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Occupational Health and Hygiene Study of Sawmill Workers in Sathyamangalam
1.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 01 | Jan 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1445 Occupational Health and Hygiene Study of Sawmill Workers in Sathyamangalam M Mohamed Irsath 1, T Jishin Jayan2 1(P.G) Student, Dept of Industrial Safety Engineering, Bannari Amman Institute of Technology, Sathyamangalam, Tamil Nadu, India 2Asst. Professor, Dept. of Industrial Safety Engineering, Bannari Amman Institute of Technology, Sathyamangalam, Tamil Nadu, India ---------------------------------------------------------------------***---------------------------------------------------------------------- Abstract - An occupational health and hygiene study was carried out in saw mill workers around sathyamangalam. Postal questionnairesandobservational walk-throughsurveys were used to gather data. At three work sites, industrial hygiene walk-through inspections were done, with measures for wood dust and noise taken. The study's goal was to gather information on the present state of Occupational health and safety issues, as well as an estimate of wood dust and noise exposures. The exposure to wood dust were lesser and the noise were higher than the exposure limit. Total dust concentrations in the air ranged from 0.001 mg/m3 to 3.87 mg/m3, and noise exposure was between 65 to 110 dB. From this survey we also can able to get they are also affected from various Work-related symptoms like cough, lower back pain, Eye irritation, sneezing, chestpain, Breathlessness, Rashesand Musculoskeletal pain. Key Words: saw mill, Industrial hygiene, Wood, Wood Dust, Noise, Survey, Work-related symptoms, Occupational health and safety. 1.INTRODUCTION Wood processing activities involve various procedures which convert raw wood into usable forms. Sawmills, the wood furniture business, and the door manufacturing sector are all places wheresuchprocessingis done. A sawmill is a facilitywheretimbersaremachine-sawn into various widths of planks or boards. The sawmill industry has various risks, one of which being dust. Wood dust is the fine, powdery debris that results from the processing of wood. The carcinogenic effects of wood dust, particularly hardwood dust, on the nasal cavity, paranasal sinus, and nasopharynx are well documented. Other risks mentioned by sawmill workers include unprotectedmoving components of machinery, noise, and heat, in addition to dust. Jacobson (2008)saysthatHisreviewconcludedthat wood dust exposure is a risk factor for the development of asthma, chronic bronchitis, rhino-conjunctivitis,andchronic impairment of lung function. Eyeirritationandupperairway symptoms have been reported after exposure to spruce and pine dust levels in the range 0.1–6.3 mg/m3[1].Accordingto hangstrom k (2008) exposures to wood dust and monoterpenesarecommonlymeasuredinthewood-refining industries. Personal wood dust exposure levels at wood pellet production plants have been noted to be between <0.60 and 8.0 mg/m3 as inhalable dust and levels of monoterpene (only α-pinene) were <0.28 to 25 mg/m3. Peaks in exposure can,however, bemeasuredusingpersonal real-time monitors [2]. Paul Adekunle onakoya (2013) he explains the noise produced in saw mills and how they can affect people after prolonged period of exposure. The prevalence of hearing loss and the patternofhearinglossare evaluated among the workers. The prevalence of hearing impairment was said to be 89.7%. Finally, it was found that hearing loss and tinnitus were the auditory effects of prolonged exposure to noise [3]. Ayodele and Olubayo-Fatiregun(2013),saysthatmajorityof sawmill workers with respect to their educational level and background are not well educated or trained in the areas of occupational hazard identification and evaluation. Thus,the rate of occupational hazard exposure from this industry is very high. 1.1 SAW DUST Sawdust,alsoknown as wood dust, is abyproductof cutting, grinding, drilling, sanding, or otherwise pulverizing wood or other materials with a saw or other tool; it is made up of fine wood particles. It can be a hazard in manufacturing industries,and wood dust can cause health problemssuchas asthma. Inhaling dust into the lungs can cause breathing difficulties and lung diseases such as occupational asthma and lung cancer. The most common method of exposure to wood dust is inhaling it. Getting dust in your eyes can irritate and damage them. Skin contact with wood dust can result in skin ulceration, irritation, and dermatitis. 1.2 NOISE Wood Processing machines used in industriesleads to the generation of high noise level. Exposure to high levels of noise, particularly in the workplace, has been a global concern due to strong evidence linking it to a number of serious challenges. Short or long periods of noise exposure can cause auditory effects suchasfatigueandhearingloss,as well as indirect non-auditory effects such as speech
