ATLANTA, IL —
OSHA Inspection: HOPKINS AGRICULTURAL CHEMICAL CO.
Complaint inspection · Health discipline
At a glance
On , OSHA opened a complaint health inspection of HOPKINS AGRICULTURAL CHEMICAL CO. in 303 S.W. ARCH ST., ATLANTA, IL 61723 (NAICS 000000). OSHA activity number 101316123.
Where did this inspection happen?
- Establishment
- HOPKINS AGRICULTURAL CHEMICAL CO.
- Site address
- 303 S.W. ARCH ST.
- City
- ATLANTA
- State
- IL
- ZIP
- 61723
- Mailing
- P.O. BOX 398, ATLANTA, IL 61723
What kind of inspection was it?
- Inspection type
- Complaint (B)
- Scope
- Partial (B)
- Discipline
- Health
- Advance notice
- No
- Union status
- N
When did the case open and close?
- Opened
- Closing conference
- Case closed
- Data loaded
Establishment context
- NAICS code
- 000000
- SIC code (legacy)
- 2879
- Employees
- 35
- Ownership type
- A
Citations
15 citations on file for this inspection.
5(a)(1)
- Issued
- Abate by
- Penalty
- Initial $640.00 · Current $330.00 Reduced
27202333
General-duty citation text
Section 5(a)(1) of the Occupational Safety and Health Act of 1970: The %% employer did not furnish employment and a place of employment which were free from recognized hazards that were causing or likely to cause death or serious physical harm to employees in that employees were exposed to: The hazard of inhalation of the toxic pesticides diazinon and terbufos, in excess of the recommended exposure limits for the mixture, the individual recommended limits for each substance, and the ceiling limits for the terbufos. a) The diazinon formulator was exposed to diazinon at an eight-hour time-weighted average level of 0.2487 milligrams per cubic meter (mg/m3) approximately 2.5 times the threshold limit value of 0.1 mg/m3. He was also exposed to a mixture of diazinon and terbufos approximately 2.6 times the recommended exposure limit for this mixture. The recommended exposure limits for diazinon and terbufos are 0.1 milligrams per cubic meter (mg/m3) and 0.05 mg/m3, respectively. These limites were established to prevent the respiratory sensitization, cholinesterase inhibition, and irritating effects of the organophosphates, diazinon and terbufos. Sampling was conducted 373 minutes on January 21, 1988. The unsampled period of 107 minutes was assumed to be zero exposure. b) The counter formulator was exposed to terbufos at a ceiling level of 0.2523 mg/m3, approximately 1.4 times the permissible ceiling exposure limit of 0.2 mg/m3 and an eight-hour time-weighted average of 0.2271 mg/m3 approximately 1.4 times the threshold limit value of 0.05 mg/m3. He was also exposed to a mixture of diazinon and terbutos approximately 4.6 times the recommended exposure limit for this mixture. The recommended exposure limits for diazinon and terbutos are 0.1 mg/m3 and 0.05 mg/m3, respectively. These limits were established to prevent the respiratory sensitization, cholinesterase inhibition, and irritating effects of the organophosphates, diazinon and terbufos. Sampling was conducted for 432 minutes on January 28, 1988.Zero exposure was assumed for the unsampled period of 48 minutes. c) The counter sealer was exposed to terbufos at an eight-hour time- weighted average (TWA) of 0.1047 mg/m3, approximately 2.1 times the recommended TWA of 0.05 mg/m3. He was also exposed to a mixture of diazinon and terbufos approximately 2.1 times the recommended exposure limit for this mixture. The recommended exposure limits for diazonon and terbufos are 0.1 mg/m3 and 0.05 mg/m3, respectively. These limits were established to prevent the respiratory sensitization cholinesterase inhibition, and irritating effects of the organophosphates, diazinon and terbufos. Sampling was conducted for 404 minutes on January 21, 1988. Zero exposure was assumed for the unsampled period of 76 minutes. d) The counter sealer was exposed to terbufos at a ceiling level of 0.23 mg/m3, approximately 1.2 times the permissible ceiling exposure limit of 0.2 mg/m3 and an eight-hour time-weighted average (TWA) of 0.1969 mg/m3, approximately 3.9 times recommended TWA of 0.05 mg/m3. He