Evidence map›Paper›PMID 29689464›Full record

ArticleEnvironment international2018

Children's residential exposure to organophosphate ester flame retardants and plasticizers: Investigating exposure pathways in the TESIE study.

Allison L Phillips, Stephanie C Hammel, Kate Hoffman, Amelia M Lorenzo, Albert Chen, Thomas F Webster, Heather M Stapleton

Open access · greenAbstract read
In one paragraph

Article in Environment international, 2018. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 55 papers.

0numbers the graph read from it
0cells of the map it votes in
55citing papers in PubMed
11.0field-weighted citation impact, top 1% of its field
1 · What the graph read from it

What it found

Each row is one number read from the abstract, on the scale the paper reported it, with its interval. Left of the dashed line favours the treatment, right favours the comparator. Under each row is the sentence it came from. New to these charts? A ten-minute tutorial.

The abstract states no effect estimate the extractor could read, or names no intervention and outcome on the map, so this paper lights no cell and moves no belief. It is still indexed, cited and linked below.

2 · The registry

The trial behind it

Trials whose registry record cites this paper, or whose number appears in the abstract. A trial that started after this paper was published is citing it as background, not reporting it.

Neither the registry nor the abstract names a trial number. If this is a trial report, that itself is worth knowing.

3 · Its place in the literature

Who cites it

55 citing papers in PubMed, 157 citations in OpenAlex.

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  11. Children's exposure to brominated flame retardants in the home: The TESIE study.Environmental pollution (Barking, Essex : 1987) · 2024
    Article
  12. Article
  13. Patterns of urinary organophosphate ester metabolite trajectories in children: the HOME Study.Journal of exposure science & environmental epidemiology · 2024
    Article
  14. Article
  15. Investigation ofCurrent research in toxicology · 2024
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4 · The record

Corrections and comments

PubMed lists nothing against this paper. Absence here is not a guarantee, only a check that was made.

5 · Who and what money

Authors and funding

7 authors at 2 institutions in 1 country.

Allison L PhillipsNicholas School of the Environment, Duke University, Durham, NC, United States. Electronic address: allison.l.phillips@duke.edu.
Stephanie C HammelNicholas School of the Environment, Duke University, Durham, NC, United States. Electronic address: stephanie.hammel@duke.edu.
Kate HoffmanNicholas School of the Environment, Duke University, Durham, NC, United States. Electronic address: kate.hoffman@duke.edu.
Amelia M LorenzoNicholas School of the Environment, Duke University, Durham, NC, United States. Electronic address: amelia.lorenzo@duke.edu.
Albert ChenNicholas School of the Environment, Duke University, Durham, NC, United States.
Thomas F WebsterBoston University School of Public Health, Boston University, Boston, MA, United States. Electronic address: twebster@bu.edu.
Heather M StapletonNicholas School of the Environment, Duke University, Durham, NC, United States. Electronic address: heather.stapleton@duke.edu.
Duke University · USBoston University · US

Funding

Zebrafish as a Detector of Organophosphate ExposureP42ES010356 · NIEHS · DUKE UNIVERSITY · PI AMY H HERRING · 2000 to 2026
$56.2M
Children's Exposure to Flame Retardants: Effects on Thyroid Hormone RegulationR01ES016099 · NIEHS · DUKE UNIVERSITY · PI STAPLETON, HEATHER M · 2008 to 2017
$5.0M
Duke University Program in Environmental HealthT32ES021432 · NIEHS · DUKE UNIVERSITY · PI Akhenaton-Andrew Dhafir Jones, Joel Newman Meyer · 2013 to 2026
$4.0M
NIEHS NIH HHS P42 ES010356NIEHS NIH HHS R01 ES016099NIEHS NIH HHS T32 ES021432
6 · The paper itself

Abstract

backgroundFollowing the phase-out of polybrominated diphenyl ethers (PBDEs), organophosphate esters (OPEs) have been increasingly used in consumer products and building materials for their flame retardant and plasticizing properties. As a result, human exposure to these chemicals is widespread as evidenced by common detection of their metabolites in urine. However, little is known about the major exposure pathways, or factors that influence children's exposure to OPEs. Furthermore, little data is available on exposure to the novel aryl OPEs.

objectivesTo examine predictors of children's internal exposure, we assessed relationships between OPEs in house dust and on hand wipes and levels of their corresponding metabolites in paired urine samples (n = 181). We also examined associations between urinary metabolites and potential covariates, including child's age and sex, mother's educational attainment and race, and average outdoor air temperature.

methodsChildren aged 3 to 6 years provided urine and hand wipe samples. Mothers or legal guardians completed questionnaires, and a house dust sample was taken from the main living area during home visits. Alkyl chlorinated and aryl OPEs were measured in dust and hand wipes, and composite urine samples were analyzed for several metabolites.

resultsTris(2-chloroethyl) phosphate (TCEP), tris(2-chloroisopropyl) phosphate (TCIPP), tris(1,3-dichloro-2-propyl) phosphate (TDCIPP), 2-ethylhexyl diphenyl phosphate (EHDPHP), triphenyl phosphate (TPHP), and 2-isopropylphenyl diphenyl phosphate (2IPPDPP) were detected frequently in hand wipes and dust (>80%), indicating that these compounds were near-ubiquitous in indoor environments. Additionally, bis(1-chloro-2-propyl) 1-hydroxy-2-propyl phosphate (BCIPHIPP), bis(1,3-dichloro-2-propyl) phosphate (BDCIPP), diphenyl phosphate (DPHP), mono-isopropyl phenyl phenyl phosphate (ip-PPP), and mono-tert-butyl phenyl phenyl phosphate (tb-PPP) were detected in >94% of tested urine samples, signifying that TESIE participants were widely exposed to OPEs. Contrary to PBDEs, house dust OPE concentrations were generally not correlated with urinary OPE metabolite levels; however, hand wipe levels of OPEs were associated with internal dose. For example, children with the highest mass of TDCIPP on hand wipes had BDCIPP levels that were 2.73 times those of participants with the lowest levels (95% CI: 1.67, 4.48, p < 0.0001). Of the variables examined, hand wipe level was the most consistent and strongest predictor of OPE urinary metabolite concentrations. Outdoor air temperature was also a significant predictor of urinary BDCIPP concentrations, with a 1 °C increase in temperature corresponding to a 4% increase in urinary BDCIPP (p < 0.0001).

conclusionsOPE exposures are highly prevalent, and data provided herein further substantiate hand-to-mouth contact and dermal absorption as important pathways of OPE exposure, especially for young children.

Indexed as

Environmental ExposureChildChild, PreschoolCohort StudiesFlame RetardantsHumansOrganophosphatesPlasticizersResidence CharacteristicsFlame RetardantsOrganophosphatesPlasticizers

Identifiers

PMID29689464
PMCPMC5980657
OpenAlexW2802652985

What OpenQuestion holds

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Registered trials

None linked

Read under generation 80e0d062 · epoch 390. Bibliography from PubMed, PubMed Central and OpenAlex; grants from NIH RePORTER; trial links from ClinicalTrials.gov; estimates, votes and beliefs from the OpenQuestion graph.