scholarly journals Occupational Exposure to Flour Dust. Exposure Assessment and Effectiveness of Control Measures

Author(s):  
Andrea Martinelli ◽  
Fabiola Salamon ◽  
Maria Luisa Scapellato ◽  
Andrea Trevisan ◽  
Liviano Vianello ◽  
...  

The adverse effects associated with exposure to flour dust have been known since the 1700s. The aim of the study was to assess the occupational exposure to flour dust in Italian facilities, identify the activities characterized by the highest exposure, and provide information to reduce workers’ exposure. The study was performed in different facilities such as flourmills (n = 2), confectioneries (n = 2), bakeries (n = 24), and pizzerias (n = 2). Inhalable flour dust was assessed by personal and area samplings (n = 250) using IOM (Institute of Occupational Medicine) samplers. The results showed personal occupational exposure to flour dust over the American Conference of Governmental Industrial Hygiene (ACGIH) and the Scientific Committee on Occupational Exposure Limit (SCOEL) occupational limits (mean 1.987 mg/m3; range 0.093–14.055 mg/m3). The levels were significantly higher for dough makers in comparison to the dough formers and packaging area subjects. In four bakeries the industrial hygiene surveys were re-performed after some control measures, such as installation of a sleeve to the end of pipeline, a lid on the mixer tub or local exhaust ventilation system, were installed. The exposure levels were significantly lower than those measured before the introduction of control measures. The exposure level reduction was observed not only in the dough making area but also in all bakeries locals.

1999 ◽  
Author(s):  
I. Burstyn ◽  
K. Teschke ◽  
K. Bartlett ◽  
S. Kennedy

2021 ◽  
Vol 11 (1) ◽  
Author(s):  
Maria Helena Guerra Andersen ◽  
Anne Thoustrup Saber ◽  
Marie Frederiksen ◽  
Per Axel Clausen ◽  
Camilla Sandal Sejbaek ◽  
...  

AbstractAir force ground crew personnel are potentially exposed to fuels and lubricants, as raw materials, vapours and combustion exhaust emissions, during operation and maintenance of aircrafts. This study investigated exposure levels and biomarkers of effects for employees at a Danish air force military base. We enrolled self-reported healthy and non-smoking employees (n = 79) and grouped them by exposure based on job function, considered to be potentially exposed (aircraft engineers, crew chiefs, fuel operators and munition specialists) or as reference group with minimal occupational exposure (avionics and office workers). We measured exposure levels to polycyclic aromatic hydrocarbons (PAHs) and organophosphate esters (OPEs) by silicone bands and skin wipes (PAHs only) as well as urinary excretion of PAH metabolites (OH-PAHs). Additionally, we assessed exposure levels of ultrafine particles (UFPs) in the breathing zone for specific job functions. As biomarkers of effect, we assessed lung function, plasma levels of acute phase inflammatory markers, and genetic damage levels in peripheral blood cells. Exposure levels of total PAHs, OPEs and OH-PAHs did not differ between exposure groups or job functions, with low correlations between PAHs in different matrices. Among the measured job functions, the UFP levels were higher for the crew chiefs. The exposure level of the PAH fluorene was significantly higher for the exposed group than the reference group (15.9 ± 23.7 ng/g per 24 h vs 5.28 ± 7.87 ng/g per 24 h, p = 0.007), as was the OPE triphenyl phosphate (305 ± 606 vs 19.7 ± 33.8 ng/g per 24 h, p = 0.011). The OPE tris(1,3-dichlor-2-propyl)phosphate had a higher mean in the exposed group (60.7 ± 135 ng/g per 24 h) compared to the reference group (8.89 ± 15.7 ng/g per 24 h) but did not reach significance. No evidence of effects for biomarkers of systemic inflammation, genetic damage or lung function was found. Overall, our biomonitoring study show limited evidence of occupational exposure of air force ground crew personnel to UFPs, PAHs and OPEs. Furthermore, the OH-PAHs and the assessed biomarkers of early biological effects did not differ between exposed and reference groups.


