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HHE Search Results
1058 HHE reports were found based on your search terms. Reports are listed in order of year published with the most recently published reports listed first.
Year Published and Title
(1999) Allgrind Plastics, Inc., West Portal, New Jersey. (Click to open report) In January 1998, the State of New Jersey, Department of Health and Senior Services (NJDHSS), requested technical assistance from the National Institute for Occupational Safety and Health (NIOSH) in investigating a possible health hazard at the Allgrind Plastics, Inc., milling facility in West Portal, New Jersey. Allgrind Plastics is primarily engaged in size reduction of various plastics using attrition mills, knife mills, and hammer mills. In general, the company does many small jobs and thus o... (Click to show more)In January 1998, the State of New Jersey, Department of Health and Senior Services (NJDHSS), requested technical assistance from the National Institute for Occupational Safety and Health (NIOSH) in investigating a possible health hazard at the Allgrind Plastics, Inc., milling facility in West Portal, New Jersey. Allgrind Plastics is primarily engaged in size reduction of various plastics using attrition mills, knife mills, and hammer mills. In general, the company does many small jobs and thus over time has processed many types of plastics. Within the last few years, the company has also been processing organic materials, primarily shark cartilage, into fine powders for use as natural remedies for various diseases. The request was prompted by the death of a 38-year-old employee of an acute asthma attack while at work on April 19, 1997. Prior to his death, the employee had attributed acute asthmatic symptoms to shark cartilage dust on a number of occasions. On May 26-28, 1998, an industrial hygienist and two medical officers from NIOSH, and an industrial hygienist from the NJDHSS, visited Allgrind Plastics. They conducted a walk-through evaluation of the plant, met with all current workers, and reviewed pertinent company records. Subsequent to the visit, former employees were contacted by telephone and questioned regarding work-related symptoms. Also, bulk samples collected at the worksite underwent laboratory analysis. In addition to the site visit noted above, personnel from the NJDHSS conducted a prior site visit on November 14, 1997, and conducted industrial hygiene evaluations, with air sampling of selected processes, on March 12 and April 22, 1998. Personal samples in the shark grinding areas measured 44.7 and 26.4 milligrams per cubic meter of air (mg/m 3 ) total dust and 5.14 and 0.92 mg/m 3 respirable dust on March 12, 1998. During the sampling on April 22, 1998, the personal samples measured 12.3 mg/m 3 total dust and 1.97 mg/m 3 respirable dust, and concentrations of 2.94 mg/m 3 total dust and 0.34 mg/m 3 respirable dust were measured on samplers worn by an operator milling plastic. Area samples for total dust did not exceed 0.43 mg/m 3 , and area respirable dust samples remained below 0.24 mg/m 3 during both days of sampling by NJDHSS. Endotoxin concentrations of bulk samples of shark cartilage did not exceed 1.6 endotoxin units per milligram (EU/mg). It was found that unique exposures exist at Allgrind Plastics due to the production of dusts from materials not normally inhaled. Air monitoring showed that certain processes generated significant airborne concentrations of these dusts. Limited medical experience exists to predict the health effects of many of these dusts after inhalation. However, medical findings noted during the May 1998 site visit were consistent with a significant burden of work-associated respiratory symptoms in current and former workers, many of them irritative in nature. In addition, three workers were identified as being likely to have developed true occupational asthma after working at Allgrind Plastics for a period of months to years. An additional worker was identified with urticaria and angioedema induced by a material in the workplace (ethylene diamine acid phosphate). These findings strongly suggest that a sensitizing substance or substances are present in the workplace and capable of inducing disease. Two materials were identified as particular problems by workers. Shark cartilage dust was the material most frequently identified as troublesome by current and former workers. Ethylene diamine acid phosphate was the second most frequently cited material. Dusts of both appear to be irritating. Ethylene diamine is a well documented sensitizer and has been reported to cause asthma. Shark cartilage has not previously been reported to cause immunologic sensitization but in theory it could. Although dusts generated from both of these materials are regulated under a "particulates, not otherwise classified or regulated (PNOC/R)" standard, this standard is likely not fully protective against the effects of poorly studied but potentially more injurious dusts such as those encountered here. Various industrial hygiene measures are recommended to control dust exposures, not only to the respiratory tract but also to face, eyes, and skin. In addition, worker education, environmental monitoring, and medical surveillance measures are recommended for prevention of disease, as well as for early identification and prevention of disease progression. NIOSH investigators conclude that dusts produced by industrial processes at Allgrind Plastics are a significant health hazard. Many workers have symptoms when exposed to these dusts. Several workers have developed asthma while working at the plant. Two materials, shark cartilage dust and ethylene diamine acid phosphate dust, appear to pose a significant health hazard. The "Recommendations" section of this report provides suggestions for ways to decrease problems caused by these dusts. These include ways to decrease exposure, worker education, ways to detect early illness, and what to do if a worker gets sick.
