1. Alignment of tools for workplace exposure assessment

IOHA 2018 Washington: Progress in the alignment of control banding tools

AIHCe 2017 Seattle: Testing Hazard Banding Performance and Strength

BOHS OH2017 Harrogate: Filling the OELV gap: Optimise Hazard Banding

NVvA Conference 2017: The alignment of parallel OH tools. An IOHA project?

IOHA 2015 Conference: The need for international alignment of Occupational Hygiene tools

2. Exposure assessment, variability and control

2024

The IOHA2024 Basic Characterisation PDC (Dublin 9 June). Download the zip-files with handouts and the Excel application IH-Aligner.
IH-Aligner is an Excel tool to process and export results of PAS measurements performed within a Similar Exposure Group (SEG) or an Exposure Scenario (ES). It performs the arithmetic adjustment of measurement results to the correct time-weighted average (TWA) matching with the OELV reference period. Furthermore, tests are performed on the goodness-of-fit (log)normality of the TWA set and several UTL95%,## calculated for testing compliance. The main benefit is that measurement results are converted into a format that can be imported (copied and pasted) into most freely available statistical programmes used in occupational hygiene. The use of IH-Aligner is free of charge. However, we would welcome feedback.

IOHA2024 Dublin 13 June. on the Rehab of measurement uncertainty in compliance testing.

2022

NYF 2022 EN689 Conference. OELV compliance decisions and the EN689 preliminary test.

If the 95% percentile (C95%) of a log-normal shaped exposure distribution is around the Occupational Exposure Limit Value (OELV) and PAS measurements are taken within a SEG to test compliance with the OELV, then the EN689 5.5.2 preliminary test can unnecessarily delay compliance decisions and is less cost-effective for employers compared to the EN689 5.5.3 statistical test, which measures with 70% confidence whether fewer than 5% of exposures in the SEG exceed the OELV (C95,70% > OELV). The preliminary test decision schedule also underestimates workers' health risk and delays necessary control measures for GSD greater than 6.

2018

IOHA 2018 Conference. Towards a library of exposure profile related GSD values

Occupational exposure assessment is normally characterised by measurement series with small sample sizes, compared with other quality-control areas such as environmental monitoring and product safety. A library of SEG or exposure profile (EN689 3.1) specific GSDs may support the appraiser (the EN689 synonym for assessor) to test the confidence of their sample GSD (is it too small or too large for the SEG examined) when six or fewer PAS measurements are available. Such a library provides scientists with a tool to make their Bayesian compliance testing methods more credible. Existing GSD info already debunks existing, historical myths that the long-term GSD must be smaller than 3 (IHSTat).

2017

NVvA Conference 2017 Ioannidis and do individuals performing the same job have different average exposures?

The pressure to publish and use only positive and 'significant' findings in OELV limit setting and exposure modelling drives journals and researchers to rearrange or reject data, support unvalidated methods, and selectively cite publications regardless of their validity or relevance. Institutes and journals in occupational exposure sciences should be transparent (make raw data available) and work according to the codes on research integrity.

2016

SOPHYT Forum (Lille). Statistics and representative measurements

Scheme prEN 689 (2016) compliance testing

BOHS prEN 689 workshop (Glasgow). Representative measurements and exposure variability within the SEG

2015

CEN137 TC1 (Paris). Identifying exceptional exposure within a SEG using Student-t/ANOVA statistical tests

AEHI Seminario (Barcelona). The new CEN 689 Compliance testing guidance

CEN137 TC1 (Delft). Lognormality and the handling of non-detects

IOHA BW_Stat PDC (London). Basic Characterisation

IOHA BW_Stat PDC (London). Compliance testing

2014

Deutsche Gesellschaft fuer Arbeitshygiene. BW_Statv1.xlsx The Excel tool for the BOHS-NVvA compliance testing guidance.

2013

BOHS Conference (Manchester). Between-worker differences and sampling strategy flaws

2011

BOHS-NVvA Compliance testing guidance

2001

NVvA Guidance on exposure data recording

Long-term exposure sampling at a Dutch (bio)chemical production site

2000

The distribution of long-term GSDs in well-defined chemical industry SEGs in Dutch, English PPT

1999

8-hour TWA OELV for chronic toxic chemical substances based on long-term NOEL or DNELS (in Dutch, English summary)

On the compliance control of long-term OELVs. Vinyl chloride monomer (in Dutch, English summary)

WEEL Committee. Workplace Environmental Exposure Levels (OARS WEELs). Melamine. American Industrial Hygiene Association. Fairfax Virginia 1999.