2019 ◽  
Vol 69 (7) ◽  
pp. 475-481 ◽  
Author(s):  
C Wen ◽  
X Wen ◽  
R Li ◽  
S Su ◽  
H Xu

Abstract Background Silicosis is caused by long-term exposure to silica dust. Crystal rhinestone workers can be exposed to high levels of silica dust and are at risk of silicosis. Aims To explore silicosis cases, silica dust exposure and control measures in a rhinestone factory in South China. Methods We extracted and analysed data on new silicosis cases reported to China’s occupational disease and occupational health information monitoring system between 2006 and 2012 from a rhinestone factory in South China. We measured the quartz content of bulk dust, static total and respirable dust samples. Results Ninety-eight silicosis cases were reported between 2006 and 2012. The mean duration of silica dust exposure was 9.2 years (range 3–16). Drilling and polishing workers accounted for 96 (98%) of cases. We collected 1479 static samples including 690 total dust and 789 respirable dust samples. Mean dust levels for drilling were 1.01 mg/m3 (range 0.20–3.80) for total dust and 0.51 mg/m3 (range 0.04–1.70) for respirable dust. Mean dust levels for polishing were 0.59 mg/m3 (range 0.20–2.10) for total dust and 0.28 mg/m3 (range 0.08–0.71) for respirable dust. Over a third [289/789 (37%)] of total dust samples and 129/690 (19%) respirable dust samples exceeded the national permissible exposure limit. Conclusion Exposure to silica dust, ineffective dust control measures and inefficient health surveillance may have contributed to the incidence of silicosis in the factory we studied. Identification of silica dust exposure and effective dust control measures would reduce the risk of silicosis in rhinestone workers.


2017 ◽  
Vol 33 (3(93)) ◽  
pp. 91-120
Author(s):  
Agata Stobnicka ◽  
Rafał Górny

The term "flour dust" refers to particles derived from finely ground cereal grains and "non-cereal" grains. Flour flour usually also contains ingredients that play an important role in improving dough quality, such as enzymes, additives such as baker's yeast, flavors, spices and chemical ingredients such as preservatives. Flour is one of the basic raw materials used in the food industry and in the production of animal feed. Taking into account the nature of the production activities in mentioned industries, the highest occupational exposure to flour dust is usually observed in bakeries and grain mills. Significant exposure to flour dust is also found in factories of pasta, pizzeria and pastry, restaurant kitchens, malt factories, animal feed factories and agriculture. The main route of exposure to flour dust in occupational conditions is respiratory and skin. The main effect of repeated or long-lasting human exposure to flour dust is irritation and allergy. Epidemiological reports have shown that asthma, conjunctivitis, rhinitis and skin reactions are the main adverse health effects of flour dust exposure. Currently in Poland for flour dust the maximum admissible value (MAC, NDS) is the same as for organic dust (plant and animal origin). The MAC values are: for inhalable fraction 2 mg/m3 and for respirable fraction 1 mg/m3 when dust contains 10% or more crystalline silica and when dust contains less than 10% of crystalline silica, 4 mg/m3 for inhalable fraction and 2 mg/m3 for respirable fraction. The need to prepare documentation for flour dust resulted from the fact that existing documentation and MAC values mainly concern the effects of farmers' exposure to organic dust of plant and animal origin. It did not refer to flour dust for which the sensitization effect is critical. The basic mechanism of action of the flour dust on the body is the reaction of hypersensitivity with stimulation antibodies type E (IgE) developing shortly after exposure to the antigen. The value of hygienic norms for flour dust in Poland has not been established, yet. There is no data regarding animal experiments and in vitro studies with flour dust. On the basis of epidemiological studies, the risk of nasal symptoms has been found to increase with dust concentrations of 1 mg/m3 and the risk of asthma at concentrations above 3 mg/m3. The SCOEL assumes that exposure to the inhalable fraction of flour at a concentration of ≤ 1 mg/m3 protects most exposed workers from nasal mucositis and that the predicted symptoms, if present, are mild. However, the concentration of flour dust <1 mg/m3 may cause symptoms in already sensitized workers. The results of the study show that the full protection against allergens present in the flour dust in the air at low concentrations is difficult to achieve. At the same time, ACGIH's recommended TLV value for the inhalable flour dust fraction at 0.5 mg/m3 (8-h TWA). The "dose-response" results suggest that the symptoms of exposure to flour, especially from the lower respiratory tract, asthma, as well as the risk of sensitization, are rare in the inhalable fraction concentration in the range 0.5  1 mg/m3. Considering the above, the Interdepartmental Commission for MAC and MAI at the 84th meeting of 4.11.2016 adopted the TLV value for the inhalable fraction of flour dust at the level of 2 mg/m3, that is, at the level of the current MAC value for inhalable fraction of dust containing > 10% of the crystalline silica. No grounds for determining the short-term limit MAC(STEL) and the limit value in biological material. The standard is marked with "A" (sensitizing substance).