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(1999) Bio-Solids Land Application Process LeSourdsville, Ohio. (Click to open report) In response to an employee request for a health hazard evaluation (HHE) received on May 29, 1998, the National Institute for Occupational Safety and Health (NIOSH) conducted a site visit at the R.H. Sheppard Co., Inc., facility in Hanover, Pennsylvania. The request asked NIOSH to determine if reported worker health problems were associated with exposure to contaminants in plant No. 1 and Department No. 109, at this automotive power steering unit manufacturer. The reported health problems include... (Click to show more)In response to an employee request for a health hazard evaluation (HHE) received on May 29, 1998, the National Institute for Occupational Safety and Health (NIOSH) conducted a site visit at the R.H. Sheppard Co., Inc., facility in Hanover, Pennsylvania. The request asked NIOSH to determine if reported worker health problems were associated with exposure to contaminants in plant No. 1 and Department No. 109, at this automotive power steering unit manufacturer. The reported health problems included allergic reactions, respiratory infections, and skin and eye irritation. Potential exposures identified in the request included metalworking fluids (MWFs), naptha, and metal dust from grinding. Inadequate ventilation was also noted as a concern.
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(1999) Central Maui Composting Facility Maui, Hawaii. (Click to open report) On March 28, 1995, the National Institute for Occupational Safety and Health (NIOSH) received a management request for a health hazard evaluation from the Maui County Council, Maui, Hawaii. The Council asked NIOSH to evaluate their composting operation since they recently began receiving complaints of poor working conditions from former employees, as well as complaints from neighboring business (Kahului Airport) about odors emitting from the composting site. There was no indication that any curr... (Click to show more)On March 28, 1995, the National Institute for Occupational Safety and Health (NIOSH) received a management request for a health hazard evaluation from the Maui County Council, Maui, Hawaii. The Council asked NIOSH to evaluate their composting operation since they recently began receiving complaints of poor working conditions from former employees, as well as complaints from neighboring business (Kahului Airport) about odors emitting from the composting site. There was no indication that any current employees have or had any health problems associated with the compost operation. This request was also prompted by the NIOSH Alert pertaining to Organic Dust Toxic Syndrome (ODTS). On May 11, 1995, NIOSH investigators conducted an initial site visit to the composting facility. During that site visit, the composting operation was toured, and area air samples were collected for total dusts, bacteria, fungi, and endotoxin. Bulk samples were collected of the various compost products for microbiological analysis. The purpose for collecting theses samples was to determine the microbial activity of the compost. The contractor operating the site was in the process of ending his contract with the County, so very little work was being accomplished at that time. On September 11-13, 1995, a return visit was made to the composting facility to conduct a comprehensive industrial hygiene survey. During that survey, the old contractor was still in the process of leaving and the new contractor preparing to take over operations. During that transition, the old contractor was loading and removing product, while the new contractor was focusing on reducing the stock-pile of accumulated green waste and sewage sludge by mixing one static windrow of compost. A final survey was conducted during June 24-26, 1996. During that survey, the composting site was fully operational under the new management. Many positive changes to the site were obvious, including the reduced stock pile of sewage sludge and green waste, a new office trailer, and most importantly, new front-end loaders equipped with air conditioned enclosed cabs. Other equipment used consisted of a compost mixing truck, a screener, and a new chipper/grinder. Water was also now available from the nearby quarry to spray on the compost and the roads to keep dust down. Total dust concentrations from the samples collected upwind ranged from 0.2 to 