1996

Occupational Exposure Database core information

1994

Letter to the editor on methodological flaws in the analysis of within and between worker variability

1991

HYGINIST: Compliance testing software for workplace exposure within a Similar Exposure Group (SEG) with goodness-of-fit, regression-based handling of non-detects, comparing sample GM and GSD with priors, and optimising sample size.

1984

Maintenance painters solvent exposure assessment and effect-specific OELV

1980

Tetrachloroethylene in exhaled air of residents near dry-cleaning shops

3. Occupational Exposure Limits (holistic, DN/MEL, Kick-off, Hazard Banding and their hierarchy)

2016

Scientific publication On the Strength and Validity of Hazard Banding and its supplementary data

NVvA Conference presentation (Scheveningen). Testing strength and validity of Hazard Band engines

2015

IOHA Conference (London). Finding best performing hazard band engines within Control Banding tools

2014

AIHCe (San Antonio). Validation of health hazard grouping in Control Banding

AIHCe (San Antonio). Kick-off limits. For substances with no OELV/DNEL, but with GHS/CLP classification

Estimating the vapour pressure and the OELV for compliance testing of complex solvent mixtures using XLUNIFAC (BOHS conference 2014 Nottingham).

BOHS Poster (Nottingham). A hierarchy of OELVs

Presentation H3##-statement based kick-off levels. Bilthoven NVT-AT 140925

Careful with that DNEL, Occupational Hygienist! A quantitative comparison with higher hierarchy OELVs

2006

DOHSBase-Compare: ranking inhalation risk potential of chemicals for substitution purposes (in Dutch)

2005

Publication R-phrase based Kick-off levels (in Dutch, English summary)

1992-today

Dohsbase, a comprehensive database with hierarchical information on phys-chem, health hazard info, OELVs, sampling methods and risk ranking of chemicals used in the workplace.

4. Occupational health and epidemiology

2005

Benzene and Leukemia.

A retrospective cohort study among 311 Dutch workers employed in a HSO/Caprolactam production facility exposed to pure benzene (IARC Group 1 carcinogen) between 1951 and 1968.

Observations and analysis: 1% lost to follow-up. Mortality 39%. Overall Standardized Mortality Ratio (SMR) 85.9% (95% CI: 71.3-102.6%).

Of 275 cohort members, exposure could be quantified, resulting in 43,725 ppm-years.

One leukaemia case (non-acute myeloid) was observed in the second of three exposure categories, compared with 1.17 expected.

3.3 and 7.5 Additional leukaemia cases predicted by extreme benzene risk models (Austin, 1988 ; Rinsky, 1981) were rejected with probabilities due to chance of 0.03 and 0.0001 respectively.

Conclusion: The absence of leukaemia excess deaths in this cohort with long-term benzene exposure levels of 0.5-20 ppm per day, 159 ppm-years (520 mg/m3-years) per worker on the average, is consistent with the ECHA/RAC (2018) mode-of-action-based threshold approach for benzene-induced leukaemia.

Strengths: a well-defined industrial cohort with stable employment, lower overall mortality, and pure benzene exposure. A predefined research protocol and separated assessment of individual exposure and cause of death reduce the risk of observer bias, data dredging and post hoc manipulation of the dose-response.

The relatively high baseline health status, access to healthcare and lifestyle factors in the wealthy coal area in the Netherlands may have contributed to differences in observed risk estimates compared to other benzene cohorts.

Limitations: the cause of death was unknown for 5 of the 121 deaths, and cumulative exposure data were unavailable for 36 workers.

Noteworthy finding: a statistically significant excess of brain tumours was observed (6 cases versus 0.95 expected), a finding that has also been reported in industrial cohorts from countries with developed healthcare systems.

1998

Update Acrylonitrile cohort study

1992

Mortality of Workers exposed to Acrylonitrile

1991

Mortality of coke plant workers in the Netherlands

1984

Mortality among laboratory assistants in a Coke plant [1928-1946] (in Dutch, English summary). The first properly conducted retrospective occupational cohort study in the Netherlands.