120 µg/m 3 (0.03-0.04 ppm) respectively. The paper does not state the duration ofsamples or the locations where the samples were taken. In the paper Dean used 40ppm-years (0.5 – 6.6 additional leukemia cases per 1000 exposed workers) as thecumulative dose for the risk calculation.The paper identifies a potential exposure to benzene in relation to venting of outboarddiesel tanks inboard to allow for the increasing seawater pressure during diving.2. A recent study by Glass et al (2005) of the Australian petroleum workersfound a strong association between benzene and leukemia at exposure doses greaterthan the cumulative dose of 16 ppm-years.3. Severs & Sabiston (2000) reported levels of benzene in the range 87 – 249µg/m 3 (0.027 – 0.078 ppm) onboard HMCS Okanagan which is consistent with theresults reported by Dean (1996).4. As benzene is an ingredient of diesel fuel and diesel exhausts, Boffetta (2004)has reviewed the published epidemiological studies involving diesel exhausts toevaluate whether there is evidence to support that diesel exhaust exposure increasesthe risk of leukemia, and Acute Myeloid leukemia (AML) in particular. A total of 27studies and reports were considered. Studies covered a wide range of occupations andindustries. The conclusion was that available evidence did not support the hypothesisthat there was an association between diesel exhausts and risk of leukemia and AMLin particular.5. In a very recent paper (Kopstein (2006)) advised listing of benzene in MaterialSafety Data Sheets (MSDSs) be mandatory even if present as a trace contaminant (
occupational health exposure studies to diesel emissions as the sampling and analysismethodology was not the same nor was the data compared with other countriesregulatory values. Due to the uncertainty of what degree of exposure constitutes anunacceptable level of risk, bodies such as International Agency for Research onCancer (IARC, 1989b), World Health Organisation (WHO, 1996), Health EffectsInstitute (HEI, 2002), US National Institute of <strong>Occupational</strong> Safety and Health(NIOSH 1988), and American Conference of Governmental Industrial Hygienistshave not proposed or set an occupational exposure level or a level of risk. Thesebodies accept that the animal data for carcinogenicity is strong but there areuncertainties in the human studies due to confounders and exposure data deficiencies.The US Mine Safety and Health Administration (MSHA, 2005) and the GermanBundesministerium fűr Arbeit (German Ministry of Labour, 2005) have set exposurelevels for the mining industries in their respective countries based on elementalcarbon sampled and analysed by specific methods. The German value is a technicallimit, which means that the best available technology should be used to control theexposure.Diesel FuelThe types, composition, and health effects of diesel fuel are well reviewed in anumber of publications (IARC, 1989a), (World Health Organisation WHO, 1996).Marine diesels may contain more than 10% polycyclic aromatic hydrocarbons whichare associated with possible cancer causation. However in their review of diesel fuelIARC concludes that there is inadequate evidence for carcinogenicity in humans butlimited evidence for experimental animals exposed to marine fuel, and rates it as apossible human carcinogen.Exposure to diesel fuel (liquid) and mists (droplets/aerosols) occurs through fuelhandling, cleaning of diesel parts during maintenance, and leakages and/or incompletecombustion in diesel engines/exhausts. A likely source of diesel vapour/mist in airoccurs during the period between opening and shutting of the explosion cocks on startup as stated by the submariners during the walk through on HMAS ONSLOW andfocus groups.The hydrocarbon emissions (vapour and mist) are not uniquely due to diesel but alsomay arise from hydraulic fluids, lubricating oils and mists from draining the aircompressor (Rubly (2005)).From the literature it appears there has been a tendency to measure volatile organiccompounds as a whole as it can be done in real time. This technique is fine if thepurpose is to identify the source of emission and track its behaviour but it does notgive any information about the composition and concentration of the individualcomponents that make up that emission. Only one study (Severs & Sabiston, (2000))has reported some of the components and their concentrations.Diesel ExhaustDiesel exhausts are a complex mixture of gases (carbon monoxide, carbon dioxide,sulphur dioxide, oxides of nitrogen), vapour/mists (a very broad range of organiccompounds and their oxidation products), and particulate matter (including carbon,high molecular weight polycyclic aromatic compound, organic heterocycliccompounds, inorganic sulphates and nitrates, and metals (IARC (1989)). It is not39
- Page 1 and 2: Oberon Class SubmarineOccupational
- Page 3 and 4: ContentsExecutive Summary..........
- Page 7 and 8: There is strong anecdotal evidence
- Page 10: decommissioned) in 1992. The five r
- Page 13 and 14: Ventilation Arrangements(from Kane
- Page 15 and 16: Approach Adopted in this StudyIn or
- Page 17 and 18: Departmental DocumentsDefence Scien
- Page 19 and 20: of diesel-electric propulsion and a
- Page 21 and 22: 4. Gan & Mazurek (~ 2005), “Expos
- Page 23 and 24: to avoid short and long term effect
- Page 25 and 26: from the air vents, in excess of 65
- Page 27 and 28: Overseas Studies Relating to Oberon
- Page 29 and 30: For the compounds identified with *
- Page 31 and 32: pollution by 33%. There is a length
- Page 33 and 34: Air Quality Standards1. In his brie
- Page 35 and 36: Continuous Exposure Guidance levels
- Page 37: ClothingStandard orders refer to th
- Page 41 and 42: Issues of body absorption of diesel
- Page 43 and 44: eading time is 10 minutes. The 0.2
- Page 45 and 46: Comment. This study is cited as the
- Page 47 and 48: • secrecy associated with submari
- Page 49 and 50: 3-methyl hexanedimethylcyclohexane1
- Page 51 and 52: - performance of tasks in cramped c
- Page 53: smoke candles ·torpedo 'hot runnin
- Page 56 and 57: The control room onONYX, looking af
- Page 58: Committee and the University of Que
- Page 61 and 62: Many references were made to a sens
- Page 63 and 64: safety was compromised for speed an
- Page 65 and 66: Health HazardsThe health hazards id
- Page 67 and 68: Psychological• Stress caused by n
- Page 69 and 70: Tar epoxiesJason pistols?berylliumE
- Page 71: Some of the psychological effects i
- Page 75 and 76: Table 3: Rank and job description b
- Page 77 and 78: Junior SailorsEngineeringTradespers
- Page 79 and 80: Seaman- maintainerelectricalLeading
- Page 81 and 82: Table 4: Exposure Profile and Quali
- Page 83 and 84: DiscussionThis project appears to b
- Page 85 and 86: in surface vessel engine rooms. The
- Page 87 and 88: exceeded the guideline of 50 microg
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ConclusionIn conclusion, the occupa
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AnnexesAnnex A: The Project TeamAnn
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Annex B toOberon Class SubmarineOcc
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locked cabinets at CMVH and accesse
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THIS PAGE WILL BE DETACHED FROM YOU
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• What were the specific tasks co
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List of Documents not AvailableAnne
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ReferencesLiterature ReviewAdelson
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Gorman R., Liss G.M., (1985), “Oc
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McKinnery, W. N., Jr. and Moore, R.
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Aeronautical and Maritime Research
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