21.5 mg/m3, with the highest level measured on the outside of the loader working the greens. Other samples of note were the total and respirable samples collected inside and outside of the cab of a front end loader loading in the greens area. Total dust concentrations inside the cab were 0.69 mg/m3, while concentrations measured outside were 21.5 mg/m3. Respirable dust concentrations inside and outside the cab were 0.3 ands 0.72 mg/m3, respectively with the highest level measured on the access road to the landfill. Bacteria concentrations ranged from none detected (ND) to 8.0 x 107 colony forming units per cubic meter of air (CFU/m3), with the highest levels also measured on the loader at the greens. The primary bacteria identified was Bacillus. Thermophilic bacteria was only detected on the sample collected near the workshop. Fungi concentrations ranged from ND to 2.8 x 106 CFU/m3, with the highest levels measured near chipper/grinder. The primary fungi identified from the samples were Aspergillus and Penicillium. Endotoxin concentrations ranged from none detected (ND) to 3.0 x 105 endotoxin units per cubic meter of air (EU/m3), with the highest concentration measured near the greens chipper/grinder. To reduce this potential hazard it is important to reduce worker exposures by means of either engineering controls (e.g., enclosed cabs), respiratory protection, or a combination of engineering controls and respiratory protection. Samples collected showed that the enclosed cabs, when used properly such as keeping the windows closed, can reduce worker exposures. However, these controls are relatively ineffective if the cab windows are opened during compost handling operations. Also, these results show that individuals in the general area of the composting pads or those not operating enclosed equipment, should either wear respiratory protection or stay upwind during turning operations. The results from this health hazard evaluation has shown that the enclosed machinery cabs on the equipment can reduce exposures. Also, these results show that individuals in the general area of the chipper/grinder should wear respiratory protection during operation. Acceptable levels of airborne microorganisms have not been established. Lack of standardized exposure assessment techniques, inability to measure non-viable organisms, and inter-individual variability in response have confounded efforts to set such standards. Just as individuals vary in their resistance to disease, a few individuals may be particularly sensitive to some of the organisms in compost.
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(1999) City of Springfield, Department of Public Works Composting Facility, Springfield, Missouri. (Click to open report) On March 27, 1995, the National Institute for Occupational Safety and Health (NIOSH) received a management request for a health hazard evaluation from the City of Springfield, Missouri, to assess any possible employee health effects from operation of the city's composting facility. There were no indications that employees have or had any health problems associated with the compost operation. This request was prompted by the publication of the NIOSH Alert pertaining to Organic Dust Toxic Syndrome... (Click to show more)On March 27, 1995, the National Institute for Occupational Safety and Health (NIOSH) received a management request for a health hazard evaluation from the City of Springfield, Missouri, to assess any possible employee health effects from operation of the city's composting facility. There were no indications that employees have or had any health problems associated with the compost operation. This request was prompted by the publication of the NIOSH Alert pertaining to Organic Dust Toxic Syndrome (ODTS). The City of Springfield has two separate composting operations. The first operation was located on a large asphalt pad (adjacent to the sewage treatment plant) and consisted of windrows of mixed sewage sludge and saw dust/wood chips which produced a "Class A" compost. The second site, also adjacent to the sewage treatment plant, was a more conventional composting operation where city residents disposed of their yard waste, the yard waste piled and turned as necessary to produce compost. The finished compost is available to city residents for their home use. Loading of the finished composted product is done by the residents in their own vehicles. During the three surveys conducted