Data from Washington State's work-related asthma surveillance system were used to characterize isocyanate-induced asthma cases occurring from 1999 through 2010. Injured worker interviews and medical records were used to describe the industry, job title, work process, workers’ compensation cost, and exposure trends associated with 27 cases of isocyanate-induced asthma. The majority (81%) of cases were classified within the surveillance system as new-onset asthma while 19% were classified as work-aggravated asthma. The workers’ compensation cost for isocyanate-induced asthma cases was $1.7 million; this was 14% of the total claims cost for all claims in the asthma surveillance system. The majority of cases (48%) occurred from paint processes, followed by foam application or foam manufacturing (22%). Nine of the asthma cases associated with spray application occurred during application to large or awkward-shaped objects. Six workers who did not directly handle isocyanates (indirect exposure) developed new-onset asthma. Two cases suggest that skin contact and processes secondary to the isocyanate spray application, such as cleanup, contributed to immune sensitization. Surveillance data provide insight for the prevention of isocyanate-induced respiratory disease. Key observations are made regarding the development of work-related asthma in association with a) paint application on large objects difficult to ventilate, b) indirect exposure to isocyanates, c) exposure during secondary or cleanup processes, and d) reports of dermal exposure.
Isocyanates are widely recognized as a common cause for occupational asthma.(
Beyond respiratory disease, there are at least six cases of fatal exposure to isocyanates reported in the literature. A total of three fatal asthma cases are reported for MDI exposure in three different processes: truck bed liner application, foundry work, and foam operation.(
Occupational health surveillance has the potential to characterize isocyanate-induced asthma so that research, policy, and educational outreach can be strategically directed to specific industries or applications for disease prevention. Isocyanate-induced asthma cases identified in the surveillance system described here occurred during the period 1999–2010. Cases were reviewed in-depth to characterize the job title, process description, isocyanate species, and workers’ compensation costs associated with the asthma case. The purpose of this review was to identify isocyanate-based processes associated with asthma, and to characterize exposure to help inform prevention activities.
Workers' compensation insurance is mandated for all non-federal employers in Washington State unless they are covered by an alternative workers’ compensation program (e.g., Federal Employees' Compensation Act, Longshoremen's and Harbor Workers' Compensation Act). Workers' compensation insurance can be obtained through either (a) the state's industrial State Fund (SF) insurance program administered by the Department of Labor & Industries (L&I) or (b) through self-insurance. The State Fund provides coverage for approximately 1.9 million (about two-thirds) of the workers in the state and 99.7% of all employers. The remaining 450 employers self-insure for workers' compensation. To self-insure, employers must have at least $25 million in assets, an effective accident-prevention program, a minimum of 3 years of business operations, and specific liquidity requirements.(
Distinction between State Fund and self-insured workers is made because while data from both programs are collected into L&I's Workers' Compensation database, less information about self-insurance claims (medical records and claim costs) is typically reported to the state. Because of this, the surveillance system described here reflects primarily State Fund-insured workers. Occupational asthma is a reportable condition in Washington State for health care providers and health care facilities.(
Washington State's asthma surveillance system has been described in detail.(
Two primary goals of the surveillance system are to classify the type of asthma and to document the agent causing the asthma. This information is obtained through a questionnaire administered over the telephone with the injured worker. The questionnaire incorporates the Sentinel Event Notification System for Occupational Risks (SENSOR) case classification scheme for occupational asthma adopted by the National Institute for Occupational Safety and Health (NIOSH).(
Within the SENSOR case classification scheme, WAA is defined as work-related exacerbations of a preexisting asthma condition. Workers with a history of symptomatic or treated asthma within the past 2 years and who have an increase in symptoms or use of asthma medications are classified as having work-aggravated asthma.(
RADS refers to new-onset persistent asthma resulting from a one-time high-dose irritant exposure.(
To gain further insight into the isocyanate-induced asthma cases, surveillance interviews and medical records were reviewed by one of the authors and also by a research analyst. Additionally, information to answer the following yes/no questions was sought: 1) if a spray application, was the item large, awkwardly shaped, or a fixed outdoor structure?, and 2) did the injured worker directly handle isocyanates? When an injured worker reported during the surveillance interview or in the medical records that dermal exposure to isocyanates was a factor contributing to his or her asthma, this was noted. These questions were answered in relation to the predominant task performed, or if emergency care was sought, to the task being performed at the time of respiratory distress.
