notes for authors of systematic reviews, systematic maps and other related manuscriptsElsevier, https://www.elsevier.com/journals/environment-international/0160-4120/guidance-notes (2017), Accessed 9th Jan 2019Google ScholarGrandjean, 2018P. GrandjeanDelayed discovery, dissemination, and decisions on intervention in environmental health: a case study on immunotoxicity of perfluorinated alkylate substancesEnviron. Health, 17 (2018), p. 62Google ScholarGrandjean and Budtz-Jorgensen, 2013P. Grandjean, E. Budtz-JorgensenImmunotoxicity of perfluorinated alkylates: calculation of benchmark doses based on serum concentrations in childrenEnviron. Health, 12 (2013), p. 35Google ScholarGuruge et al., 2006K.S. Guruge, L.W. Yeung, N. Yamanaka, S. Miyazaki, P.K. Lam, J.P. Giesy, P.D. Jones, N. YamashitaGene expression profiles in rat liver treated with perfluorooctanoic acid (PFOA)Toxicol. Sci., 89 (2006), pp. 93-107CrossRefView Record in ScopusGoogle ScholarJames et al., 2016K.L. James, N.P. Randall, N.R. HaddawayA methodology for systematic mapping in environmental sciencesEnviron. Evid., 5 (2016)Google ScholarMacon et al., 2011M.B. Macon, L.R. Villanueva, K. Tatum-Gibbs, R.D. Zehr, M.J. Strynar, J.P. Stanko, S.S. White, L. Helfant, S.E. FentonPrenatal perfluorooctanoic acid exposure in CD-1 mice: low-dose developmental effects and internal dosimetryToxicol. Sci., 122 (2011), pp. 134-145CrossRefView Record in ScopusGoogle ScholarMDHHS (Michigan Department of Health and Human Services), 2019MDHHS (Michigan Department of Health and Human Services). Public Health Drinking Water Screening Levels for PFAS https://www.michigan.gov/documents/pfasresponse/MDHHS_Public_Health_Drinking_Water_Screening_Levels_for_PFAS_651683_7.pdf (accessed 10 April 2019). Division of Environmental Health 2019.Google ScholarMiake-Lye et al., 2016I.M. Miake-Lye, S. Hempel, R. Shanman, P.G. ShekelleWhat is an evidence map? A systematic review of published evidence maps and their definitions, methods, and productsSyst. Rev., 5 (2016), p. 28Google ScholarNC State Center for Human Health and the Environment, 2018aNC State Center for Human Health and the Environment. The GenX Exposure Study. https://chhe.research.ncsu.edu/the-genx-exposure-study/ (accessed 22 January 2019). North Carolina State University; 2018a.Google ScholarNC State Center for Human Health and the Environment, 2018bNC State Center for Human Health and the EnvironmentGenX Exposure Study: PFAS Blood Sample Resultshttps://chhe.research.ncsu.edu/wordpress/wp-content/uploads/2018/11/Community-event-BLOOD-slides.pdf (2018), Accessed 22nd Jan 2019Google ScholarNHDES (New Hampshire Department of Enviornmental Services), 2019NHDES (New Hampshire Department of Enviornmental Services)Summary report on the New Hampshire Department of Environmental Services development of maximum contaminant levels and ambient groundwater quality standards for perfluorooctanesulfonic acid (PFOS), perfluorooctanoic acid (PFOA), perfluorononanoic acid (PFNA), and perfluorohexanesulfonic acid (PFHxS)https://www.des.nh.gov/organization/commissioner/pip/publications/documents/r-wd-19-01.pdf (2019), Accessed 4th Apr 2019Google ScholarNJDWQI (New Jersey Drinking Water Quality Institute), 2018NJDWQI (New Jersey Drinking Water Quality Institute)Maximum Contaminant Level Recommendation for Perfluorooctane Sulfonate in Drinking Waterhttps://www.state.nj.us/dep/watersupply/pdf/pfos-recommendation-summary.pdf (2018), Accessed 26th Oct 2018Google ScholarNJDWQI, 2017NJDWQIMaximum Contaminant Level Recommendation for Perfluorooctanoic Acid in Drinking Waterhttps://www.nj.gov/dep/watersupply/pdf/pfoa-recommend.pdf (2017), Accessed 26th Oct 2018Google ScholarNTP (National Toxicology Program), 2016NTP (National Toxicology Program). Monograph on Immunotoxicity Associated with Exposure to Perfluorooctanoic Acid (PFOA) and Perfluorooctane Sulfonate (PFOS). Office of Health Assessment and Translation. Research Triangle Park, NC: National Toxicology Program; https://ntp.niehs.nih.gov/ntp/ohat/pfoa_pfos/pfoa_pfosmonograph_508.pdf (accessed 5 November 2018). 