2.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 01 | Jan 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1446 interference, annoyance, decreased mental peace and task performance, and a variety of psychological changes. 1.3 OBJECTIVE The main object of this project is to identify the health and hygiene of the saw mill workers in sathyamangalam and estimate the amount of wooddust and noise a level exposure. 2. MATERIALS AND METHODOLODY Materials used in the study were noise level meter for noise level measurement and Personal Air Sampler for dust level measurement. 2.1 NOISE LEVEL METER Noise Level Measurement was taken for differenttypesof wood processing machinery used in the saw mill. A sound level meter is used because it closely mimics the loudness perceived by the human ear. Fig-1: Sound Level Meter Fig-1 shows the digital data logging sound levelmeter,model SL-4010, manufactured by Lutron Instruments was used in this Project. The equipment complies with ANSI S1.4 and IEC 61672-1 Type 2 requirements, measuring and displaying Sound Pressure Level (SPL) from 35dB(A) to 130dB(A) with 1.0dB(A) accuracy in three measurement ranges. The background noise for each sawmill was measured when the sawmill was active and the machines were in use. Noise level for each machinewas taken and noise levelsurveyalsotaken for all the wood processing machines in the sawmills. 2.2 PERSONAL AIR SAMPLER Wood Dust concentration for each site was taken for consecutive days using a personal level air sampler. Fig-2 is the personal air sampler used for personal air sampling for workers, instrument used was a Polltech make Model PEM- AFH37 Filter Holder AcrylicBody(forGF/AFilterPaperof37 mm diameter) for PM sampling. Filter Paper used for sampling is 47mm dia whatman Filter paper. Fig-2: Personal Air Sampler Before attaching the filter paper to the ceramic cup, the initial weight of the filter paper was measured. After the sampling time once again the filter paper was measured to find the weight of the dust that deposit on the filter paper The sampling time was set to 8 hours and volume of air was set to 2 l/m3. Whatman Filter with diameter of 47mm was attached to the ceramiccup.Once the sampler is switched on the motor inside the sampler started to create suction due to the dust will come and settle near the filter paper. The ceramic cup needs to place near the breathing area. Q (mg/m3) =(Wb-Wa) *1000/(f*t) (1) Where, Q- Dust Concentrarion Wa- Initial weight of filter Paper Wb-Final weight of filter Paper f- Flow rate t- Total time 3 Questioner Survey This questioner survey was carried among sawmill workers around sathyamangalam. The questionnaire considered, hazards (heat, noise, dust, and vibration), health problems (musculoskeletal disorders, low back pain, cough, breathlessness, chest pain, chest tightness, sneezing, rashes, eye irritation, and injuries), awareness and use of PPE, and hygiene practices (hand washing, bathing, and changing of clothes at close of work) among the wood workers. The health problems were classified into two types one is
3.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 01 | Jan 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1447 Respirable and other is non-Respirable health problem among saw mill workers. 