at these composting sites, work area air samples were collected for total dusts, ammonia , bioaerosols and endotoxins. Also, real-time monitoring of respirable dust was accomplished inside and outside of equipment used to turn the compost piles. Finally, bulk samples were collected of various compost products and analyzed for microorganisms. Overall, total dust concentrations ranged from Non-detectable (ND) to 22.5 milligrams per cubic meter of air (mg/m3), with the highest samples being located downwind from the sites. Bacteria concentrations ranged from ND to 6.02 x104 colony forming units per cubic meter of air (CFU/m3), with the highest concentrations measured during compost turning operations. The most predominant bacteria found on the samples was Bacillus. Fungi air samples ranged from ND to 2.7 x 105 CFU/m3, with the highest concentrations measured downwind of the green waste compost site. The predominant fungi identified on the samples was Aspergillus. Endotoxin results ranged from ND to 381 endotoxin units per cubic meter of air (EU/m3), with the highest levels measured during compost turning. Ammonia concentrations were measured as high as 20 ppm during compost turning operations. Samples collected indicate that the enclosed equipment cabs, when used properly by keeping the windows closed, can reduce worker exposures. However, these controls are relatively ineffective if the cab window are opened during composting handling operations. City residents were observed shoveling compost into their own vehicles, digging through the compost piles in search of finer material, shoveling hot or cooking compost with their bodies positioned into the steam rising from the piles, and loading their vehicles while in close proximity to end-loaders turning piles. Residents may be at a greater risk of developing ODTS than the city's workers since they are most likely uninformed of the health effects of breathing organic dust, use no respiratory protection, or because of a pre-existing medical condition that may make them more susceptible. Since ODTS is not a widely recognized illness, the syndrome might be misdiagnosed by community physicians. The results from this health hazard evaluation have shown that enclosed machinery cabs on the equipment can reduce exposure when used properly by keeping the windows closed. Also, these results show that individuals in the general area of the composting pads or those not operating enclosed equipment, should stay upwind during turning operations. However, controlling exposures to city residents at the green waste composting site may pose a more difficult problem. Residents may be at a greater risk in developing ODTS since they are most likely uninformed of the health effects of breathing organic dust, use no respiratory protection, or because of a pre-existing medical condition that may make them more susceptible. Since ODTS is not a widely recognized illness, the syndrome might be improperly diagnosed by community physicians. Recommendations are provided.
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(1999) Delphi Chassis Systems, Dayton, Ohio. (Click to open report) On June 6, 1997, the National Institute for Occupational Safety and Health(NIOSH) received a request for a health hazard evaluation (HHE) from employee and management representatives of Delphi Chassis Systems in Dayton, Ohio. The request stated that employees in departments 2, 12, 37, and 40 of this automotive brake parts manufacturing facility were experiencing a high frequency of upper respiratory irritation and colds. A prior HHE request (HETA 96-0199) involving the same concerns had been rec... (Click to show more)On June 6, 1997, the National Institute for Occupational Safety and Health(NIOSH) received a request for a health hazard evaluation (HHE) from employee and management representatives of Delphi Chassis Systems in Dayton, Ohio. The request stated that employees in departments 2, 12, 37, and 40 of this automotive brake parts manufacturing facility were experiencing a high frequency of upper respiratory irritation and colds. A prior HHE request (HETA 96-0199) involving the same concerns had been received on June 10, 1996. In response to that first request, an initial walk-through survey was conducted on August 30, 1996, at which time several brake pads were collected for analysis. That HHE was postponed by management and union representatives due to ongoing contract negotiations.