Claim costs for self-insured workers were excluded from the cost summary because these claims have incomplete cost records in the L&I's Workers' Compensation database and cannot be accurately estimated. For State Fund workers' compensation claims the costs presented are based on all costs paid to date for closed claims. For claims that were still active and open (n = 3) on the date of extraction (Dec. 15, 2011), the claim costs represent those costs paid to date as well as an estimate of future expected claim costs. Future expected claim costs are estimated by the workers' compensation case reserve unit. Reserves are based on an experienced claim adjudicator's best estimations of claim costs for the life of the claim. If appropriate, reserves are estimated for medical care by injury type, wage costs, vocational rehabilitation costs, permanent partial disability, pension, and other claim costs. Costs are not adjusted for inflation.
Claims are defined as compensable if they meet a 3-day waiting period for time loss compensation and are further classified as “compensable,” “kept-on-salary,” “total permanent disability,” “fatal,” or “loss of earning power.” Time loss payments occur over time and in some cases may extend over several years. Both compensable and medical-only (non-compensable) claims from the State Fund are included in this analysis. The indirect cost to employers (e.g., employee turnover, productivity loss, and poor employee morale), the indirect costs to workers, and the administrative costs of managing the claims are not included in the claim costs. The Kruskal-Wallis non-parametric rank test was used to compare the median costs of isocyanate-induced asthma cases with all other asthma cases.
Among the 1,469 cases brought into the asthma surveillance system, there were 27 cases from exposure to isocyanates. Many of the cases are from Washington's manufacturing sector (North American Industry Classification System (NAICS) codes 31–33,
Distribution of Isocyanate-Induced Asthma Cases Across NAICS Code Sector (2-digit) and National Industry (6-digit)
| NAICS Code | # Isocyanate-induced asthma cases |
|---|---|
| 23 Construction | |
| 238320 Painting and wall covering contractors | 2 |
| 238310 Drywall and insulation contractors | 1 |
| 31–33 Manufacturing | |
| 325510 Paint and coating manufacturing | 2 |
| 336411 Aircraft manufacturing | 2 |
| 313230 Nonwoven fabric mills | 1 |
| 326199 All other plastic product manufacturing | 1 |
| 327991 Cut stone and stone product manufacturing | 1 |
| 332321 Metal window and door manufacturing | 1 |
| 332999 All other misc. fabricated metal product mfg. | 1 |
| 336214 Travel trailer and camper manufacturing | 1 |
| 336612 Boat building | 1 |
| 339950 Sign manufacturing | 1 |
| 42 Wholesale Trade | |
| 423990 Other misc. durable goods merchant wholesalers | 1 |
| 54 Professional, scientific, and technical services | |
| 541330 Engineering services | 1 |
| 81 Other services | |
| 811121 Automotive body, paint, and interior repair and maintenance | 8 |
| 92 Public administration | |
| 922160 Fire protection | 1 |
| 924110 Admin. of air and water resources and solid waste mgmt. | 1 |
| Total # cases | 27 |
The Standard Occupational Classification (SOC) codes for the 27 isocyanate-induced asthma cases are given in
Distribution of Isocyanate-Induced Asthma Cases Across Occupations
| Standard Occupational Classification (SOC) code | # Isocyanate-induced asthma cases |
|---|---|
| 11 Management Occupations | |
| 119199 Managers, All Other | 1 |
| 33 Protective Service Occupations | |
| 332011 Firefighters | 1 |
| 43 Office and Administrative Support Occupations | 1 |
| 439061 Office Clerks, General | |
| 47 Construction and Extraction Operations | |
| 472061 Construction Craft Laborer | 1 |
| 472141 Painters, Construction, and Maintenance | 3 |
| 49 Installation, Maintenance, and Repair Occupations | |
