Journal of Occupational Health
Online ISSN : 1348-9585
Print ISSN : 1341-9145
ISSN-L : 1341-9145
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Comparison of chemical risk assessment methods in South Korea and the United Kingdom
Min-Uk KimSaemi ShinSang-Hoon Byeon
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2015 Volume 57 Issue 4 Pages 339-345

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Abstract

Objectives: The objective of this study was to compare Control of Substances Hazard to Health (COSHH) Essentials (a chemical risk assessment method in the UK) with Chemical Hazard Risk Management (CHARM) (a chemical risk assessment method in South Korea). The differences between the two processes were explored with a particular focus on their features and distinctions. Methods: The results obtained from applying COSHH Essentials and CHARM to 59 carcinogenic, mutagenic, and reprotoxic (CMR) substances were analyzed. The outcomes of the working environment assessments and the collated information about the usage of CMR chemicals were used for the analysis. Results: Among the 59 substances tested, 56 substances were rated at a risk level lower than 2, when evaluated with CHARM. However, with COSHH, all 59 substances were rated at risk level 3 or higher. With COSHH Essentials, the highest hazard group of 4 was automatically assigned to category E substances, regardless of the exposure level assessment. However, for CHARM, the risk could be adjusted according to the exposure level assessment, even for hazard group of 4. Conclusions: CHARM allocated lower risk levels to hazardous substances than COSHH Essentials. Ultimately, COSHH Essentials assesses exposure level through the physical properties and overall handling, and considers hazard with H-statements and R-phrases. COSHH Essentials was deemed more conservative than CHARM. CHARM may have underestimated the risk according to exposure level, even though the chemicals were highly hazardous. Therefore, CHARM can be used for the localized risk assessment of chemicals used in individual workplaces.

(J Occup Health 2015; 57: 339–345)

Introduction

In South Korea, there is growing concern that chemical accidents are causing severe pollution and health problems1). This is principally due to the continuous rise in the number of injuries and fatalities, alongside significant economic losses. There have recently been a number of chemical accidents, for example, hydrofluoric acid leakages in Gumi in 2012, at the Cheongju industrial complex in 2013, and at Samsung Electronics' Hwaseong workplace in 20132). It has become increasingly apparent that the government and employers have a responsibility to safeguard the health of their workers by ensuring that all chemicals are managed safely.

Examples of the existing risk assessment legislation include the Framework Directive on Safety and Health at Work (Directive 89/391/EEC, Europe), the Occupational Safety and Health Act 2006 (Japan), and the Workplace Safety and Health Act 2006 (Singapore)3).

In 1998, the UK Health and Safety Executive (HSE) announced a series of papers concerning the control banding (CB) strategy used to determine the recommended level of risk control4). The HSE also developed the Control of Substances Hazardous to Health (COSHH) Essentials to give small- and medium-sized enterprises advice on approaches for conducting risk assessment of chemicals in the workplace5). COSHH Essentials is a global chemical-managing toolkit that uses warning labels and a simple method for predicting exposure6). It employs a qualitative method based on the CB technique to assess and manage risks7). Various studies have been conducted using COSHH Essentials, which include a study on control methods and technique selection for vapor degreasing and bag filling operations and a study on comparing real exposure and control methods of organic chemicals in medium-sized businesses that produce coating and painting materials for automobiles812).

Protecting the health of workers from the effects of chemicals is challenging in South Korea. This is because business owners are required to limit the exposure of their workers to hazardous chemicals, but there is no formal chemical risk assessment process in place. In 2012, the Korea Occupational Safety and Health Agency (KOSHA) developed a chemical risk assessment system known as Chemical Hazard Risk Management (CHARM), which uses CB13). Although CHARM has been referenced in academic, technical, and preliminary studies, its use as a form of risk assessment for protecting workers from exposure to hazardous chemicals has received minimal attention.

In order to address this issue, this study compares the COSHH Essentials (UK) risk assessment with the CHARM system (South Korea). The assessment of 59 carcinogenic, mutagenic, and reprotoxic (CMR) substances was performed using both processes, enabling direct comparison of the results according to exposure levels and usage quantities of the chemicals. From the results, the features and differences of the two systems were highlighted.