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(1999) Eagle-Picher Industries, Joplin, Missouri. (Click to open report) On October 20, 1995, the National Institute for Occupational Safety and Health (NIOSH) received a request for a health hazard evaluation (HHE) at Eagle-Picher Industries, Inc., in Joplin, Missouri. The request was submitted by a representative of the United Steelworkers of America Rubber/Plastic Industry Conference, in Akron, Ohio. The request concerned potential employee exposures to a number of chemical hazards, particularly lithium, mercury, and lead chromate, in various operations at the fac... (Click to show more)On October 20, 1995, the National Institute for Occupational Safety and Health (NIOSH) received a request for a health hazard evaluation (HHE) at Eagle-Picher Industries, Inc., in Joplin, Missouri. The request was submitted by a representative of the United Steelworkers of America Rubber/Plastic Industry Conference, in Akron, Ohio. The request concerned potential employee exposures to a number of chemical hazards, particularly lithium, mercury, and lead chromate, in various operations at the facility. Following a walkthrough survey at the plant on December 12-13, 1995, the NIOSH investigators focused on lithium exposures in the process room, pill room, and dry room 108; mercury exposures in the pit and pasting room; identifying an orange substance on the walls in the potting area; and investigating the cause of eye irritation in the solder room. NIOSH investigators returned to the plant on April 17, 1996, and conducted another walkthrough survey to plan for two full days of industrial hygiene and biological monitoring of employee exposures to lithium and mercury, which took place on April 18-19, 1996. For lithium, NIOSH investigators conducted an exposure assessment for all day-shift employees working in the process room, the pill room, and dry room 108. The exposure assessment was comprised of biological monitoring, full-shift personal breathing zone air monitoring, and hand-wipe sampling. In addition, a self-administered questionnaire was used to assess other factors that could affect serum lithium concentrations. Collection of serum specimens from 41 participants giving informed consent was conducted near the end of the day shift at the end of a work week, when serum lithium concentrations are expected to be at or near steady state. The geometric mean serum lithium concentration was 1.75 micrograms per liter (ug/l), with a range of "not detected" to 11.2 ug/l. These serum lithium concentrations were well below therapeutic and toxic concentrations established for patients taking lithium medication. Serum lithium concentrations, however, differed by work area, showing that occupational exposure was occurring. Workers in the process room (5.59 ug/l) and pill room (4.14 ug/l) had higher mean concentrations than workers in the dry room (1.09 ug/l). Over a 2-day period, NIOSH industrial hygienists collected full-shift personal breathing zone (PBZ) samples for lithium among 39 employees in the process room, the pill room, and dry room 108. The overall geometric mean concentration of lithium in air was 1.79 micrograms per cubic meter (ug/m3), with a range of "not detected" to 121.8 ug/m3. As with the serum concentrations, the air sampling indicated higher mean exposures for process room (25.9 ug/m3) and pill room workers (15.3 ug/m3) compared with dry-room workers (0.45 ug/m3). On the second day of sampling, hand -wipe samples for lithium were collected from 10 employees in the pill room and 14 employees in dry room 108. Samples were collected as employees left their work to go to lunch. The geometric mean of lithium on the wipe samples was 61.7 g, with a range of 9 to 649 g. The mean result among pill room workers (174.9 g) was higher than those among dry -room workers (29.3 g). Additional environmental samples were collected to address other issues raised in the request. Analysis of a bulk sample of dust collected from a diffuser in the potting area showed that the majority of the sample was composed of a variety of phthalate esters. Bis-phenol A and some of its derivatives, which are consistent with the presence of epoxy resins, were also major components. The presence of the constituents of the potting compounds on the diffuser may indicate that these substances are being recirculated in the workroom air. A wipe sample was collected from the exterior of a duct near the diffuser. The sample was analyzed for metals. Results showed the presence of aluminum, barium, cadmium, cobalt, chromium, copper, iron, lithium, magnesium, manganese, mercury, molybdenum, nickel, lead, phosphorous, silver, titanium, vanadium, yttrium, zinc, zirconium. Two short-term PBZ air samples were collected to assess employee exposure to rosin solder flux decomposition products, specifically aldehydes and formaldehyde. The results indicated that none of these products were present in amounts greater than the limits of detection for the method. Mercury (Hg) exposure monitoring and urine Hg concentrations were determined among workers in the Hg treatment and negative pasting areas. The overall average Hg full-shift time weighted average (TWA) exposure concentration was 18.3 ug/m3, and the TWA exposure concentrations ranged from 3.5 to 48.3 ug/m3. Only 2 of 17 full-shift TWA Hg exposure measurements exceeded the American Conference of Governmental and Industrial Hygienists (ACGIH) TLV for Hg of 25 ug/m3, and both of these were from processors in the negative pasting area. In general, Hg exposures in the negative pasting area were slightly higher than those in the Hg treatment area. No Hg over-exposures were found during short-term, task-based air sampling. Only 1 of 17 workers had a urine Hg concentration above the ACGIH Biological Exposure Index, and the reasoning behind this high level could not be determined in this survey.
