Examination of Permeation Resistance of Chemical Protective Gloves Made of Laminate-Film Materials Against Chemical Substances.

This study investigated the permeation resistance of chemical protective gloves made of laminate film comprising nylon, ethylene-vinyl alcohol copolymer (EVOH), and other materials against different chemical substances to examine their usability in different work processes. The permeation resistance of the chemical protective glove was tested using the Japanese Industrial Standards (JIS) test method against twelve substances: acetone, acetonitrile, dichloromethane, ethyl acetate, n-hexane, methanol, tetrahydrofuran, toluene, 2-propanol, 1-butanol, 1,4-diethylene dioxide, and ethanol. After 480 min, no substance, except for methanol and ethanol, permeated at a standard permeation rate of 0.1 µg/cm2/min. Methanol and ethanol showed permeation at 1 min and 30 min elapsed, respectively. Hence, the gloves tested in this study exhibited permeation resistance to various chemical substances, and can thus be used in many work processes. Some film materials have short permeation time against certain chemical substances, but the chemical protective gloves tested in this study can be used at work sites, such as manufacturing sites, that require permeation resistance to different chemical substances.

[Survey on Preparedness, Concerns, and Support Demands for Autonomous Management of Chemical Substances].

The management of workplace chemicals shifted from a regulatory-based to a self-managed approach as of April 2023. To assess readiness, concerns, and necessary support for this change, a free-response questionnaire survey was conducted for the participants of the "Promoting self-management of chemicals in enterprises" seminar held by the Department of Occupational Health, Graduate School of Medicine, University of Occupational and Environmental Health, Japan, in January-February 2023. Text-mining using KH Coder (Ver.3) was conducted to investigate relationships between words that appeared in sentences using a co-occurrence network and hierarchical cluster analysis. From the questionnaire's description text, combinations of the terms "information" and "collection," "small and medium-sized" and "enterprise," and "chemical" and "substance" were extracted. Results suggest a need for "information gathering" and "support for small and medium-sized enterprises."

Assessment of dermal exposure to N,N-dimethylacetamide in spray workers by combining personal exposure monitoring, biological monitoring, and glove permeation monitoring: A pilot study.

OBJECTIVES: We assessed dermal exposure to N,N-dimethylacetamide (DMAC) in a spray worker by utilizing a combination of personal exposure monitoring, biological monitoring, and glove permeation monitoring. We also determined the protective effects of chemical protective gloves (CPGs). METHODS: Surveys with and without CPG usage were performed on different days. In the survey with CPG usage, the worker had worn leather gloves over the CPG. Personal exposure monitoring and glove permeation monitoring were performed using 3M Organic Vapor Monitor 3500 and PERMEA-TEC Pads respectively. Urinary concentration of DMAC and its metabolites (N-methylacetamide [NMAC], N-hydroxymethyl-N-methylacetamide [DMAC-OH], S-(acetamidomethyl) mercapturic acid [AMMA]) were measured in the before-shift and end-of-shift samples collected from the worker. RESULTS: Personal exposure DMAC concentration in the survey with CPG usage (0.32 ppm) was twice that in the survey without CPG usage (0.15 ppm). However, urinary concentrations of DMAC-OH and AMMA in the end-of-shift samples in the survey with CPG usage (DMAC-OH, 0.74 mg/g creatinine; AMMA, 0.10 mg/g creatinine) were lower than those in the survey without CPG usage (DMAC-OH, 1.27 mg/g creatinine; AMMA, 0.24 mg/g creatinine). Urinary concentrations of DMAC and NMAC were below the limit of detection in all samples. DMAC concentrations in PERMEA-TEC Pads that were used in the surveys with and without CPG usage were in the range of 0.3-2.1 µg/sample and 16.4-1985.2 µg/sample respectively. CONCLUSIONS: The combination of CPG usage and leather gloves was effective in preventing dermal exposure to DMAC.

Simple and reliable method to simultaneously determine urinary 1- and 2-naphthol using in situ derivatization and gas chromatography-mass spectrometry for biological monitoring of naphthalene exposure in occupational health practice.

OBJECTIVES: The aim of this study was to develop and validate a simple and reliable gas chromatography-mass spectrometry (GC-MS) method to simultaneously determine urinary 1-naphthol (1-NAP) and 2-naphthol (2-NAP) for biological monitoring of occupational exposure to naphthalene. METHODS: NAPs were derivatized in situ with acetic anhydride after enzymatic hydrolysis, extracted with n-hexane, and analyzed using GC-MS. Validation of the proposed method was conducted in accordance with US Food and Drug Administration guidance. A final validation was performed by analyzing a ClinChek® -Control for phenolic compounds. RESULTS: The linearity of calibration curves was indicated by a high correlation coefficient (>0.999) in the concentration range 1-100 µg/L for each NAP. The limits of detection and quantification for each NAP were 0.30 and 1.00 µg/L, respectively. The recovery was 90.8%-98.1%. The intraday and interday accuracies, expressed as the deviation from the nominal value, were 92.2%-99.9% and 93.4%-99.9%, respectively. The intraday and interday precision, expressed as the relative standard deviation, was 0.3%-3.9% and 0.4%-4.1%, respectively. The ClinChek® values obtained using our method were sufficiently accurate. CONCLUSIONS: The proposed method is simple, reliable, and appropriate for routine analyses, and is useful for biological monitoring of naphthalene exposure in occupational health practice.