2016.Google ScholarPeden-Adams et al., 2008M.M. Peden-Adams, J.M. Keller, J.G. Eudaly, J. Berger, G.S. Gilkeson, D.E. KeilSuppression of humoral immunity in mice following exposure to perfluorooctane sulfonateToxicol. Sci., 104 (2008), pp. 144-154CrossRefView Record in ScopusGoogle ScholarPelch et al., 2019Pelch, K.E.; Reade, A.; Wolffe, T.; Kwiatkowski, C.F. PFAS Health Database: A Protocol for a Systematic Evidence Map. https://zenodo.org/record/2832470#.XNt2Lo5Ki70 (accessed 14 May 2019). Zenodo; 2019.Google ScholarScheringer et al., 2014M. Scheringer, X. Trier, I.T. Cousins, P. de Voogt, T. Fletcher, Z. Wang, T.F. WebsterHelsingor statement on poly- and perfluorinated alkyl substances (PFASs)Chemosphere, 114 (2014), pp. 337-339ArticleDownload PDFView Record in ScopusGoogle ScholarShoemaker et al., 2018J.A. Shoemaker, D.R. TettenhorstDevelopment O.o.R.a (Ed.), Method 537.1: Determination of Selected per- and Polyflrorinated Alkyl Substances in Drinking Water by Solid Phase Extraction and Liquid Chromatography/Tandem Mass Spectrometry (LC/MS/MS) (2018)Cincinnati, OHGoogle ScholarTucker et al., 2015D.K. Tucker, M.B. Macon, M.J. Strynar, S. Dagnino, E. Andersen, S.E. FentonThe mammary gland is a sensitive pubertal target in CD-1 and C57Bl/6 mice following perinatal perfluorooctanoic acid (PFOA) exposureReprod. Toxicol., 54 (2015), pp. 26-36ArticleDownload PDFView Record in ScopusGoogle ScholarUS EPA, 2006US EPAPFOA Stewardship Program. Risk Management for Per- and Polyfluoroalkyl Substances (PFASs) under TSCAUnited States Environmental Protection Agency (2006)https://www.epa.gov/assessing-and-managing-chemicals-under-tsca/risk-management-and-polyfluoroalkyl-substances-pfass#tab-3, Accessed 27th Apr 2019Google ScholarUS EPA (United States Environmental Protection Agency), 2016aUS EPA (United States Environmental Protection Agency)Drinking Water Health Advisory for Perfluorooctane Sulfonate (PFOS)Office of Water, Washington, D.C. (2016)https://www.epa.gov/sites/production/files/2016-05/documents/pfos_health_advisory_final_508.pdf, Accessed 20th Jan 2019Google ScholarUS EPA, 2016bUS EPADrinking Water Health Advisory for Perfluorooctanesulfonate (PFOS)Office of Water, Washington DC (2016)https://www.epa.gov/sites/production/files/2016-05/documents/pfos_health_advisory_final-plain.pdf, Accessed 8th Jan 2019Google ScholarUS EPA, 2016cUS EPADrinking Water Health Advisory for Perfluorooctanoic Acid (PFOA)Office of Water, Washington DC (2016)https://www.epa.gov/sites/production/files/2016-05/documents/pfoa_health_advisory_final-plain.pdf, Accessed 8th Jan 2019Google ScholarUS EPA, 2018aUS EPAToxicity Assessment: Human Health Toxicity Values for Hexafluoropropylene Oxide (HFPO) Dimer Acid and its Ammonium Salt (CASRN 13252-13-6 and CASRN 62037-80-3)Office of Water, Washington DC (2018)https://www.epa.gov/sites/production/files/2018-11/documents/genx_public_comment_draft_toxicity_assessment_nov2018-508.pdf, Accessed 10th Jan 2019Google ScholarUS EPA, 2018bUS EPAToxicity Assessment: Human Health Toxicity Values for Perfluorobutane Sulfonic Acid (CASRN 375-73-5) and Related Compound Potassium Perfluorobutane Sulfonate (CASRN 29420-49-3)Office of Water, Washington DC (2018)https://www.epa.gov/sites/production/files/2018-11/documents/pfbs_public_comment_draft_toxicity_assessment_nov2018-508.pdf, Accessed 10th Jan 2019Google ScholarUS EPA, n.dUS EPA. Basic Information on PFAS. PFOA, PFOS and Other PFASs: United States Environmental Protection Agency https://www.epa.gov/pfas/basic-information-pfas (accessed 27 April 2019).Google ScholarUS NLM (United States National Library of Medicine), 2016US NLM (United States National Library of Medicine). Unified Medical Language System (UMLS). Bethesda, MD: United States National Library of Medicine; https://www.nlm.nih.gov/research/umls/ (accessed 10 January 2019). 2016.Google ScholarWhite et al., 2011S.S. White, J.P. Stanko, K. Kato, A.M. Calafat, E.P. Hines, S.E. FentonGestational and chronic low-dose PFOA exposures and mammary gland growth and differentiation in three generations of CD-1 miceEnviron. Health Perspect., 119 (2011), pp. 1070-1076CrossRefView Record in ScopusGoogle Scholar© 2019 The Authors. Published by Elsevier Ltd.