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(1999) Gwinnett Medical Center, Lawrenceville, Georgia. (Click to open report) On February 1, 1999, the National Institute for Occupational Safety and Health (NIOSH) received a management request for a health hazard evaluation (HHE) at the Gwinnett Medical Center (GMC) in Lawrenceville, Georgia. The request asked NIOSH to determine if workplace exposures are related to health problems reportedly experienced by some GMC employees working in the In Patient Surgery (IPS) and Day Surgery (DS) departments at this hospital. Health problems described in the request included derma... (Click to show more)On February 1, 1999, the National Institute for Occupational Safety and Health (NIOSH) received a management request for a health hazard evaluation (HHE) at the Gwinnett Medical Center (GMC) in Lawrenceville, Georgia. The request asked NIOSH to determine if workplace exposures are related to health problems reportedly experienced by some GMC employees working in the In Patient Surgery (IPS) and Day Surgery (DS) departments at this hospital. Health problems described in the request included dermatitis, burning and itching eyes, respiratory irritation, headache, and cough. Potential exposures included construction dust and debris, volatile contaminants from new carpet and paint, disinfectants, common cleaning chemicals, and waste anesthetic gases. On March 1, 1999, NIOSH investigators conducted an initial site visit at GMC. The purpose of this site visit was to review the current status of the health complaints with GMC personnel, inspect the IPS and DS departments and observe work practices, and assess the ventilation system supporting these two areas. A follow-up site visit was conducted on April 20-21, 1999. During this follow up site visit, eight area air samples for natural rubber latex (NRL) allergen were collected in the IPS and DS departments. Bulk and surface samples for NRL allergen analysis were obtained from ceiling plenums (ventilation return air pathways) in both departments. Because of concerns regarding latex allergy, GMC had previously implemented a powder-free latex glove policy and cleaned both the DS and IPS departments. In response to cases of clinically confirmed latex allergy in the DS department, the ventilation duct work was also cleaned. No workers in the IPS department were found to be latex-allergic and the ventilation duct work in this area was not cleaned. NRL monitoring was conducted to compare the two areas. At the time of the NIOSH site visits, the health concerns in the DS department were associated with poor indoor environmental quality (IEQ), and monitoring for standard IEQ parameters (temperature, relative humidity [%RH], and carbon dioxide [CO2]) was conducted in this area. No NRL allergen was detected on any of the air samples collected from the IPS or DS departments. However, NRL allergen was not detected on two quality control sample filters spiked with known concentrations of NRL. Therefore, a meaningful comparison of airborne NRL allergen between the DS and IPS cannot be made from these results. Regulatory standards for acceptable levels of NRL allergen in air have not been established. The bulk and surface dust samples indicated the presence, at various concentrations, of NRL allergen in the return air (RA) plenums from the IPS and DS departments. NRL allergen in bulk samples from the RA plenum in IPS ranged from 21,070 nanograms per gram sample (ng/gm) to 52,800 ng/gm. The two samples from the RA plenum in DS contained 21,067 ng/gm and 39,301 ng/gm of NRL allergen. Regulatory criteria for NRL allergen in surface or dust samples has not been established, although guidelines have been suggested (Mayo Clinic) for bulk dustsamples. The suggested recommendations for bulk dust are: Low, < 10,000 ng/gm; Low-Moderate, 10,000-100,000 ng/gm; High, >100,000 ng/gm. Although only limited samples were collected, there did not appear to be any appreciable difference in NRL concentrations in dust between the DS and IPS departments. The temperature, RH, and CO2 monitoring found all measured parameters to be within acceptable ranges. Inspection of the air handling units (AHUs) providing ventilation to the IPS and DS departments found the units to be clean and well maintained. The units are equipped with efficient filtration that should effectively prevent most dust particles from entering the supply side of the air handlers. As such, dispersion of latex containing particles from supply ducts into occupied areas is unlikely. However, because a reservoir of NRL was identified in the plenum spaces, episodic dispersion of latex-containing particles is a possibility, and actions should be implemented (e.g., proper work practices, particularly during maintenance activities) to control the potential release of NRL-containing dust into occupied areas. Humidification of supply air to the operating rooms is accomplished by direct injection of boiler steam, and there is the potential for introducing boiler water treatment chemicals into the system, and subsequently into the work environment.