Methods

COSHH essentials and CHARM

For COSHH Essentials, R-phrases and H-statements are involved in hazard level assessment14). Conversely, for CHARM, four sources of information are used to identify the following: (i) whether the chemical is a CMR substance, (ii) what the occupational exposure limit (TWA-OELs) is and (iii) what the R-phrases and H-statements are according to the material safety data sheet13).

COSHH Essentials determines how much of the substance will be used according to its physical properties (e.g., dustiness and volatility)15). However, CHARM uses three assessment criteria, which include (i) considering whether the chemical has caused occupational diseases in works and then considering the occupational exposure levels, (ii) the quantities used, and (iii) the physical properties of the substance under consideration13).

For COSHH Essentials, there are five hazard groups (A=very low, B=low, C=medium, D=high, E=very high) and four exposure levels (1=low, 2=medium, 3=high, 4=very high) for the risk assessment of chemicals; in the CHARM system, there are four hazard groups (1=low, 2=medium, 3=high, 4=very high) and four exposure levels (1=low, 2=medium, 3=high, 4=very high)13, 14). The hazard definitions of COSHH Essentials and CHARM are identically classified according to the standards presented in “the Chemicals Hazard Information and Packaging for Supply Regulations” (CHIP)16) and “Classification, Labeling, and Packaging of Substances and Mixtures Regulations” (CLP)17). However, there is a difference in the hazard groups that determine the hazard level, with one having five groups (A–E) and the other only four (14). In COSHH Essentials, CMR substances are classified as grades D–E if they are carcinogenic or mutagenic and as grade D if they are toxic for reproduction. On the other hand, in CHARM, CMR substances are not classified as grades D–E but are classified identically as grade 4, the highest hazard group. In COSHH Essentials and CHARM, the exposure definition is identically classified according to the physical properties (e.g., dustiness and volatility)15). However, in CHARM, when the results of working environment measurements are applied, the exposure levels are determined according to the exposure grades of the chemical substances (the results of the working environment measurements divided by the TWA-OELs), and there are four exposure levels (1=less than 10%, 2=10% or more but less than 50%, 3=50% or more but less than 100%, 4=more than 100%)13).

With CHARM, the final risk level (1=low, 2=medium, 3=high, 4=very high) is determined by classifying the results, which are obtained by multiplying the exposure level grade and the hazard score as shown in Table 113). However, for COSHH Essentials, the risk level is determined by combining the exposure level and hazard grades according to the physical state of the chemicals (e.g., solid or liquid) as shown in Fig. 118). Figure 1 shows a method for determining the risk level of COSHH Essentials and CHARM.

Table 1. Determination of the risk level for CHARM

CHARM: Chemical Hazard Risk Management.

Fig. 1.

Estimation of the risk level for Control of Substances Hazard to Health (COSHH) essentials and Chemical Hazard Risk Management (CHARM).

Application to hazardous substances

In accordance with the South Korean Occupational Safety and Health Acts, working conditions are investigated every 5 years19). Therefore, data involving annual chemical usage, number of exposed workers, and workplaces that use chemicals were obtained from these surveys.

In South Korea, the classification and concentration of hazardous airborne substances inhaled by workers is monitored, alongside any possible links to health issues. The workplace is then examined to determine whether improvements to working practices are required18).

According to local occupational safety and health standard rules, hazardous substances that must be managed and monitored in working environments, include 113 organic compounds, 23 metals, 17 acids and alkalis, and 15 gaseous materials, and CMR substances are included in this group20).

In this study, 59 chemicals for which both working environment measurements and usage information were available were used to compare the risk assessment methods of CHARM and COSHH Essentials21).

Table 2 shows the details of 17 chemical substances (a subgroup of the 59 chemicals studied), including hexane, methoxyethanol, etc. Daily usage was calculated by dividing the annual usage by the number of working days (300 d/yr). The overall daily usage for one workplace was calculated by dividing the total daily usage by the number of workplaces.