[Characteristics that Occupational Safety and Health Engineers Should Know Before Conducting Health and Safety Education for Workers with Developmental Disorders].

As a result of the amendment to the act on promotion of employment of persons with disabilities the statutory employment rate for handicapped people was raised from 2.0% to 2.2% in April 2018. By 2021, it will be raised again by 0.1% to 2.3%. The number of jobs for handicapped people has also been increasing recently, and it is predicted that the number of jobs for people with developmental disorders will also increase. From this perspective, it is predicted that occupational safety and health engineers, such as health officers, will have more opportunities to give safety and health education to workers with developmental disorders. People with developmental disorders have various characteristics that are different from those with an ordinary type of development, and occupational health and safety engineers need to understand their characteristics when providing education for them. This report summarizes the characteristics of people with developmental disorders that occupational safety and health engineers should know when educating them.

[Study on the Establishment of a Specific Similar Exposure Group (SEG) in Personal Exposure Monitoring: A Case Report of Indium Tin Oxide Target Surface Grinding Process].

Surface grinding workers of Indium Tin Oxide target material are exposed to an indium compound with high toxicity. We divided individual exposure workers into similar exposure groups (SEG) and examined the effectiveness of the classification of SEG. Sampling was carried out twice a day for a total of 10 times, in 9 of which a work environment measurement in unit work area was performed at the same time. The classification examined two methods. One method was to set all the workers in the work place as one group (SEG1), and the other was to classify them depending on whether the workers handled the target material contained indium or not (SEG2). The group handled indium-contained material was SEG2(+) n=9, and the other was SEG2(-) n=9. Only the arithmetic mean value (AM) of four groups 2.8-27.4 µg/m3 in the SEG2(+) was lower than the measurement B value of the work environment measurement, but the AM of all the groups in SEG2(+) 2.8-276.8 µg/m3 was higher than the geometric mean value of measurement A 0.4-12.3 µg/m3. The concentration range of 100 µg/m3 or more of SEG2(+) AM was 20% of the total. This range was not recognized in the other items, and the variation of SEG2(+) was small. Even though the evaluation of SEG1 is control class 2, if revaluated on SEG2(+), 50% of the SEG2(+) were evaluated as control class 3. It is possible to efficiently manage chemical substances by establishing specific SEG properly stratified.

A survey on selection, use, maintenance, and management of chemical protective gloves at workplaces in Japan.

OBJECTIVES: The aim of this study was to survey the selection, use, and maintenance of chemical protective gloves (CPGs) at real workplaces. METHODS: Subjects comprised 817 workers using CPGs at seven domestic manufacturing plants in Japan. We administered an anonymous questionnaire survey comprising the following aspect related to CPGs: environment of use, conditions of use, method of selection, knowledge/awareness pertaining to their use, method of use, precautionary measures associated with their use, maximum time of use, and maintenance. We compared responses provided by management staff and field workers. Chi square test was used for the analysis. RESULTS: Respondents included 661 (80.9%) manufacturing workers, 121 (14.8%) managers or supervisors, and 35 (4.3%) others. In total, 70.5% organic solvents, 28.9% acid or/and alkali, 18.1% dust, and 10.3% carcinogenic substances were the chemical substances handled using CPGs. The reason for deciding to wear CPGs was "the use of chemical substances" for 46.5%, "notice in safety data sheet (SDS) " for 29.8%, and "management staffs' guidance" for 21.4% respondents. "The grasp of chemical substances" was 70.1% (91.1% excluding "not applicable" ). "Warning of caution on skin and eyes" was indicated by 69.5% (91.0%) and "educational reasons for use of CPGs" was accepted by 68.1% (90.7%) respondents. On the other hand, the rate of responses such as "obtaining permeability test results of target substances" and "mixed substances are selected considering substances with short permeation time" was 25.2% (38.4%) and 29.2% (48.4%), respectively. The rate of "yes" as a response in the item concerning "permeation test" was low. On comparing the response provided by the management staff and field workers, the rate of "the permeation test result of the target substance was obtained" was 27.7% for management staff and 41.2% for field workers (p = 0.022). Regarding the cuffs of CPGs, the rate of "to fold back and to prevent sagging" and "mounted with tape" were 30.5% and 21.8% for management staff and 50.2% and 42.2% for field workers (p = 0.001 and p = 0.001), respectively. DISCUSSION: This survey results suggested that the knowledge of "permeation test" of CPGs was not yet popular at industrial workplaces. It is necessary to disseminate knowledge related to "permeation test" to the users from manufacturers of CPGs. Additionally, the employer should appoint an administrator to ensure that CPGs are worn and increase the understanding of correct knowledge and usage of CPGs among workers.