was also exposed to a mixture of diazinon and terbufos approximately 4.0 times the recommended exposure limit for this mixture. The recommended exposure limits for diazinon and terbufos are 0.1 mg/m3 and 0.05 mg/m3, respectively. These limits were established to prevent the respiratory sensitization cholinesterase inhibition, and irritating effects of the organophosphates, diazinon and terbufos. Sampling was conducted for all 411 minutes in January 21, 1988. Zero exposure was assumed for the unsampled period of 69 minutes. e) The counter sealer was exposed to terbufos at an eight-hour time- weighted average (TWA) of 0.0632 mg/m3, approximately 1.3 times the recommended TWA of 0.05 mg/m3 a mixture of diazinon and terbufos approximately 1.3 times the recommended exposure limit for this mixture. The recommended exposure limits for diazinon and terbufos are 0.1 milligrams per cubic meter (mg/m3) and 0.05 mg/m3, respectively. These limtis were established to prevent the respiratory sensitization cholinesterase inhibition and irritating effects of the organophosphates, diazinon and terbufos. Sampling was conducted 449 minutes on January 28, 1988. Zero exposure was assumed for the unsampled period of 31 minutes. f) The counter packer was exposed to terbufos at a ceiling level of 0.25 mg/m3, approximately 1.3 times the permissible ceiling exposure limit of 0.2 mg/m3 and eight-hour time-weighted average of 0.2297 mg/m3, approximately 4.6 times the recommended TWA of 0.05 mg/m3. He was also exposed to a mixture of diazinon and terbufos approximately 4.6 times the recommended exposure limits for diazinon and terbufos are 0.1 mg/m3 and 0.05 mg/m3, respectively. These limits were established to prevent the respiratory sensitization cholinesterase inhibition, and irritating effects of the organophosphates, diazinon and terbufos. Sampling was conducted for 441 minutes on January 28, 1988. Zero exposure was assumed for the unsampled period of 39 minutes. g) The counter packer was exposed to terbufos at an eight-hour time- weighted average of 0.1913 mg/m3, approximately 3.8 times the recommended TWA of 0.05 mg/m3. He was also exposed to a mixture of diazinon and terbufos approximately 3.9 times the recommended exposure limit for this mixture. The recommended exposure limits for diazinon terbufos are 0.1 mg/m3 and 0.05 mg/m3, respectively. These limits were established to prevent the respiratory sensitization cholinesterase inhibition, and irritating effects of organophosphates, diazinon and terbufos. Sampling was conducted for 439 minutes on January 28, 1988. Zero exposure was assumed for the unsampled period of 41 minutes. h) The diazinon sealer was exposed to diazinon at an eight-hour time- weighted average of 0.111 mg/m3, approximately 1.1 times the recommended TWA of 0.1 mg/m3 a mixture of diazinon and terbufos approximately 1.2 times the recommended exposure limit for this mixture. The recommended exposure limits for diazinon and terbufos are 0.1 milligrams per cubic meter (mg/m3) and 0.05 mg/m3, respectively. These limits were established to prevent the respiratory sensitization cholinesterase inhibition, and irritating effects of the organophosphates, diazinon and terbufos. Samping was conducted 444 minutes on January 28 1988. Zero exposure was assumed for the unsampled period of 36 minutes. Feasible and effective abatement can be expected to include, but is not limited to: 1) Replacement and maintenance of the seals on the mixers. 2) Inspection, repair, and maintenance of the joints and connections on the transfer piping. 3) Maintenance of negative pressure in the mixers. 4) Development and use of alternate quality control sampling techniques not requiring direct employee exposure. 5) Cleaning and decontamination of the counter mixing floor. 6) Development of an interlocking system for the automatic bag hanger on the counter line to prevent discharge of the pesticide when the bag is not in place. 