Table 2. Chemical information
Substance CAS No. No. of worker's No. of workplaces TWA-OELs (mg/m3) Work environment measurements (mg/m3) Daily amounts (t) Daily amounts (t) / Workplaces
2,3-Epoxy-1-propanol 556-52-5 6 8 6.1 0.003 1 × 10−5 1 × 10−6
Stoddard solvent 8052-41-3 885 16 525 14.8 1.35 × 102 8.44
1,2,3-Trichloropropane 96-18-4 6 552 60 4.54 0.8 1.5 × 10−3
N,N-Dimethylacetamide 127-19-5 81 24 35 2.21 6.08 × 103 2.53 × 102
Ethylene dichloride 107-06-2 161 1 40 1.61 4.98 × 103 4.98 × 103
Acrylonitrile 107-13-1 283 2,522 4.5 0.07 2.25 × 103 0.89
2-Methoxyethyl acetate 110-49-6 181 58 24 0.44 1.9 3.3 × 10−2
1,2-Epoxypropane 75-56-9 56 3 5 0.12 0.19 0.06
Hexane (n-hexane) 110-54-3 3,336 11 180 2.72 1.15 × 104 1.05 × 103
1,4-Dioxane 123-91-1 30 1 72 0.88 8.4 8.4
Dichloromethane 75-09-2 2,116 106 175 10.42 5.57 × 103 52.57
Hydroquinone 123-31-9 484 770 2 0.001 0.02 3 × 10−5
1,1,2-Trichloroethane 79-00-5 172 13 55 0.83 1.63 0.13
Methyl n-butyl ketone 591-78-6 34 1 20 1.58 0.23 0.23
Methoxyethanol 109-86-4 118 484 16 0.73 9.5 0.02
p-Nitrochlorobenzene 100-00-5 3 114 0.6 0.001 1 × 10−5 3 × 10−7
Vanadium pentoxide 1314-62-1 4 9 0.05 0.006 0.4 0.04

Results

The greatest difference between COSHH Essentials and CHARM is that they are applied differently, given the available information for the assessed substances. Furthermore, CHARM includes the results of working environment measurements. In order to establish the effects of these differences, risk assessments were conducted in the workplace for 59 CMR substances with known (measured) values using the CHARM manual13) and the COSHH Essentials guidelines14). Physicochemical data for the substances were obtained from the Globally Harmonized System-Material Safety Data Sheets (GHS-MSDSs) via KOSHA22).

Table 3 shows the risk level for 17 chemical substances as determined by CHARM and COSHH Essentials. Figure 2 shows the results of the hazard and exposure evaluations by CHARM and COSHH Essentials.

For CHARM, CMR materials were labeled as grade 4, which is the highest hazard grade in the assessment. In COSHH Essentials, the hazard assessment differed for the CMR materials. Carcinogenic or mutagenic materials like Stoddard solvent, ethylene dichloride, dichloromethane, etc., were designated grades D or E. Materials toxic to reproduction like 1,2,3-trichloropropane, N,N-dimethylacetamide, methyl n-butyl ketone, methoxyethanol, etc., were labeled as grade D.

Table 3. Risk levels of CHARM and COSHH essentials
Substance CAS NO. CHARM COSHH essentials
Hazard Exposure Risk level Hazard Exposure Risk level
2,3-Epoxy-1-propanol 556-52-5 4 1 2 E 1 4
Stoddard solvent 8052-41-3 4 1 2 E 2 4
1,2,3-Trichloropropane 96-18-4 4 1 2 E 2 4
N,N-Dimethylacetamide 127-19-5 4 1 2 D 2 3
Ethylene dichloride 107-06-2 4 1 2 E 3 4
Acrylonitrile 107-13-1 4 1 2 E 3 4
2-Methoxyethyl acetate 110-49-6 4 1 2 D 3 4
1,2-Epoxypropane 75-56-9 4 1 2 E 3 4
Hexane (n-hexane) 110-54-3 4 1 2 D 3 4
1,4-Dioxane 123-91-1 4 1 2 D 3 4
Dichloromethane 75-09-2 4 1 2 D 4 4
Hydroquinone 123-31-9 4 1 2 E 1 4
1,1,2-Trichloroethane 79-00-5 4 1 2 D 3 4
Methyl n-butyl ketone 591-78-6 4 1 2 D 3 4
Methoxyethanol 109-86-4 4 1 2 D 3 4
p-Nitrochlorobenzene 100-00-5 4 1 2 E 1 4
Vanadium pentoxide 1314-62-1 4 2 3 E 3 4

CHARM: Chemical Hazard Risk Management. COSHH: Control of Substances Hazard to Health.