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(1999) Handi-Shop, Inc., Mexico, Missouri. (Click to open report) The National Institute for Occupational Safety and Health (NIOSH) received a confidential request for a health hazard evaluation (HHE) at Handi-Shop, Inc. in Mexico, Missouri. the HHE requester was concerned that health risks may have been associated with dust exposures of workers who packaged 'NVX, STPP, and forta fiber' and noted 'there may be other work areas that should be checked also.' Workers' health problems, reportedly included allergies, rashes, sinus problems, and sneezing. The reques... (Click to show more)The National Institute for Occupational Safety and Health (NIOSH) received a confidential request for a health hazard evaluation (HHE) at Handi-Shop, Inc. in Mexico, Missouri. the HHE requester was concerned that health risks may have been associated with dust exposures of workers who packaged 'NVX, STPP, and forta fiber' and noted 'there may be other work areas that should be checked also.' Workers' health problems, reportedly included allergies, rashes, sinus problems, and sneezing. The requester also reported that 'several workers throughout the years have had doctors' orders to stop working in the dust.
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(1999) LDS Hospital/Intermountain Health Care, Salt Lake City, Utah. (Click to open report) On November 18, 1998, the National Institute for Occupational Safety and Health (NIOSH) received a request for a health hazard evaluation (HHE) from the Occupational Health Nurse at the Latter Day Saints/Intermountain Health Care hospital in Salt Lake City, Utah. The HHE request stated that several nurses and nurses' aides working in the bone marrow transplant unit (BMT) had experienced allergic symptoms. These included two reports of anaphylaxis and several reports of less severe symptoms, such... (Click to show more)On November 18, 1998, the National Institute for Occupational Safety and Health (NIOSH) received a request for a health hazard evaluation (HHE) from the Occupational Health Nurse at the Latter Day Saints/Intermountain Health Care hospital in Salt Lake City, Utah. The HHE request stated that several nurses and nurses' aides working in the bone marrow transplant unit (BMT) had experienced allergic symptoms. These included two reports of anaphylaxis and several reports of less severe symptoms, such as shortness of breath, rashes, and itching. The health effects reported by the health care workers were thought to be associated with an activity specific to the BMT: the infusing of patients with a solution containing stem cells and dimethyl sulfoxide (DMSO). The NIOSH investigation consisted of concurrent medical and industrial hygiene evaluations on December 7, 1998, and an additional medical evaluation on February 18-19, 1999. The medical evaluation included a questionnaire, private interviews with employees, and review of medical records. The industrial hygiene evaluation consisted of air, surface, and bulk dust sampling to evaluate the presence of DMSO and latex proteins in the BMT. None of the volatile chemicals known to be present in the stem cell infusion solutions, including DMSO, were detected in the air during the administration of stem cells into a patient. Natural rubber latex was not detected in air samples. A medical records review revealed rashes and respiratory symptoms to be the most commonly reported symptoms among affected employees. Since no direct dermal contact with DMSO occurs, and no chemicals could be measured in the breathing zone of the staff nurse or in the ambient environment of the room where the infusion occurred, it is unlikely that skin and respiratory symptoms are caused by exposures from the administration of stem cells. Medical questionnaires (from 64 workers) revealed that 22% of employees reported some type of chest symptom and 50% reported skin symptoms including rashes (47%) and hives (13%). Hay fever was reported by 59% of the employees and 22% reported a physician diagnosis of asthma. Pre-existing atopy and asthma in the employees who worked in the BMT could explain the upper respiratory symptoms reported by staff in the BMT. Skin symptoms (especially hand rash) are common in the nursing profession due to frequent washing and drying of the hands and the use of gloves as a part of universal precautions.