| 491011 First-Line Supervisors of Mechanics, Installers, and Repairers | 1 |
| 493021 Automotive Body and Related Repairers | 1 |
| 51 Production Occupations | |
| 512099 Assemblers and Fabricators, All Other | 5 |
| 514000 Metal Workers and Plastic Workers | 2 |
| 519112 Painters, Transportation Equipment | 1 |
| 519121 Coating, Paint, and Spraying Machine Setters, Operators, and Tenders | 1 |
| 519122 Painters, Transportation Equipment | 5 |
| 519199 Production Workers, All Other | |
| 53 Transportation and Material Moving Occupations | 3 |
| 537051 Industrial Truck and Tractor Operators | 1 |
| Total # cases | 27 |
Summary of the Processes and Trends Associated with Isocyanate-Induced Asthma
| Process | # Isocyanate-induced asthma cases | # Cases involving large objects | # Cases indirect exposure |
|---|---|---|---|
| Painting (total cases) | |||
| Automotive | 8 | 2 | 1 |
| Industrial coating | 4 | 4 | 1 |
| Signs | 2 | 1 | – |
| Unknown | 1 | – | – |
| Manufacturing | 2 | – | 2 |
| Packaging (shipment of goods) | 2 | – | – |
| Building insulation | 1 | – | 1 |
| Adhesives in aircraft mfg. | 2 | 2 | – |
| Truck bed liner application | 2 | – | – |
| Resin and molds in production mfg. | 2 | – | 1 |
| Sealant | 1 | – | – |
| Total | 27 | 9 | 6 |
Characterization of Isocyanate-Induced Asthma Cases Identified Through a Surveillance System
| ID | Job Title | NAICS | Process (Isocyanate) | Respiratory Protection | Asthma |
|---|---|---|---|---|---|
| 1 | Missile Craftsman | 541330 | Respirator used, type not specified. | NOA | |
| 2 | Painter, industrial equipment | 336612 | Had used APR. Began using a SAR at symptom onset. | NOA | |
| 3 | Painter, concrete coating | 238320 | Half mask, SAR used inconsistently -indirect exposure. | NOA | |
| 4 | Painter, industrial journeyman | 924110 | ‘Full’ PPE required when spraying product; injured worker felt exposure came from handling containers in storage area, when no PPE used. | NOA | |
| 5 | Painter, industrial signs | 238320 | Dust mask | NOA | |
| 6 | Painter and sign fabricator | 339950 | APR | WAA | |
| 7 | Painter | 325510 | Half-face occasionally worn. | NOA | |
| 8 | Forklift driver | 313230 | None used – indirect exposure. | NOA | |
| 9 | Equipment technician | 325510 | Occasionally wears half face APR and PAPR – indirect exposure. | NOA | |
| 10 | Assembler | 326199 | Unknown | Unk | |
| 11 | Aerospace assembler | 332999 | Unknown | WAA | |
| 12 | Assistant, residential foam insulator | 238310 | Dust mask at first SOB episode, APR at second episode. Indirect exposure. | RADS | |
| 13 | Unknown | 336411 | Unknown | NOA | |
| 14 | Interiors mechanic | 336411 | Unknown | NOA | |
| 15 | Mgr. and Sprayer, truck bed linings | 811121 | APRs and PAPR for 2.5 years, then SAR for the last 9 months. | NOA | |
| 16 | Sprayer, truck bed linings | 811121 | Full face SAR. Faulty air supply to respirator. | NOA | |
| 17 | Sprayer; mold maker | 327991 | Unknown | WAA | |
| 18 | Tire press operator | 423990 | None used – indirect exposure. | NOA | |
| 19 | Production Worker | 332321 | Unknown | RADS | |
| 20 | Painter and Stainer | 336214 | Unknown | NOA | |
| 21 | Firefighter, fire truck fabricator, painter | 922160 | Dust mask | NOA | |
| 22 | Manager, automotive office | 811121 | None used – indirect exposure. | NOA | |
| 23 | Painter, automotive | 811121 | Inconsistent use of APR and SAR | WAA | |
| 24 | Painter, automotive | 811121 | SAR used | NOA | |
| 25 | Painter and Mgr., automotive | 811121 | PPE not used 10 years ago. | NOA | |
| 26 | Painter, automotive | 811121 | Half-face APR at time of attack. Wore PAPR after attack. | WA A | |
| 27 | Painter, automotive | 811121 | Full face SAR used in paint booth. | NOA |
SENSOR Asthma Classification for Isocyanate-Induced Asthma Cases Compared to “All Other” Asthma Cases
| Asthma cases from isocyanates 1999 – 2010 | Asthma cases from “all other” agents 2001 – 2010 | |