Fig. 2.

Classification of hazard and exposure level according to Chemical Hazard Risk Management (CHARM) and Control of Substances Hazard to Health (COSHH) essentials.

The results of the exposure assessment showed that most materials had grade 1 exposure values (less than 10%)13) in the working environment measurements compared with the occupational exposure limit (TWA-OELs)23). Only 3 of the 59 CMR materials were found to be grade 2 (between 10 and 25%) in the measurements. The numbers of CMR materials classified in each grade from 1 to 4 in the results of the exposure assessment by COSHH Essentials according to the usage and physical properties (fugacity/volatility) of each material were 4, 21, 26, and 8, respectively.

The results of the risk assessment showed that most chemicals evaluated using CHARM were assigned a lower risk (by 2 grades), whereas COSHH Essentials rated the risk level as grade 4 most frequently.

COSHH Essentials assessed the riskiness of grade E chemical substances, which have the highest hazard assessment results, as grade 4, even though the results from the exposure assessment were low (grades 1 or 2). However, CHARM assessed the riskiness of chemicals with low exposure grades (grades 1 or 2) as grade 2 or 3, despite assigning a grade of 4 in the hazard assessment.

Figure 3 shows the comparisons of the risk level classification by CHARM and COSHH Essentials; the evaluations of the same CMR substances differed. The risk assessment was lower for CHARM than for COSHH Essentials. CHARM found low risk levels (grade 2) for 56 of the 59 substances. However, COSHH Essentials assessed higher risk levels (grade 4) for 51 of the 59 substances tested. Therefore, for the same CMR substances, CHARM assigned low risk levels in 95% of cases and COSHH Essentials assessed a high risk in 87% of cases. CHARM labeled 3 chemical substances at grade 3, while COSHH Essentials found 8 chemical substances at that grade.

Fig. 3.

Classification of risk level according to Chemical Hazard Risk Management (CHARM) and Control of Substances Hazard to Health (COSHH) essentials.

Discussion

Chemical substances are widely used, but when mishandled, they pose a hazard to the environment and can cause various occupational diseases24). In South Korea, carcinogens have become a social concern following growing incidents of lung cancer in workers exposed to asbestos and of leukemia in semiconductor factory workers25).

This study used CMR chemical substances to compare the features and distinctions of CHARM and COSHH Essentials for risk assessment of chemicals.

COSHH Essentials was developed in the UK as a convenient risk assessment method for chemicals used by small- and medium-sized enterprises26). CHARM, which is based on COSHH Essentials, is the system used in South Korea to assess risks in the workplace13). When evaluating CMR chemical substances, CHARM labels the most hazardous chemicals as a grade 4. However, COSHH Essentials assess hazards according to the R-phrases or H-statements of the chemical substances. Hazard information is applied to the R-phrase or H-statement by defining the CHIP16) and CLP17) for each chemical. The hazard class of the chemical substances in this study were the same as those for the CHIP and CLP regulations27).

Although COSHH Essentials and CHARM apply similar methods and standards, there were some differences in the methods with which the risk level was determined. For example, COSHH Essentials determines the risk level by classifying chemicals as solid or liquid, whereas CHARM does not consider the physical state of the chemical28). Furthermore, the risk level in COSHH Essentials is assessed by a combination of the hazard and exposure levels as shown in Fig. 1, whereas CHARM calculates the risk by multiplying the hazard and exposure levels as shown in Table 1. In this study, the methods for determining risk levels were compared using banding as shown in Fig. 1; however, the only differences were in the procedure, since both methods use a combination of hazard and exposure levels.