2017 ◽  
Vol 33 (1(91)) ◽  
pp. 97-113
Author(s):  
Andrzej Sapota ◽  
Małgorzata Skrzypińska-Gawrysiak ◽  
ANNA KILANOWICZ

Nitroethane is a colorless oily liquid with a mild fruity odor. It is used mainly as a pro-pellant (e.g., fuel for rockets), and as a solvent or dissolvent agent for cellulose esters, resins (vinyl and alkyd) and waxes, and also in chemical synthesis.Occupational exposure to nitroethane may occur during the process of its production and processing. There are no data on air concentra-tions of nitroethane in occupational exposure. In 2010–2015, workers in Poland were not exposed to nitroethane concentrations exceed-ing the maximum allowable value – 75 mg/m3 (the limit value valid since 2010).Nitroethane can be absorbed into the body via inhalation of its vapors or by ingestion.The discussed cases of nitroethane acute poi-soning caused by an accidental ingestion of artificial fingernail remover containing pure nitroethane concerned children under three years. Few hours after ingestion, cyanosis and sporadic vomiting were observed in children. The methemoglobin level reached 40÷50%.Neither data on chronic nitroethane poisoning in humans nor data obtained from epidemio-logical studies are available.On the basis of the results of acute toxicity studies nitroethane has been categorized in the group of hazardous compounds. However, eye and dermal irritation or allergic effects have not been evidenced. The studies of sub-chronic (4 and 90 days) and chronic (2 years) exposure to nitroethane per-formed on rats and mice (concentration range 310 ÷ 12 400 mg/m3) revealed the methemo-globinogenic effect of this compound and a minor damage to liver, spleen, salivary gland and nasal turbinates.Niroethane has shown neither mutagenic nor carcinogenic effects. Its influence on fertility has not been evidenced either. After chronic exposure (2 years) of rats to ni-troethane at concentration of 525 mg/m3 (the lowest observed adverse effect level – LOAEL), a slight change in a body mass of exposed fe-male animals and subtle changes in biochemi-cal parameters were observed, but there were no anomalies in hematological and histopatho-logical examinations.The value of 62 mg/m3 has been suggested to be adopted as the MAC value for nitroethane after applying the LOAEL value of 525 mg/m3 and relevant coefficients of uncertainty. The STEL value for nitroethane was proposed ac-cording to the methodology for determining short term exposure level value for irritating substances as three times MAC value (186 mg/m3) to prevent the effects of sensory irri-tations in humans. Because of its methemoglo-binogenic effect, 2% Met-Hb has been suggest-ed to be adopted as the value of biological ex-posure index (BEI), like the value already adopted for all methemoglobinogenic sub-stances.The Scientific Committee on Occupational Exposure Limits (SCOEL) proposed the time-weighted average (TWA) for nitroethane (8 h) as 62 mg/m3 (20 ppm), short-term exposure limit (STEL, 15 min) as 312 mg/m3 (100 ppm) and “skin” notation.Proposed OEL and STEL values for nitroethane were subjected to public consultation, con-ducted in 2011 by contact points, during which Poland did not raise any objections to the pro-posals. The proposed values for nitroethane by SCOEL has been adopted by the Advisory Committee on Safety and Health at Work UE (ACSH) and included in the draft directive establishing the IV list of indicative occupa-tional exposure limit values.