3. RESULTS AND DISCUSSION 3.1 Noise level Measurement Noise levels of each machine are given below in table-1. The noise level for four different types of machines used in saw mill was measured. Table-1: Noise level for each machine S.n o Machine Idea condition(dB A) Minimu m level (dBA) Maximu m Level (dBA) 1 Vertical BandSaw 80 88 98 2 Horizont al Band Saw 80 90 99.4 3 Surface Planner 79 85.1 88.4 4 Thicknes s Planner 80.5 86.5 87.1 The Occupational safety and health administration (OSHA) recommend permissible noiseexposureforworkersexposed to a TWA noise level is 85 decibels or higher over an 8-hour work. From the Table-2 it clearly says that noise level was higher than the permissible limit Fig-1: Average noise level chart for Sawmill Machines The average level of noise in the Sawmill machines are represented in the Fig-1. In sawmill theymostlyworkonfour sizes of woods 4 feet, 6 feet and 7 feet. The average noise levels of machines at sawmill ranged from 85dBA to 100dBA for 7 feet wood with thehighestvaluerecordedforhorizontal band saw and the lowest value recorded for the surface planner machine. The average noise levels for vertical band saw are varies from 90dBA to98dBA,averagenoiselevelsfor Horizontal band saw are varies from 91.5dBA to 102.4dBA, average noise levels forSurface planner variesfrom85.2dBA to 88.4dBA, and average noise levels for Thickness planner varies from 87dBA to 90.5dBA. Noise level survey was taken forthe machines in saw mill with the distance of .5m,1m,1.5,2m. The obtained values of the vertical band saw, Horizontal band saw, surface planner and Thickness planner machines are mentioned in the Fig-2, Fig-3, Fig-4 and Fig-5. The noise level at the .5m is higher than the 2m. The noise level forHorizontal bandis102.4dBA which higher in this survey, from that distance only the operator will operate that machine which is highly hazardous, without the right Personal protective equipment that noise will damage the hearing. Fig-2: Noise level survey for Horizontal band saw Fig-3: Noise level survey for vertical band saw
4.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 01 | Jan 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1448 Fig-4: Noise level survey for Surface planner Fig-5: Noise level survey for Thickness planner All the machine in the saw mills is exceed the OSHA Threshold limit, it was hazards to the employee, from the Questioner survey it is clearly shows that some employee having hearing deficiency. The Noise can be reducedinseveralwayslikeengineering and administrative control. Engineering controlsarethebest long-term solution to the occupational noise problem controls like buying quite machinery and equipment, maintaining machinery and equipment frequently, reducing machinery and equipment vibration, Isolating the noise source in an insulated room by operating the equipment remotely, Placingabarrierbetweenthesourceandemployee. If the noise is not reduced, then we have to go for administrative control. Administrative control includes marking hearing protection zones with notices, supervising the use of hearing protectors, usage of correct PPE for the level of noise, monitoring, and conducting regular audiometrytesttocheck whether hearing protectionmeasures are working perfectly. 3.2 Dust level Measurement Filter paper weights are given in the Table-2. Time duration and flow rates are 400minutes and 2 Liter/minutes for all sampling. Table-2: Weight of the filter paper S.no Initial weight (g) Final Weight (g) 1 0.17 0.34 2 0.17 0.30 By substituting the above valuesintheequation(1).TheDust concentration value ranges from 0.01mg/m3 to 0.2125 mg/m3 for 8 hours of work. According to the obtained result and comparing with the TLV. The amount of dust exposure was very less. The dust concentration depends on environmental conditions. Inrainy season mostofwoodsare in wet condition so while cutting most of the dust will settle with that wood itself. But in summer season the woods arein dry condition, while cutting wood dust will not settle on the wood so the dust concentration have to be high when compared to raining season. Dust level concentration in the area was lesser then the Threshold limit. However, in questioner survey some employee says that they are having eye irritation and cough. Cough was mentioned by 71.4% of Worker, this is because of the respirable dust present in that area. They are controlled by applying engineering andadministrativecontrol.Usageof Local Exhaust Ventilation to capture dust, Use of on-tool extraction on saws and grinders to control wood dust at source, Proper maintenance, Usage of lubricant, by wearing RPE and other personal protection equipment, providing washing facilities at work site, and Advise workers to wash their face and hands immediately after finishing. 3.3 Occupational health disease. A total of 35 workers wereparticipatedinthissurvey.The common occupational hazard reported bytheresponsewere separated into two types respirable Table-3: Respirable health Problems. Symptoms Subject n=35 Percentage Cough 25 71.4 Sputum 20 57.1 Sneezing 23 65 Chest Pain 3 8.5 Chest Tightness 5 14