The level of risk identified was much lower for CHARM than for COSHH Essentials; the hazard assessment was high for both, but the exposure assessment was low for both. CHARM determines the exposure level according to working environment measurements of the chemicals. COSHH Essentials assesses exposure levels using the physical properties and overall handling, and evaluates hazard through the H-statements or R-phrases. It has been judged to be more conservative than CHARM.

The results of the working environment measurements of the 59 CMR chemical substances applied in this study showed that the workplace exposure levels were mostly lower than 10% compared with the occupational exposure limit (TWA-OELs). The percentage of workplaces in Korea where working environment measurements exceed the TWA-OELs is as low as 8%29, 30). Furthermore, according to results of working environment measurements in car manufacturers, which uses a host of different chemicals, carcinogen like benzene were barely detected31, 32). For example, the working environment measurements for workplaces utilizing dichloromethane showed that 25.4% of workplaces had undetectable levels, 50.5% of workplaces had exposure levels of less than 10%, and 17.8% of workplaces had exposure levels of less than 50%33).

For COSHH Essentials, CMR chemical substances are typically assessed as high risk because of the immediate allocation of a high hazard grade, regardless of the exposure level. However, for CHARM, when the exposure level is assessed as low, the risk is also considered low, despite the high hazard level of the CMR substances. Therefore, the exposure level influences the risk of the chemical more than the hazard level. Although a high-risk CMR substance may be used continuously, the risk management action will be assigned a risk level of 1 if the exposure level is low. Thus, there is a concern that a highly hazardous chemical substance will be assessed as low risk. As a result, it may be more effective to use CHARM for localized risk assessments for chemicals used in individual workplaces.

Acknowledgments: This study was supported by the Korea Occupational Safety and Health Agency and a research grant from Korea University. The authors gratefully acknowledge their support.

Conflict of interest: The authors declare that there are no conflicts of interest.

