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 NIOSH Publication No. 2004-146

Worker Health Chartbook 2004

 Worker Health Chartbook > Chapter 2 > Poisoning
Chapter 2: Fatal and Nonfatal Injuries, and Selected Illnesses and Conditions

Poisoning

Preventing occupational poisonings and pesticide-related illnesses and injuries requires ongoing activities to determine the underlying causes of overexposure to chemicals and pesticides in the workplace. Surveillance promotes prevention by describing the magnitude and distribution of these adverse health conditions among workers and by serving as an early warning system of harmful effects not detected by product manufacturers. Two sources of data advance these surveillance objectives: the BLS annual survey of employers for occupational poisonings (part of SOII) and case-based reporting of pesticide-related illnesses and injuries by SENSOR.

Annual Survey of Employers: Reports of Occupational Poisonings (BLS)

Poisonings (systemic effects of toxic materials) include poisoning by the following: (1) lead, mercury, cadmium, arsenic, or other metals; (2) carbon monoxide, hydrogen sulfide, or other gases; (3) benzol, carbon tetrachloride, or other organic solvents; (4) insecticide sprays such as parathion and lead arsenate; and (5) other chemicals such as formaldehyde, plastics, and resins. During 1972–2001, the number of occupational poisonings ranged from a high of 7,600 cases in 1993 to a low of 2,800 cases in 2001 (Figure 2–151). Rates varied during 1984–2001 from a high of 1.0 per 10,000 full-time workers in 1993 to a low of 0.3 in 2001 (Figure 2–152). Within reporting States in 2001, the number of occupational poisoning cases ranged from fewer than 50 to 300 (Figure 2–153). Rates in 2001 varied by State from a low of less than 0.1 per 10,000 full-time workers in many States to a high of 1.2 in Maine; the U.S. rate was 0.3 per 10,000 full-time workers (Figure 2–154).

Magnitude and Trend

How did the number of occupational poisonings change during 1972–2001?
chart thumbnail - click on image for larger view.Figure 2-151 Number of occupational poisoning cases in private industry, 1972-2001. During 1972-2001, occupational poisonings peaked at 7,400 cases in 1974, declined to 3,000 cases in 1983, peaked again in 1993 at 7,600 cases, then declined to 2,800 cases in 2001. (Source: BLS [2002].)

How did the rates of occupational poisonings change during 1984–2001?
chart thumbnail - click on image for larger view.Figure 2-152 Annual rates of occupational poisoning in private industry, 1984-2001. BLS reported poisoning rates ranging from a high of 1.0 per 10,000 full-time workers in 1993 to a low of 0.3 in 2001. Occupational poisonings have low rates and generally account for only about 1% of all illnesses. (Source: BLS [2002].)

Numbers and Rates among States

How did the number of occupational poisonings differ by State in 2001?
chart thumbnail - click on image for larger view.Figure 2-153 Number of occupational poisoning cases in private industry by State, 2001. The number of occupational poisoning cases within reporting States ranged from fewer than 50 to 300 in 2001. BLS reported a total of 2,800 occupational poisoning cases in 2001. States with the highest numbers included California (300), Illinois (200), Indiana (200), Michigan (200), Missouri (200), North Carolina (2002) and Texas (200). (Source: BLS [2002].)

How did the rates of occupational poisoning differ by State in 2001?
chart thumbnail - click on image for larger view.Figure 2-154 Incidence rates for occupational poisoning in private industry by State, 2001. Occupational poisoning rates varied from a low of less than 0.1 per 10,000 full-time workers in many States to a high of 1.2 per 10,000 full-time workers in Maine. The U.S. rate was 0.3 per 10,000 full-time workers. (Source: BLS [2002].)

Case-Based Reporting of Pesticide-Related Illness and Injury (SENSOR)

Pesticides are substances used to prevent, destroy, repel, or mitigate pests. They are used to protect the food supply and to control disease vectors. No perfectly safe form of pest control exists. Pesticides continue to raise concerns about their potential toxicity to humans. NIOSH provides technical and financial support for State-based surveillance of acute, occupational, pesticide-related illness and injury through the SENSOR program. The SENSOR-pesticides program is partially funded by the U.S. Environmental Protection Agency (EPA).