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(1999) Puerto Rico Aqueduct and Sewer Authority Sergio Cuevas Bustamante Filtration Plant, Frujillo Alto, Puerto Rico. (Click to open report) On May 6, 1998, the National Institute for Occupational Safety and Health (NIOSH) received a confidential employee request for a Health Hazard Evaluation (HHE) at the Sergio Cuevas Bustamante Filtration Plant of the Puerto Rico Aqueduct and Sewer Authority. The requesters expressed concern regarding respiratory problems and dermatitis possibly associated with exposures to hydrated lime [calcium hydroxide, Ca(OH)2], chlorine gas [Cl2], and two coagulants [GC 850 (basic aluminum chloride solution)... (Click to show more)On May 6, 1998, the National Institute for Occupational Safety and Health (NIOSH) received a confidential employee request for a Health Hazard Evaluation (HHE) at the Sergio Cuevas Bustamante Filtration Plant of the Puerto Rico Aqueduct and Sewer Authority. The requesters expressed concern regarding respiratory problems and dermatitis possibly associated with exposures to hydrated lime [calcium hydroxide, Ca(OH)2], chlorine gas [Cl2], and two coagulants [GC 850 (basic aluminum chloride solution) and PRP 4440 (polydimethydiallylammonium chloride)]. A site visit was conducted at this potable water filtration plant on June 29-30, 1998. Of the 25 people employed at the filtration plant, 19 (76%) worked the morning shift (6 a.m. to 2 p.m.), when most of the activities at the filtration plant were performed. On the day of the site visit, 17 employees were present and all were interviewed. Two of the interviewed workers reported that they were diagnosed by physicians as having asthma, which had developed since working at this plant. Both workers reported noticeable improvements of this health condition during vacations, sick leave, or lay-offs. Five of the workers (including the two asthmatics) reported at least two respiratory symptoms in the ten days preceding the interview. These symptoms included difficulty breathing, phlegm production, chest tightness, wheezing, and shortness of breath. All symptomatic workers reported that they believed their symptoms were related to long-term exposure to hydrated lime and chlorine gas. Other reported health problems included sinusitis, itchy eyes, skin rash, and dermatitis. Area air sampling for hydrated lime, chlorine, and particulates was conducted at locations and times of anticipated elevated exposures. Personal breathing zone (PBZ) air sampling for hydrated lime also was performed; however, the method used to analyze the hydrated lime failed. A count of particles in air during hydrated lime loading operations, a procedure reported by workers to often result in elevated dust levels, revealed only moderate losses of hydrated lime during loading when compared to the period after loading. No detectable levels of chlorine were measured in the area where chlorine cylinders were stored or in the room where chlorine was added to the water supply. The two coagulants of concern were confined to an area where little human exposure should occur, so monitoring was not conducted. Management and employees reported that there had been problems associated with the handling of hydrated lime in the past. A crack, still visible but repaired by the time of the NIOSH site visit, had developed in the side of a silo which contained about 130,000 pounds of hydrated lime, allowing hydrated lime to be released into the workplace. The conveyor feeding hydrated lime into the water supply was designed to have barriers around it but they had been removed and hydrated lime was observed on surfaces throughout the room. Workers reported that hydrated lime periodically escaped into the environment from the top of the silo during loading, despite a filtration system to prevent its escape. The connection between the supply truck and the pipes carrying the hydrated lime to the top of the silo was difficult to seal properly and reportedly hydrated lime was spilled. On the day preceding the NIOSH site visit, a worker received a dose of hydrated lime in the face during a maintenance task at the silo. Several other safety concerns were identified at the plant, including absence of appropriate guarding of roof openings and lack of a complete confined space entry program, which indicate that more rigorous administrative controls should be implemented. Este informe también está disponible en español: <a href="https://www.cdc.gov/niosh/hhe/reports/pdfs/1998-0217-2772.pdf"target="_blank">https://www.cdc.gov/niosh/hhe/reports/pdfs/1998-0217-2772.pdf</a>.
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