2018 ◽  
Vol 6 (6) ◽  
Author(s):  
Antoine Francis Obame Nguema ◽  
Akihiro Tokai ◽  
Ibnu Susanto Joyosemito ◽  
Naoya Kojima

The processing of petroleum products in gasoline storage and distribution facility for loading operation, has caused the generation of vapor emissions sources. Benzene is one of those vapor emissions that workers are likely to be exposed at high exposure level during conducting out specific tasks such as loading gasoline to various petroleum storage transport modes. This results in many problems on human health such as cancer and non-cancer diseases. However, the estimate of benzene exposure to indicate the control measures has not been fully explored in previous researches. In this study, the occupational exposure estimate of benzene in Gabon’s gasoline storage and distribution facility was investigated by using a quantitative and predictive exposure inhalation model; to estimate benzene concentration before and after applying control measures. The results indicate that the benzene concentrations varied between 9.46 mg/m³ and 187 mg/m³ for short term and has the value of 187 mg/m³ for long term. The implementation of control measures including using vapor recovery system, chemical filter mask and improving worker’s behavior might contribute to significantly reduce benzene concentration to the range of 4.52 – 29.08 mg/m³ for short term and down to 4.55 mg/m³ for long term. This almost meets the Agency Governmental Industrial Hygienists standard, in which occupational exposure limit for short term and long term exposure is 8.1 mg/m³ and 3.16 mg/m³, respectively.


2020 ◽  
Vol 10 (6) ◽  
pp. 759-767
Author(s):  
Milap Sharma ◽  
Krishan K. Kataria ◽  
Narendra M. Suri ◽  
Suman Kant

Foundry workers are exposed to numerous health hazards, which includes respirable dust exposure as a prominent health issue. Apart from metallic dust, respirable crystalline silica (RCS) is generated during the fettling operation, which is very hazardous and a leading cause for silicosis. Evaluation and control of such hazards deserve particular attention in order to reduce the dust exposure level upto the permissible limits. In present study, an attempt was made to propose a low-cost design control intervention utilizing sensor based intelligence (ATmega328P microcontroller and an optical dust-sensor, SHARP GP2Y1010AU0F) for monitoring the dust exposure, followed by virtual ergonomics approach in CATIAV5R20. The proposed device was tested under several operating conditions. The results indicated that the prototype was sensitive to dust, having higher average dust density values under the dust haze weather condition (arithmetic mean (AM): 0.2590 mg/m3, geometric mean (GM): 0.2350 mg/m3) and fettling work-section (AM: 0.2550 mg/m3, GM: 0.2164 mg/m3) respectively, as compared to other conditions. Also, biomechanics analysis yielded the spine compression values lesser than the recommended limits, validating that the proposed fettling booth models could be considered as suggestive engineering control measures in conjunction with the designed prototype, so as to minimize the respirable dust exposure levels.


2021 ◽  
Vol 9 ◽  
Author(s):  
Krassi Rumchev ◽  
Yun Zhao ◽  
Andy Lee

Occupational dust exposure can occur in various settings, including bakeries. A case study was conducted in an industrial bakery in Perth, Western Australia, to assess exposure to particulate dust concentration. The factory was separated into three production zones and an office area which represented as a control zone. Results indicated that bakery workers in the production zones were exposed to higher ambient dust particle concentrations compared to those from the office environment. Coarse particles (&gt;10 μm in aerodynamic diameter) were the predominant particle size fraction measured in all studied areas with the highest median exposure level recorded in the dough room (0.181 mg/m3, interquartile range 0.283). High personal concentration of respirable particles was also measured in the dough room (median 2.26 mg/m3) which exceeded the recommended limit of 1.5 mg/m3 and was more than 50 times higher than the concentration recorded in the office (0.04 mg/m3). The variation in dust concentrations between production zones underlines the need of more knowledge about how aerosol fractions are distributed across the production process. The findings also suggest that bakery workers are exposed to high dust levels that may increase their risk of developing respiratory diseases and the decrease of present exposure levels is imperative.


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