7) Repair and maintenance of the existing ventilation system to ensure a continuous and unobstructed exhaust rate of at least 200 fpm. 8) Installation of a slotted, flanged exhaust system along the length of the bag hanger and sealer on the counter line. Enclose the remaining length of the conveyor. 9) Modification of the counter conveyor line to minimize the number of bags damaged. 10) Installation of a holding bin with a vacuum system equipped with high efficiency filters to remove spilled pesticide on the counter line. 11) Enclosure of the diazinon mixer. 12) Installation of slotted ventilation system at the raw material entry point at the diazinon screw conveyor. 13) Assure that all spills are cleaned with vacuums equipped with high efficiency filters. Disclaimers: a) The employer is not limited to the abatement methods suggested by OSHA. b) The methods explained are general and may not be effective in all cases. c) The employer is responsible for selecting and carrying out an appropriate abatement method. STEP 1: - Effective respiratory protection shall be provided and used by exposed employees as an interim protective measure until feasible engineering and/or administrative controls can be implemented or whenever such controls fail to reduce employee exposure to within permissible exposure limits. STEP 2: - Submit to the Area Director a written detailed plan of abatement outlining a schedule for the implementation of engineering and/or administrative measures to control employee exposure to hazardous substances as referenced in this citation. This plan shall include, at a minimum, target dates for the following actions which must be consistent with the abatement dates required by this citation: 1) Evaluation of engineering/administrative control options; 2) Selection of optimum control methods and completion of design; 3) Procurement, installation and operation of selected control measures; 4) Testing and acceptance or modification/redesign of controls. All proposed control measures shall be approved for each particular use by a competent industrial hygienist or other technically qualified person. Ninety (90) day progress reports are required during the abatement period. STEP 3: - Abatement shall have been completed by the implementation of feasible engineering and/or administrative controls upon verification of their effectiveness in achieving compliance.
Recent events (2)
- — I (S) $330.00
- — Z (S) $640.00
1910.134 B10
- Issued
- Abate by
Recent events (2)
- — I (S)
- — Z (S)
1910.134 E04
- Issued
- Abate by
1910.23 C01
- Issued
- Abate by
- Penalty
- Initial $350.00 · Current $179.00 Reduced
Recent events (2)
- — I (S) $179.00
- — Z (S) $350.00
1910.95 D03
- Issued
- Abate by
- Penalty
- Initial $640.00 · Current $327.00 Reduced
Recent events (2)
- — I (S) $327.00
- — Z (S) $640.00
1910.95 I02 I
- Issued
- Abate by
1910.95 K01
- Issued
- Abate by
1910.133 A01
- Issued
- Abate by
- Penalty
- Initial $640.00 · Current $327.00 Reduced
Recent events (2)
- — I (S) $327.00
- — Z (S) $640.00
1910.151 C
- Issued
- Abate by
1910.212 A01
- Issued
- Abate by
- Penalty
- Initial $350.00 · Current $179.00 Reduced
Recent events (2)
- — I (S) $179.00
- — Z (S) $350.00
1910.212 A03 II
- Issued
- Abate by
- Penalty
- Initial $350.00 · Current $179.00 Reduced
Recent events (2)
- — I (S) $179.00
- — Z (S) $350.00
1910.1200 F04 I
- Issued
- Abate by
- Penalty
- Initial $350.00 · Current $179.00 Reduced
Recent events (2)
- — I (S) $179.00
- — Z (S) $350.00
1910.1200 F04 II
- Issued
- Abate by
Recent events (2)
- — I (S)
- — Z (S)
1910.157 C01
- Issued
- Abate by
1910.95 G05 I
- Issued
- Abate by
Recent events (3)
- — P (S)
- — I (S)
- — Z (S)
More inspections at HOPKINS AGRICULTURAL CHEMICAL CO.
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RANDOLPH, WI—1986-04-22 00:00:00
HOPKINS AGRICULTURAL CHEMICAL CO.
View HOPKINS AGRICULTURAL CHEMICAL CO.'s full OSHA safety record →
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Source
This record is reproduced from the U.S. Department of Labor Open Data API (OSHA inspection dataset). The original IMIS detail view is available at OSHA's Establishment Search for activity number 101316123.