|---|---|---|
| Total # Cases | 27 | 1438 |
| -Males (%) | 24 (89) | 590 (38) |
| # Classified with Diagnosis | 26 | 571 |
| New Onset Asthma (%) | 21 (81) | 301 (52) |
| - | ||
| Work-Aggravated Asthma (%) | 5 (19) | 270 (47) |
One question answered through the review of surveillance interview data and medical records was the number of spray operation cases (n = 20) which involved large objects difficult to ventilate. Eighteen of the 20 asthma cases involving a spray application had a sufficient description of the object being painted to determine this, and 9 of these 18 cases were found to involve large, awkward, or outdoor (fixed) objects (
A second question answered through data review was whether workers handled isocyanates directly (e.g., operated the spray gun or applicator) or indirectly (e.g., assisted spray operations or performed associated tasks nearby). Twenty-four of the 27 asthma cases had enough information for this to be assessed. Six of these 24 workers (25%) developed new-onset asthma from indirect exposure to isocyanates (see
A third observation from the surveillance data was two cases in which notable exposure occurred outside of the main spray task with reports of dermal exposure. Case 15 was a truck bed liner applicator, and he indicated that while he always wore a respirator (various types) when spraying the truck liner inside a ventilated booth, he did not wear personal protective equipment (PPE) while trimming masking tape off the vehicles outside the booth (
Overall, some type of paint process was responsible for more than half (n = 15, 56%) of the 27 asthma cases from isocyanate exposure (
Information on respiratory protection was obtained through data review for 18 (67%) of the 27 cases. Three cases stated clearly that no respiratory protection was worn (2 of these were indirect exposure). Three injured workers referenced using a dust mask. Four injured workers clearly sought improved respiratory protection after symptom onset or asthma diagnosis: one case adopted progressively greater protection through initially using an air-purifying respirator (APR), then a powered-air-purifying respirator (PAPR), and finally a supplied-air respirator (SAR). Seven cases reported using more than one type of respirator. One case reported that while an APR was used, it was often removed so that the worker could breathe. Detailed information as to the effectiveness of respiratory protection programs, fit tests, or training was typically not available in the interview and medical record information.
Limited information on employment length before diagnosis was available for 24 cases (data not shown). Work history was of somewhat limited value because the length of employment does not necessarily indicate when isocyanate exposure may have started. For example, the introduction of a new process, product, or job reassignment could create a new exposure after many years of employment. Nonetheless, four (17%) cases were with their employer for 12 months or less before being diagnosed with isocyanate-induced asthma. At the opposite end of employment length, an equal proportion (4 cases, 17%) worked for 20 years or more with their employer before diagnosis. Six (25%) cases worked for 1 to 5 years, 5 (21%) worked 6 to 15 years, and 5 (21%) had worked 16 to 20 years for their employer before developing isocyanate-induced asthma.
The injured worker's employment and health outcome after diagnosis was determined for 16 cases (data not shown). A total of 11 workers left work permanently, while 5 workers returned to the workplace under modifications. At the time records were reviewed, 3 of the 5 returning workers reported a successful return with symptom resolution, 1 worker returned but was looking for a new career, and the final worker returned to work but the medical record did not indicate whether his or her return was successful or not.