Assessment of workplace air concentrations of formaldehyde during and before working hours in medical facilities.

Workplace air concentrations of formaldehyde (FA) in medical facilities where FA and FA-treated organs were stored and handled were measured before and during working hours and assessed by the official method specified by Work Environment Measurement Law. Sixty-percent of the total facilities examined were judged as inappropriately controlled work environment. The concentrations of FA before working hours by spot sampling were found to exceed 0.1 ppm in some facilities, and tended to increase with increasing volume of containers storing FA and FA-treated materials. Regression analysis revealed that logarithmic concentrations of FA during working hours by the Law-specified analytical method were highly correlated with those before working hours by spot sampling, suggesting the importance for appropriate storing methods of FA and FA-treated materials. The concentrations of FA during working hours are considered to be lowered by effective ventilation of FA-contaminated workplace air and appropriate storage of FA and FA-treated materials in plastic containers in the medical facilities. In particular, such improvement by a local exhaust ventilation system and tightly-sealed containment of FA-treated material were urgently needed for the dissecting room where FA-treated cadavers were prepared and handled for a gross anatomy course in a medical school.

Personal indium exposure concentration in respirable dusts and serum indium level.

The aim of this study was to assess the relationship between indium exposure concentration in the respirable dust fraction (In-E) and indium in serum (In-S) in workers. METHODS: A total of 39 workers were studied. The study subjects were categorized into 3 groups, namely, smelting workers (n=7), ITO workers (n=6) in an ITO grinding plant, and other workers (n=26). In-E and In-S ranged from 0.004-24.0 µg/m3 and 0.1-8.50 µg/L, respectively. The simple regression equation was log(In-S)=0.322×log(In-E)-0.443. The simple correlation coefficients for the smelting workers, ITO workers and other workers were 0.489, 0.812 and 0.163, respectively. The differences in the relationships among the three groups suggest that In-S may vary with the chemical form to which the workers were exposed. In-E and In-S seem to be positively correlated. The correlation coefficient was higher for both smelting and ITO workers than for other workers.

Control banding assessment of exposure of offset printing workers to organic solvents.

OBJECTIVES: We aimed to assess the exposure of offset printing workers to hazardous substances in the rinsing processes of small-sized companies using a control banding method. METHODS: We obtained half-year amounts of hazardous substances purchased through a questionnaire survey and the hazardous information from the safety data sheets (SDSs) and related literature. RESULTS: The amount of petroleum kerosine and carbon hydride markedly increased in 2013 compared with that in 2010. In contrast, the amount of dichloromethane (DCM) decreased in 2013, and 1,2-dichloropropane (DCP) was not used in either 2010 or 2013. Mineral oil and xylene were allocated to Hazard Group D and judged to require Control Approach 3. In addition to DCM with Global Harmonization System's carcinogenic category 1, mildly treated mineral oil and solvent naphtha, allocated into Hazard Group E, are carcinogenic to humans and were judged to require Control Approach 4. There are two limitations of the control banding assessment: first, only limited and scarce hazard information could be obtained from SDSs, and second, safe-sided judgment for control technology for industrial hygiene. CONCLUSION: Small-sized enterprises are encouraged to implement control banding assessment for hazardous substances and to access expert advice available from Regional Industrial Health Centers. Easy access to appropriate expert advice is important to compensate for the limited and scarce hazard information and safe-sided judgment for control technology for Control Approaches 3 and 4.

[A survey of the otoacoustic emissions (OAEs) of workers exposed to noise in manufacturing factories].

