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Mr. John Smith, the plant manager for Acme Automotive Parts (AAP
QUESTION
Introduction – This section should summarize the operations at the plant and why the industrial hygiene sampling is being performed.
Hazard Assessment – This section should identify the health hazards that you identified for each area at the facility.
Sampling Plan – This section will summarize the sampling that you performed. Include the types of samples you collected and the NIOSH or OSHA sampling/analytical methods you used.
Sample Results – This section will include the results from the sampling that you calculated. You can present the results in a tabular form or an equivalent method as long as the results are clearly displayed. Your results should include samples’ locations, names of employees who were sampled (make the names up), sample times (start, finish, and total times), volumes, and results in the proper units.
Evaluation of Sample Results – In this section, you should compare the sample results to existing occupational exposure limits (OELs). You can use OSHA permissible exposure limits (PELs) or other guidelines—just make sure to explain why you chose the OELs you used. You should also state whether the resulting risks are acceptable or unacceptable and the requirements for control methods.
Recommendations – Here you will summarize the control methods you recommend that the plant implement. Include all engineering controls, administrative controls, and personal protective equipment (PPE) you believe are necessary. Do not forget to include recommendations for PPE during the time it will take to implement the other controls. For respiratory protection, you must specify the level of protection (type respirator) and the types of any cartridges that would be required. Do not forget to list any written programs that you believe the plant will need.
Future Needs – Complete your report by including any recommendations for additional IH sampling you believe are necessary to evaluate the effectiveness of the controls that you recommended.
Your final report must be a minimum of three pages in length, not including title and reference pages. You must use at least two references. The textbook may be used as one reference. All citations and in-text citations must be formatted according to APA standards.
Subject | Report Writing | Pages | 6 | Style | APA |
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Answer
Occupational Safety and Health Final Report
1.0 Introduction
AAP is a manufacturer of support parts for new automobiles and serves as a small supplier to Nissan, Honda, and Volkswagen facilities in the United States. The plant consists of 8 sections from which their processes are performed. These include shipping/receiving, hydraulic presses, metal working lines, robotic welding stations, hand-welding stations in rework areas, two small paint booths, a quality assurance/quality control (QA/QC) laboratory, and a final inspection area. Industrial hygiene sampling is performed to demarcate the level of exposure on a full shift – typically 8 hours or less – of air sample (Paik & Zalk, 2019).
2.0 Hazard Assessment
This section identifies six health hazards identified each area at the facility and are subsequently tabulated:
|
Hazard |
Operational area |
1 |
Manganese Fume |
Welding areas, notably, hand welding and robotic welding |
2 |
1,2,4 Trimethylbenzene |
Paint Booth |
3 |
Metal working fluid |
Metal working lines |
4 |
Copper fume |
Hand welding |
5 |
Lead fume |
Paint Booth and welding areas |
6 |
Toluene |
Paint Booth |
7 |
Xylene |
Paint Booth |
3.0 Sampling Plan
This section covers four hazards for which sampling was done:
Manganese Fume
Personal sampling method was used for the Manganese Fumes. A personal sample was collected and analyzed for three parameters, namely, concentration, flow rate, and minimum sample time (Hulo et al., 2014). The concentration of the fumes was measured using an electrochemical sensor, while flow rate, and sample time were determined using the rotameter.
Toluene (Paint)
Using coconut charcoal adsorbent tube media and toluene for calibration of sampling train, the minimum sample time for Toluene was calculated. The area sampling method was used by dividing the exposure area into small sub-areas from which small portions of the as is collected for analysis (Esmaelnejad et al., 2015).
Metal Working Fluids
. Thoracic particulate, a type of representative fraction of inhaled particles was. Ternary solvent was used as sampling media and the sample train was calibrated using the National Institute of Standards and Technology Class S-1.1 weights. A personal sampling method was also executed as sample collection tools were obtained from individuals.
Noise Exposures
A personal sampling method was used to evaluate noise levels in the facility. Using the dosimeter- calibrated sampling train, noise samples were obtained in strategic places specifically adjacent to the grinding and welding areas.
4.0 Sample Results
This section presents sampling results for each of 7 hazards. Subsequently, he sampling location, the sampled employee, duration of sampling, and results are tabulated as shown:
Table 2
6 |
Toluene |
Paint Booth |
Paint Booth Operators Painter |
0800hrs-2000hrs |
12 |
2.604 mg/m3 (0.691 ppm) (OSHA PEL limit, 100 ppm TWA) |
7 |
Xylene |
Paint Booth |
Painter Spray paint operators |
0800hrs-2000hrs |
12 |
0.417 mg/m3 (0.095 ppm) (100ppm TWA limit) |
hydraulic press, metalworking line, robotic welding, and paint booth
5.0 Evaluation of Sample Results
From the tabulated results, only copper fumes obtained from calculations as 0.1344mg/m3 concentration, exceeds the set Occupational Safety Health Association permissible limit (OSHA PEL) of 0.1 mg/m3 TWA. Inferentially, potential hand welding locations such as the hydraulic press, metalworking line, robotic welding, and paint booth have the greatest risk of copper fume exposure. However, hazards from manganese fume, 1, 2, 4 Trimethylbenzene, Lead fume, Toluene, metal working fluid, xylene are well below OSHA PEL limits as shown in the table. It also means that locations such as shipping and receiving, QA/QC laboratory and final inspection are all within the OSHA PEL recommended range.