The total compensable and medical-only cost for isocyanate-induced asthma was approximately $1.7 million; this was 14% of the total claims cost for asthma claims from all other agents, which totaled $12.5 million (see
Workers' Compensation Cost and Time Loss for Isocyanate-Induced Asthma Cases Compared to All Other Asthma Cases
| Cost | Isocyanate-induced asthma cases 1999–2010 | All other asthma cases 2001–2010 | |
|---|---|---|---|
| Total # All Cases | n = 22 | n = 839 | |
| Total cost ($) | 1,723,867 | 10,765,746 | |
| Median ($) | 22,885 | 520 | |
| Medical-only ($) | n = 8 | n = 584 | |
| Median | 1,173 | 398 | |
| Q1–Q3 | 1,099–1,247 | 154–881 | |
| Max | 88,229 | 75,894 | |
| Compensable ($) | n = 14 | n = 255 | |
| Median | 48,112 | 3,366 | |
| Q1 – Q3 | 17,632–82,213 | 719–19,546 | |
| Max | 593,032 | 554,944 | |
| Time loss (days) | n = 14 | n = 255 | |
| Median | 367 | 39 | |
| Q1 – Q3 | 56–954 | 0–80 | |
| Max | 2,375 | 3,788 |
Review of the 27 isocyanate-induced asthma claims has identified three important observations concerning exposure to isocyanates in the workplace. First, isocyanate-induced asthma is associated with spray application on large, awkward-shaped, or fixed outdoor objects. Second, workers who do not directly handle isocyanates (indirect exposure) can experience an isocyanate dose substantial enough to cause asthma. Third, exposure from secondary tasks such as cleanup and self-reports of dermal exposure contributed to symptoms in two cases. While the majority of cases stemmed from automotive spray applications and processes involving isocyanate-based foam (manufacture, shipment packaging, and insulation) two unusual work processes were identified and are discussed in further detail below. One final observation discussed below regards respiratory protection, and its role in preventing isocyanate-induced asthma.
First, the observation of respiratory disease associated with large-object spraying is supported by exposure assessment conducted by Janko et al.(
Second, six cases document new-onset asthma to isocyanates from indirect exposure. Three of the cases involve injured workers who typically might not be enrolled in an employer's respiratory protection program such as forklift driver, equipment technician, and automotive office manager. Two additional cases occurred in workers who were not spraying isocyanate product directly, but were indirectly exposed while assisting lead sprayers. Half of the indirect-exposure cases occurred from exposure to MDI associated with the manufacturing of MDI-based foam. The observation of indirect exposure underscores the importance of: a) isocyanate source control, particularly for MDI-based manufacturing processes and b) the use of ventilation and respiratory protection for assistants working in close proximity to an isocyanate application.
The third observation relates to two cases presented here in which injured workers were exposed to isocyanates during secondary tasks (such as cleanup) and reported dermal exposure as contributing to their symptoms. There is evidence from animal toxicity studies(
Limiting dermal exposure to isocyanates is a prudent approach in the prevention isocyanate-induced asthma.(
Two cases reported here involve work processes not commonly associated with occupational asthma. The first involved the use of an MDI-based sealant in insulated glass manufacturing. The production worker (case 19), who had 31 years experience at the facility, experienced respiratory irritation within 30 days of using the MDI-based sealant during window production. The worker's respiratory symptoms resolved when the worker was retrained into the facility's service department. The second processes (case 3) involved the application of an MDI-based protection liner (similar to truck bed liners) inside a city sewer pipe. The worker developed new-onset asthma from indirect exposure as a line tender working inside the pipe during the liner application. The purpose of installing the isocyanate-based liner was to prevent corrosion and to extend the service life of the sewer pipe.
The majority of cases reported here are for exposure to processes that are similar to other cases previously reported. The most common work process presented here is exposure to automotive paints, a process that is well known to cause respiratory disease,(
Exposure to isocyanates during foam manufacturing is well known to be associated with respiratory illness,(
Regarding isocyanate exposure in workplaces overall, there are industrial processes associated with isocyanate-induced respiratory illness that are not reported here. In the wood products industry for example, isocyanate exposure in wood-chip board manufacturing(
Isocyanate-exposed workers reported using all types of respiratory protection, from dust masks through supplied air systems (
The second observation is tied to the association of asthma from exposure to painting large objects that are difficult to ventilate. While there is evidence that respiratory protection can reduce isocyanate exposure in spray operations,(
The substitution of isocyanates with less hazardous chemicals could reduce the risk of respiratory illness and is the preferred hierarchy of control. The development, testing, and adoption of isocyanate-free formulations is currently limited and varies among the many processes and products that utilize isocyanates. Toxicity testing and health evaluation of isocyanate-free products are needed to establish the safety of new chemical formulations; this is an area in need of further research and development.