5.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 01 | Jan 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1449 Table-4: Non-Respirable health Problems Symptoms Subject n=35 Percentage Lower Back Pain 20 57.14 Eye Irritation 24 68.57 Joint Pain 20 57.14 Hearing Deficiency 5 14 MechanicalInjury 10 28.5 and non-respirable problem in respirable health are shown on Table-3 and Table-4. The diseases reported by workers are cough 25 (71.4%), Sputum 20(57.1%), Sneezing 23(65%), Chest Pain 3(8.5%), Chest tightness 5(14%). Non- respirable health problem reported was Lower back pain 20(57.14%), Eye irritation 24(68.57%), Joint Pain 20(57.14%),HearingDeficiency5(14.2%),Mechanicalinjury 10(28.5%). A large proportionoftherespondentsreportedwascough 25 (71.4%), Eye irritation 24(68.57%), and Lower back pain 20(57.14%). Mechanical injury is happening due to long periods of standing, repetitive/strengthening jobs, bending, and manual lifting of heavy logs of wood can all cause injuries, as can exposure to unguarded machine parts. Low back pain can also be caused by prolonged standing, repetitive/strengthening jobs, bending, and manualliftingof heavy logs of wood. In addition, over three-quarters of the respondents in this survey worked 8–10 hours every day. This could have contributed to low back pain, as well as exhaustion, a decreased capacity to concentrate, and an increased risk of accidents. 4. CONCLUSION Based on the results, wood dust exposure is found to below than the OSHA’s threshold limit, but it can be in excess in different environmentalcondition.Noiselevelismorethan the OSHA’s threshold limit. Hearing conversation program and other controls need to be taken to reduce the noise level. Occupational health hazardsare more in sawmillingprocess, the use of Personal protective equipment is less and risky behavior among sawmill workers are statistically related to occupational hazards. Workers in sawmillsshouldbetrained on the need of using personal protection equipment in the workplace. To ensure a healthier workforce, occupational health services should be made available to this group of workers. REFERENCES [1] Jacobsen G, Schlunssen V, Schaumburg I, Taudorf E, Sigsgaard T. Longitudinal lung function decline and wood dust exposure in the furniture industry. Eur Respir J. [2] Halpin DM, Graneek BJ, Lacey J, Nieuwenhuijsen MJ, Williamson PA, Venables KM, et al. Respiratory symptoms, immunological responses, and aeroallergen concentrations at a sawmill. Occup Environ Med. [3] Demers PA, Teschke K, Kennedy SM. What to do about softwood? A review of respiratory effects and recommendations regarding exposure limits. Am J Ind Med. [4] Barcenas CH, Delclos GL, El-Zein R, et al. (2005) Wood dust exposure and the association with lung cancerrisk. Am J Ind Med; [5] Halpin DM, Graneek BJ, Lacey J, Nieuwenhuijsen MJ, Williamson PA, Venables KM, et al. Respiratory symptoms, immunological responses, and aeroallergen concentrations at a sawmill. Occup Environ Med [6] Demers PA, Teschke K, Kennedy SM. What to do about softwood? A review of respiratory effects and recommendations regarding exposure limits. Am J Ind Med. [7] Harper M, Muller BS. An evaluation of total and inhalable samplers for the collection of wood dust in three wood products industries. J Environ Monit. [8] Axelsson A, Barrenas ML (1991). Tinnitus in noise- induced hearing loss. Mosby Year book 1991 Eds. Dancer, Handerson, Salvi & Hammernik. pp. 269-276 [9] Berglund B, Linvall T, Schwela DH (1999). Guildlines qfor Community Noise. World Health Organisation, Geneva. [10] Ghoroje ADA, Marchie C, Nwobodo ED (2004). Noise induced hearing impairment as an occupational risk factor among Nigerian traders. Niger. J. Physiol. Sci. 9:14-19. [11] Wu TN, Liou SH, Shen CY, Hsu CC, Chao SL, Wang JH, Chang SF, Ko KN, Chiang HC, Chang PY (1998). Surveillance of noise-induced hearing loss in Taiwan, ROC: A report of the PRESS-NIHL results. Prev. Med. 27(1):65-69 [12] Agbalagba E.O., Akpata A.N.O., Olali, S.A. (2013) Investigation of noise pollution levels of four selected sawmill factories in Delta State, Nigeria. Advances in Applied Acoustics Journal. [13] Ali, S.A. (2011) Industrial noise levels and annoyancein Egypt. Applied Acoustics [14] Ampofo, D.K. (2012) Evaluation of noise levels of corn mills Ablekuma northsubmetro,Accra.M.ScDissertation at Kwame Nkrumah University of Science and Technology, Kumasi.
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