However, when perceived in terms of the recommended OSHA action level of 8 hours, it is observed that activities at the hydraulic press, metalworking line, robotic welding, and paint booth all last 12 hours. By inference the preceding activities have high concentrations are considered to be more than the OSHA permitted action level of 8 hours (US Department of Labor, 2020). Such a period, as well as the results that emanated from such periods, are over OSHA action level.
6.0 Recommendations
Assessment of Hazards at AAP confirms the presence of risk in all stages of operation. As such at a basic level, the firm can implement measures to control hazards. Some recommendations are subsequently tabulated:
- The firm should ensure that workers are adequately trained operation of mechanical load shifting devices such as cranes, hoists, hand trucks and forklifts) can avoid awkward loads.
- The firm should also provide personal protective equipment (PPE) and grinders. Similar equipment should have guarding of machinery guidelines such as Barrier guards, two-hand tripping devices and electronic safety devices. Additionally PPEs should guarantee safety during grinding, machining, sanding, and riveting by providing safety goggles spectacles fitted with side shields. Face shields should also be provided to shield against splashing of liquefied metal (Automotive Respirators and Safety Products, 2020). Welders should also be provided with helmets, preferably fitted with lift-front window, to provide cover from liquid metal splashes and possible burns. For particulate and chemical protection, particularly during grinding and welding operation should be fitted with exhalation valve on respirators (Automotive Respirators and Safety Products, 2020).
- The firm should also implement a strict rotation policy that ensures that employees do not engage in monotonous tasks for extended durations. The firm should also institute internal mechanism for continuous risk-assessments and pre-operational assessments. Additionally, the firm should ensure that Lockout-Tag out(LOGO) procedures are executed carefully particularly during routine maintenance of machines.
- Finally, evacuation drills in preparation for fire outbreaks should be conducted at least twice monthly.
7.0 Future Needs
Success of the IH sampling approach will invariably depend on preparations undertaken prior to the sampling process. Accordingly a study by Day, Boss, Miller and Wrenn (2016) recommends a three-step process for improvement to the sampling process. First, the firm should conduct a “walk-through investigation” focusing on present state of the buildings, open spaces, and machining areas. Secondly, improvements to the sampling process should be instigated. These changes should be targeted at individuals such as customers and visitors so as to obtain a wider perspective of the risks involved. Finally, interviews focused on employees should be conducted to gather their experiences with regard to internal work spaces and buildings (Day, Boss, Miller and Wrenn, 2016).
|
Hazard |
Sample location |
Employee sampled |
Time |
Duration |
Results |
1 |
Manganese Fume |
Robotic welding Hand welding |
Welder |
0800hrs-2000hrs |
12hours |
0.167mg/m3 (below OSHA PEL threshold of 5mg/m3 TWA) |
2 |
Copper Fume |
Hand welding |
welder |
0800hrs-2000hrs |
12 hours |
0.1344mg/m3 (Below OSHA PEL threshold 0.1 mg/m3) TWA |
3 |
Lead Fume |
Paint Booth |
Steel welders
|
0800hrs-2000hrs |
12 |
0.0417mg/m3 (Below OSHA PEL threshold of 0.05 mg/m3 TWA |
4 |
Metal Working Fluid |
Metal working line |
Riggers, heavy equipment operator, |
0800hrs-2000hrs |
12 hours |
0.694 mg/m3 (Below OSHA PEL threshold of 5mg/m3 TWA) |
5 |
1,2,4 Trimethylbenzene |
Paint Booth |
Paint Booth operators Paint Booth Technicians |
0800hrs-2000hrs |
12 |
0.1042mg/m3 (0.0212 ppm) (OSHA PEL threshold unavailable) |
References
Automotive Respirators and Safety Products. (2020). 3M Automotive Respirators And Safety Products. Retrieved July 14, 2020, from https://multimedia.3m.com/mws/media/103197O/automotive-respirators-and-safety-products.pdf Day, D. W., Boss, M. J., Miller, R. V., & Wrenn, C. (2016). Industrial Hygiene Sampling. Biological Risk Engineering Handbook: Infection Control and Decontamination, 39. Esmaelnejad, F., Hajizadeh, Y., Pourzamani, H., & Amin, M. M. (2015). Monitoring of benzene, toluene, ethyl benzene, and xylene isomers emission from Shahreza gas stations in 2013. International Journal of Environmental Health Engineering, 4(1), 17. Hulo, S., Chérot-Kornobis, N., Howsam, M., Crucq, S., de Broucker, V., Sobaszek, A., & Edme, J. L. (2014). Manganese in exhaled breath condensate: a new marker of exposure to welding fumes. Toxicology letters, 226(1), 63-69. Paik, S. Y., & Zalk, D. M. (2019). A Simple Proposition for Improving Industrial Hygiene Air Sampling Methods. Safety and health at work, 10(3), 389-392. US Department of Labor. (2020). Permissible Exposure Limits / OSHA Annotated Table Z-2. https://www.osha.gov/dsg/annotated-pels/tablez-2.html
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