Between 1998 and 1999, a total of 1,009 cases of acute, pesticide-related occupational illness were identified by the seven States participating in the SENSOR-pesticides program (Arizona, California, Florida, Louisiana, New York, Oregon, and Texas) [Calvert et al. 2004]. Cases totaled 523 in 1998 and 486 in 1999. The incidence rate was 1.17 per 100,000 full-time workers overall, 18.2 for agricultural workers, and 0.53 for nonagricultural workers. As measured by days away from work during this period, the severity of most pesticide-related illnesses was low for 69.1% of cases, moderate for 29.6%, and high for 0.4%; three fatalities were identified [Calvert et al. 2004].

Age

How did the rates of pesticide-related illnesses differ by age of worker and industry during 1998–1999?
chart thumbnail - click on image for larger view.Figure 2-155 Incidence rates of pesticide-related illness by age and industry, 1998-1999. Among industry sectors, agriculture accounted for the highest incidence rates of pesticide-related illness, ranging from 5 to 27 cases per 100,000 full-time workers. Rates were highest among younger workers, peaking among those aged 20-24, and decreasing with increasing age. (Sources: NIOSH [2002d]; Calvert [2002].)

Sex

How were pesticide-related illnesses distributed by sex of worker during 1998–1999?
chart thumbnail - click on image for larger view.Figure 2-156 Distribution and number of pesticide-related illnesses by sex of worker, 1998-1999. Sex of worker was known for 1,006 of the 1,009 pesticide-related occupational illness cases during 1998-1999. Male workers accounted for 63% (636) of all cases and female workers accounted for 36.7% (370 cases). (Sources: NIOSH [2002d]; Calvert [2002].)

Occupation

Which agricultural occupations accounted for the most pesticide-related illnesses during 1998–1999?
chart thumbnail - click on image for larger view.Figure 2-157 Distribution and number of pesticide-related illnesses among agricultural workers by occupation, 1998-1999. Farm workers reported by far the most pesticide-related illnesses (71.8% or 336 cases) during 1998-1999. Other occupations with notable pesticide-related illnesses included graders and sorters (7.5% or 35 cases) and nursery workers (4.7% or 22 cases). (Sources: NIOSH [2002d]; Calvert [2002].)

Industry

Which industry sectors accounted for the most pesticide-related illnesses during 1998–1999?
chart thumbnail - click on image for larger view.Figure 2-158 Distribution and number of pesticide-related illnesses by industry, 1998-1999. Employer or industry data were available for 911 of the 1,009 pesticide-related illness cases during 1998-99. Most of these cases (51.5% or 469 cases) were from the agricultural sector. Services accounted for 19.4% (177 cases) and transportation, communication, and public utilities accounted for 9.3% (85) cases. (Sources: NIOSH [2002d]; Calvert [2002].)

Agent or Exposure

Which classes of pesticides were responsible for reported cases of illness during 1998–1999?
chart thumbnail - click on image for larger view.Figure 2-159 Distribution and number of pesticide-related illnesses by pesticide functional class, 1998-1999. Insecticides were responsible for 49% (494 cases) of the 1,009 reported occupational illnesses related to pesticides. (Sources: NIOSH [2002d]; Calvert [2002].)

Which chemical classes of insecticides were responsible for reported cases of illness during 1998–1999?
chart thumbnail - click on image for larger view.Figure 2-160 Distribution and number of pesticide-related illnesses by insecticide chemical class, 1998-1999. The following insecticide classes were most commonly responsible for pesticide-related illnesses during 1998-1999: organophosphorus (47.2% or 233 cases), N-methyl carbamate (15.4% or 76 cases), pyrethroid (11.1% or 55 cases), and pyrethrin (9.3% or 46 cases). (Sources: NIOSH [2002d]; Calvert [2002].)

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