It is probable that the 27 cases reported here do not fully reflect the full burden of occupational asthma caused by isocyanates in the workplace. Work-related asthma is generally thought to be under-recognized, under-reported, and poorly evaluated in the general medical community,(
From a logistical perspective, there are limitations to identifying cases that have been filed and bringing them into the surveillance system. The surveillance system relies on a text word search for the word “asthma” (including misspellings) on the claim form jointly filed by the injured worker, employer, and health care provider to initiate the workers' compensation claim. Therefore claims with no (blank) text information or for which asthma is not recognized at the time of claim initiation are not brought into the surveillance system. Workers employed by a self-insured employer may not be brought into the surveillance system because those claim records are often incomplete.
The medical record review that was done to identify trends (such as direct vs. indirect isocyanate handling) is based on information such as employer-provided job descriptions or statements made from injured workers to their doctor. This information was not validated independently by the authors. Additionally, for indirectly exposed workers, the information does not explicitly rule out the possibility of direct handling at some point in their past work history.
No attempt was made to differentiate between the monomeric and oligomeric forms of isocyanates associated with illness, as this requires product MSDS sheets (not always available) to ascribe this level of detail on a case-by-case basis. The differentiation between the monomeric and oligomeric isocyanate forms is relevant to exposure assessment and in the application of United States-based occupational exposure levels (OELs). This differentiation is not critical when using the United Kingdom's OEL for all isocyanates which is based on the total reactive isocyanate group (TRIG) and does not differentiate between isocyanate forms.
It is important to note that isocyanate exposure from automotive paints is predominantly for exposure to the oligomeric, not the monomeric form, of HDI and IPDI isocyanate.(
The following summary statements and prevention guidance are based on key observations and trends made following the in-depth review of asthma cases:
Spray application on large objects is associated with isocyanate-induced asthma. Half of the asthma cases associated with spray application occurred during application to large or awkward-shaped objects; exposures can be high because the process is inherently difficult to ventilate effectively. Source control through spray gun technology, maximum paint-transfer efficiency, roller application (vs. spray gun), or other means should be explored for these applications. When source control is difficult to achieve, the protection afforded through administrative controls and PPE is essential to protect the worker. Occupational health professionals could take object size into consideration when targeting interventions or when prioritizing resources for airborne exposure monitoring.
Workers who are indirectly exposed to isocyanates can develop new-onset asthma. While it is understood that source control is required to minimize exposure for employees directly handling isocyanate products, the cases presented here underscore the role that these measures critically provide for employees who are indirectly exposed, such as forklift drivers, maintenance technicians, or others who may enter areas where isocyanates are being used. Employers can and should factor indirect isocyanate exposure into job hazard analyses.
The self-reported information collected through this surveillance system supports the prudent approach to emphasize dermal protection for workers handling isocyanates. The emphasis for dermal protection should include the main isocyanate-based process, but also secondary tasks outside of the main process, such as handling spent containers or for repeated contact—e.g., vehicle unmasking—with uncured isocyanates.
Isocyanate-induced asthma is a burden for both employees and employers and was associated here with lost days from work, disability awards, and workers' compensation costs comprising 14% ($1.7 million) of the total cost for all asthma claims.
Occupational health surveillance data were used to identify exposure characteristics and to make useful observations for the prevention of isocyanate-induced asthma. Injured worker interviews, coupled with medical record data, were rich sources of information with which to characterize the industries, processes, and circumstances associated with isocyanate exposure.
The authors thank Randy Clark, Diana Ceballos, Don Lofgren, and Todd Schoonover for manuscript review. Thanks to Nick Morris for workers' compensation claim review. This work was supported in part by CDC-NIOSH, grant number 5U60OH008487. This article is solely the responsibility of the authors and does not necessarily represent the official views of CDC-NIOSH.