Evidence map›Paper›PMID 26732820›Full record

ArticleThe Annals of occupational hygiene2016

Combining Decision Rules from Classification Tree Models and Expert Assessment to Estimate Occupational Exposure to Diesel Exhaust for a Case-Control Study.

Melissa C Friesen, David C Wheeler, Roel Vermeulen, Sarah J Locke, Dennis D Zaebst, Stella Koutros, Anjoeka Pronk, Joanne S Colt, Dalsu Baris, Margaret R Karagas and 8 more

Abstract read
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Article in The Annals of occupational hygiene, 2016. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 9 papers.

0numbers the graph read from it
0cells of the map it votes in
9citing papers in PubMed
–field-weighted citation impact
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

9 citing papers in PubMed.

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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

18 authors.

Melissa C Friesen1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA; friesenmc@mail.nih.gov.
David C Wheeler2.Department of Biostatistics, Virginia Commonwealth University, Richmond, VA 23298, USA;
Roel Vermeulen3.Institute for Risk Assessment Sciences, Utrecht University, Utrecht, The Netherlands;
Sarah J Locke1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA;
Dennis D Zaebst4.Westat, Rockville, MD 20850, USA;
Stella Koutros1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA;
Anjoeka Pronk5.TNO, 3700 Zeist, The Netherlands;
Joanne S Colt1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA;
Dalsu Baris1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA;
Margaret R Karagas6.Geisel School of Medicine at Dartmouth, Hanover, NH 03756, USA;
Nuria Malats7.Genetic and Molecular Epidemiology Group, Spanish National Cancer Research Center (CNIO), 28029 Madrid, Spain;
Molly Schwenn8.Maine Cancer Registry, Augusta, ME 04333-0011, USA;
Alison Johnson9.Vermont Cancer Registry, Burlington, VT 05402-0070, USA;
Karla R Armenti10.New Hampshire Department of Health and Human Services, Division of Public Health Services, Bureau of Public Health Statistics and Informatics, Concord, NH 03301, USA;
Nathanial Rothman1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA;
Patricia A Stewart11.Stewart Exposure Assessments LLC, Arlington, VA 22207, USA;
Manolis Kogevinas12.Centre for Research in Environmental Epidemiology (CREAL), 08003 Barcelona, Spain; 13.CIBER Epidemiología y Salud Pública (CIBERESP), 28029 Barcelona, Spain; 14.IMIM (Hospital del Mar Medical Research Institute), 08003 Barcelona, Spain;
Debra T Silverman1.Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, MD 208952, USA;

Funding

Occupational Exposure AssessmentZIACP010122 · NCI · DIVISION OF CANCER EPIDEMIOLOGY AND GENETICS · PI FRIESEN, MELISSA · 2009 to 2025
$8.6M
Intramural NIH HHS
6 · The paper itself

Abstract

objectivesTo efficiently and reproducibly assess occupational diesel exhaust exposure in a Spanish case-control study, we examined the utility of applying decision rules that had been extracted from expert estimates and questionnaire response patterns using classification tree (CT) models from a similar US study.

methodsFirst, previously extracted CT decision rules were used to obtain initial ordinal (0-3) estimates of the probability, intensity, and frequency of occupational exposure to diesel exhaust for the 10 182 jobs reported in a Spanish case-control study of bladder cancer. Second, two experts reviewed the CT estimates for 350 jobs randomly selected from strata based on each CT rule's agreement with the expert ratings in the original study [agreement rate, from 0 (no agreement) to 1 (perfect agreement)]. Their agreement with each other and with the CT estimates was calculated using weighted kappa (κ w) and guided our choice of jobs for subsequent expert review. Third, an expert review comprised all jobs with lower confidence (low-to-moderate agreement rates or discordant assignments, n = 931) and a subset of jobs with a moderate to high CT probability rating and with moderately high agreement rates (n = 511). Logistic regression was used to examine the likelihood that an expert provided a different estimate than the CT estimate based on the CT rule agreement rates, the CT ordinal rating, and the availability of a module with diesel-related questions.

resultsAgreement between estimates made by two experts and between estimates made by each of the experts and the CT estimates was very high for jobs with estimates that were determined by rules with high CT agreement rates (κ w: 0.81-0.90). For jobs with estimates based on rules with lower agreement rates, moderate agreement was observed between the two experts (κ w: 0.42-0.67) and poor-to-moderate agreement was observed between the experts and the CT estimates (κ w: 0.09-0.57). In total, the expert review of 1442 jobs changed 156 probability estimates, 128 intensity estimates, and 614 frequency estimates. The expert was more likely to provide a different estimate when the CT rule agreement rate was <0.8, when the CT ordinal ratings were low to moderate, or when a module with diesel questions was available.

conclusionsOur reliability assessment provided important insight into where to prioritize additional expert review; as a result, only 14% of the jobs underwent expert review, substantially reducing the exposure assessment burden. Overall, we found that we could efficiently, reproducibly, and reliably apply CT decision rules from one study to assess exposure in another study.

Indexed as

Models, TheoreticalAir Pollutants, OccupationalCase-Control StudiesDecision Support TechniquesEnvironmental MonitoringHumansLogistic ModelsOccupational ExposureReproducibility of ResultsSpainVehicle EmissionsAir Pollutants, OccupationalVehicle Emissionscase-controldiesel exhaustexposure assessment methodologyoccupational exposurestatistical learning

Identifiers

PMID26732820
PMCPMC4850897

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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.