References
  • 1)   Park  JK,  Seo  YW. A study on the improvement of the chemical accident response system. Korea Environment Institute; 2013. p. 1-56.
  • 2)   Choi  MK,  Choi  DM. A study on the safety management measures efficient chemical substances. J Korea Saf Manag Sci 2013; 15: 37-50 (in Korean).
  • 3)   Park  DY,  Baek  DM,  Lee  YS, et al. Development and introduction of an OSH regulatory framework based on risk assessment for Korean OSH regulation systems and policy. Occupational Safety and Health Research Institute; 2009. p. 1-175.
  • 4)   Zalk  DM,  Nelson  DI. History and evolution of control banding: a review. J Occup Environ Hyg 2008; 5: 330-46.
  • 5)   Hay  A. Controlling exposure to chemicals: a simple guide. Ann N.Y Acad Sci 2006; 1076: 790-9.
  • 6)  National Institute of Occupational Safety and Health. Qualitative risk characterization and management of occupational hazards: control banding (CB). DHHS (NIOSH); 2009. p. 1-32.
  • 7)   Fingerhut  M. Global qualitative risk management (control banding) activities. Industrial Health 2008; 46: 305-7.
  • 8)   Jones  RM,  Nicas  M. Evaluation of COSHH Essentials for vapor degreasing and bag filling operations. Ann Occup Hyg 2006; 50: 137-47.
  • 9)   Lee  EG,  James  S,  Russell  B,  Bowen,  Martin  H. Evaluation of COSHH Essentials model with a mixture of organic chemicals at a medium-sized paint producer. Ann Occup Hyg 2011; 55: 16-29.
  • 10)   Lee  EG,  James  S,  Russell  B,  Bowen0,  Martin  H. Evaluation of COSHH Essentials: methylene chloride, isopropanol, and acetone exposures in a small printing plant. Ann Occup Hyg 2009; 53: 463-74.
  • 11)   Jones  RM,  Nicas  M. Margins of safety provided by COSHH Essentials and ILO chemical control toolkit. Ann Occup Hyg 2006; 50: 149-56.
  • 12)   Lee  EG,  Kim  SW,  Feigley  CE. Exposure models for the prior distribution in Bayesian decision analysis for occupational hygiene decision making. J Occup Environ Hyg 2013; 10: 97-108.
  • 13)  Korea Occupational Safety and Health Agency. Chemical risk assessment manual. KOSHA; 2012. p. 1-95.
  • 14)  Health and Safety Executive. The technical basis for COSHH essentials: Easy steps to control chemicals. [Online]. 2013 [cited 2013 Dec 04]; Available from: URL: http://www.coshh-essentials.org.uk/assets/live/CETB.pdf
  • 15)   Maidment  SC. Occupational hygiene considerations in the development of a structured approach to select chemical control strategies. Ann Occup Hyg 1998; 42: 391-400.
  • 16)  The chemicals (hazard information and packaging for supply) regulations. 716 (2009).
  • 17)  Classification, labelling and packaging of substances and mixtures, amending and repealing regulations. 1272 (2008).
  • 18)   Russell  RM,  Maidment  SC,  Brooke  IM,  Topping  MD. An introduction to a UK scheme to help small firms control health risks from chemicals. Ann Occup Hyg 1998; 42: 367-76.
  • 19)  Occupational Safety and Health Act. 10968 (2011).
  • 20)  Local rules on occupational safety and health standard. 77 (2013)./
  • 21)  Korea Occupational Safety and Health Agency. 2009 Refund status reports national industrial work environment. Ministry of Employment and Labor; 2009.
  • 22)  Korea Occupational Safety and Health Agency. GHS/MSDS. [Online]. 2014 [cited 2014 Jan 17]; Available from: URL: http://www.kosha.or.kr/msds/msdsMain.do-menuId=69
  • 23)   Topping  M. Occupational exposure limits for chemicals. Occp Environ Med 2001; 58: 138-44.
  • 24)   Lee  KS,  Lee  HJ,  Lee  JH. A study on the provide of CMR substances information for Threshold Limit Values (TLVs) chemicals in KMoEL. J Korean Soc Occup Environ Hyg 2012; 22: 82-90 (in Korean).
  • 25)   Lee  KS,  Lee  HJ,  Lee  JH. A study on the criteria and supply status of information for managing carcinogens in domestic and foreign. J Korean Soc Occup Environ Hyg 2011; 21: 40-8 (in Korean).
  • 26)   Garrod  AN,  Evans  PG,  Davy  CW. Risk management measures for chemicals: the “COSHH essentials” approach. J Expo Sci Environ Epidemiol 2007; 17(Suppl 1): 48-54.
  • 27)   Garrod  ANI,  Rajan-Sithamparanadarajah  R. Developing COSHH Essentials: dermal exposure, personal protective equipment and first aid. Ann Occup Hyg 2003; 47: 577-88.
  • 28)   Brooke  IM. A UK scheme to help small firms control health risks from chemicals: toxicological considerations. Ann Occup Hyg 1998; 42: 377-90.
  • 29)   Kim  JH,  Won  JI. Analysis of overviews of working environment measurement and its results in Korean industry. Korean J Sanitation 1996; 11: 53-61 (in Korean).
  • 30)   Choi  SJ. Assessment on Work Environment Monitoring Program in Korea. J Korean Soc Occup Environ Hyg 2008; 18: 282-92 (in Korean).
  • 31)   Oh  DS,  Lee  YH. Study on analysis for working environmental measurement results of automobile industries. J Korean Soc Occup Environ Hyg 2004; 14: 233-42 (in Korean).
  • 32)   Park  SJ,  Lee  WH,  Lee  K,  Moon  DH. A study on the status of working environmental by type of working processes in manufacturing industry of parts and accessories for motor vehicles and its engines. J Korean Soc Occup Environ Hyg 2005; 15: 90-103 (in Korean).
  • 33)   Lee  JH,  Park  DU,  Hong  SC,  Ha  KC. Construction of an exposure matrix using a risk assessment of industries and processes involving Dichloromethane. Korean J Environ Health Sci 2010; 36: 391-401 (in Korean).
 
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