OBJECTIVES: Otoacoustic emission (OAE) testing is not widespread in Japanese industrial health. This study examined the association between hearing thresholds (HTs) and OAEs among workers exposed to noise in actual workplaces. METHODS: In two metal products manufacturing factories, 34 workers with noise exposure in the workplace (exposure group, mean age 40.6 ± 9.4 years), and 9 workers with no noise exposure (control group, 49.0 ± 14.3 years) were surveyed. The time-weighted average (LAeq) and maximum (LAMAX) of environmental noise monitoring (ENM), and the time-weighted average (LTWA) and sound exposure level (LAE) of personal noise monitoring (PNM) were measured for each subject at the same time. As hearing effect indicators of noise exposure levels, HTs (0.5, 1, 2, 4 and 8 kHz) and distortion product OAEs (DPOAEs) (2, 3 and 4 kHz) were performed before and after 5 days of work. The results of the ENM, PNM, HTs and OAEs were compared between the groups using Student's t test, and their correlations were investigated using Pearson correlation coefficients. RESULTS: Noise exposure levels of the exposure group were significantly higher than those of the control group. In the exposure group, LAeq, LAMAX, LTWA and LAE were respectively 84.5 ± 4.1 dB(A),89.5 ± 6.3 dB(A), 83.4 ± 4.7 dB(A) and 153.1 ± 15.7 dB(A), and in the control group, they were 53.2 ± 2.6 dB(A), 56.4 ± 2.4 dB(A), 67.8 ± 5.6 dB(A) and 119.5 ± 5.6 dB(A). There was no difference between hearing effect indicators (HTs and OAEs) before and after work in either group. There was no correlation between the noise exposure level (LAeq, LTWA, LTWA and LAE) and HTs or OAEs, but there was a significant correlation between the HTs and OAEs at most of frequencies. The HTs and OAEs of subjects with noise-induced hearing loss (NIHL) were significantly lower than those of subjects without NIHL. CONCLUSIONS: This study revealed there is a significant correlation of the HTs and OAEs before and after 5 days of work. In the future, OAE is expected to be used as a screening test of hearing management of noise-exposed workers in Japan.

Occupational exposure to N,N-dimethylformamide in the summer and winter.

We evaluated total body burden of N,N-dimethylformamide (DMF) taken through the lung and skin by personal exposure of workers to DMF and urinalysis of N-methylformamide (NMF) and N-acetyl-S(N-methylcarbamoyl)-cysteine (AMCC). A total of 270 workers were engaged in four different jobs in a workplace distant from main production lines emanating high levels of DMF. They were not required to wear any personal protective equipment including respirators or gloves. We found that log-transformed urinary levels of NMF and AMCC increased with an increase in log-transformed concentrations of exposure to DMF. Urinary levels of NMF and AMCC were significantly higher in the summer than the winter, although there was no significant seasonal difference in the concentrations of exposure to DMF. Our findings suggested that the increased urinary levels of NMF and AMCC in the summer resulted in increased skin absorption of DMF due to an increased amount of DMF absorbed by the moisturized skin under humid and hot conditions. Seasonal changes in the relative internal exposure index confirmed the present finding of enhanced summertime skin absorption of DMF. AMCC is thought to be a useful biomarker for assessments of cumulative exposure to DMF over a workweek and for evaluations of workers' health effects.

Seasonal difference in percutaneous absorption of N,N-dimethylformamide as determined using two urinary metabolites.

OBJECTIVE: We evaluated the percutaneous absorption of N,N-dimethylformamide (DMF) in DMF-exposed workers in the summer and winter by assessing their urinary levels of DMF metabolites. METHODS: Breathing-zone concentrations of DMF and workers' urinary levels of N-methylformamide (NMF) and N-acetyl-S-(N-methylcarbamoyl)-cysteine (AMCC) were simultaneously measured in the summer and winter in 193 male workers wearing a respirator and chemical protective gloves. RESULTS: The mean breathing-zone concentrations of DMF in both seasons were below the occupational exposure limit of 10 ppm. Although there was no significant seasonal difference in the breathing-zone concentrations of DMF, workers' urinary levels of NMF and AMCC were significantly higher in the summer than in the winter. Log-transformed urinary levels of the metabolites were significantly correlated with log-transformed breathing-zone concentrations of DMF in the summer, whereas no significant correlation between AMCC and DMF was found in the winter. The urinary levels of AMCC were dispersed more widely than those of NMF, suggesting that urinary AMCC reflected the cumulative exposure to DMF over a workweek. CONCLUSIONS: Percutaneous absorption was the principal route of exposure to DMF for the respirator-wearing workers. Increased urinary levels of NMF and AMCC in the summer were attributed to increased percutaneous absorption of DMF resulting from the increased amount of water-soluble DMF absorbed by sweaty skin caused by the increased summertime room temperature and humidity.

Solution-processed small molecule:fullerene bulk-heterojunction solar cells: impedance spectroscopy deduced bulk and interfacial limits to fill-factors.

Using impedance spectroscopy, we demonstrate that the low fill factor (FF) typically observed in small molecule solar cells is due to hindered carrier transport through the active layer and hindered charge transfer through the anode interfacial layer (IFL). By carefully tuning the active layer thickness and anode IFL in BDT(TDPP)2 solar cells, the FF is increased from 33 to 55% and the PCE from 1.9 to 3.8%. These results underscore the importance of simultaneously optimizing active layer thickness and IFL in small molecule solar cells.