“23…He undertook car servicing in a dedicated lubrication bay (the lube bay), opposite the office in which EJ and another lady worked. He estimated that the lube bay door was no more than eight yards from the office. The lube bay’s sliding doors were almost always open, save in very cold weather, as RR was using a compressed air-line. RR believed the office door was kept closed, except in hot weather. 24. RR’s job was to service and maintain vehicles brought into the workshop. This brought him regularly into contact with asbestos, particularly in the course of replacing brake shoes and clutch drive plates. The brake linings and clutch linings contained asbestos. RR described the process, undertaken by him regularly, of removing brake drums, which would have dust and dirt where the brake linings had deteriorated through wear and tear. The asbestos brake shoes and clutch drive plates would wear out over time creating dust within the brake drum and clutch housing. Whether replacing or renewing brake linings and clutch plates, RR used a compressed air-line to blow dust out of the drum, shoes, brake drum plates and clutch housing. This process released clouds of dust into the lube bay as well as out into the yard, the air-line being used to blow it out there. RR described being covered in asbestos dust, on his hands, face, hair and overalls. 25. In addition to blowing out the brake dust, RR often sanded the asbestos dust from the brake shoes and filed the edges to ensure a smooth connection. This would be done by chamfering, usually by hand with a coarse file, but occasionally with a grinding machine. RR would wear a single pair of overalls for a week at a time, after which they would be laundered. His own clothes beneath would also get contaminated. RR described seeing EJ most days as he would often have to go into the office if he needed something. 26. Understandably, RR could not provide a definitive figure for how often he serviced vehicles over the more than thirty-five years that he worked for D, but it was a regular part of his job. He stated, “On average, bearing in mind there were some weeks when I would do it more than others, I estimate that one day a week was spent servicing brake shoes and clutch drive plates and using a compressed airline in the manner that I’ve described to blow out brake drums and clutch plate housing before I started working on them and again once I’d finished the job.””
“82. The following matters pertaining to the relevant period did not appear to be in dispute and/or were matters about which there was no evidence to the contrary: (i) The physical location of the lube bay and the office in which EJ worked, relative one to the other; (ii) The lube bay doors would usually be open, unless the weather was particularly cold; (iii) The office door would usually be closed, unless the weather was particularly warm; (iv) Dust containing asbestos would be generated within the lube bay during the various tasks described by RR due his use of a compressed air line; (v) Use of the air line during tasks created dust both within the lube bay and, when the lube bay doors were open, out into the yard; (vi) The air-line was also used at the end of a working day to clean out the lube bay by blowing dust and detritus into the communal yard that separated the lube bay and office; (vii) The asbestos used in drum brake and clutch linings was chrysotile (albeit commercial chrysotile generally contained tremolite, an amphibole form of asbestos); (viii) Chrysotile asbestos is recognised to be of substantially lower potency in inducing MMP when compared with amosite or crocidolite); (ix) The asbestos component of the dust produced from used brakes and clutches that were being replaced would have been approximately 1–2 % thereof, as a result of chemical changes caused during use; (x) The communal yard was partially covered in at the front by the entrance/exit to the garage.”
“102…The evidence from C and RR identifies the following points, with my additional observations added in brackets: (i) EJ’s leaving work at the end of the day when it coincided with RR cleaning out the workshop with the air-line (potentially one day per week with some weeks involving more than one day); (ii) During visits by RR to EJ’s office (one or more visits on one day or occasionally more per week with asbestos-containing dust from that day’s work on overalls and on his person, as well as on other days when wearing overalls with previously contaminated dust on them); (iii) When the office and lube bay doors were simultaneously open (which seems to have been only occasionally); (iv) On occasions when EJ was walking across the forecourt (referred to as more than once a day by C); and (v) On (rare) occasions when EJ may have gone into the lube bay on a day when asbestos-containing dust was being generated. 103. RR’s evidence is that the office door was eight yards away (about 25 feet) from the lube bay and this was the focus of Messrs Chambers’ and Stear’s consideration of percentage estimates. Mr Chambers assumed a 90% reduction for 20-30 feet distance indoors and a further 50% reduction for short distance outdoors, reaching an exposure percentage of 5% relative to RR’s. Mr Stear considered likely time spent by EJ walking across the courtyard as a proportion of a day, applying it to a figure for 20-30 feet distance from source. This results in a range of 0.001 to 0.002 f/ml-y for an estimated time period of five to ten minutes.”
“82. Whether it is appropriate to draw an inference at all and, if so, the precise nature and extent of such an inference will depend on the particular circumstances of each case. Relevant considerations will include the proximity between a breach of duty and the non-available evidence, the effect of the other evidence before the court and what other evidence might have been available but which is not before the court.”
“100. I have also considered carefully the adverse inference point made by C, but I do not find it helpful in this case. The difference between the calculations of the occupational hygienists rested in large measure on their very different interpretation of RR’s evidence, which required judicial determination. Any measuring of levels could only have assisted in relation to RR’s exposure, but would then have been the subject of judicial determination as to what such figures represented. Any measurement would not have assisted in relation to identifying the reduction factors to be applied to EJ’s exposure, which also required judicial determination. It does not seem to me be a sustainable argument that the lack of monitoring should lead the Court to adopt uncritically Mr Chambers’ calculations in circumstances where I have concluded that they do not reflect the factual matrix I have found to exist at the relevant time.”
“2.—(1) In these Regulations, unless the context otherwise requires— “action level” means one of the following cumulative exposures to asbestos over a continuous 12-week period when measured or calculated by a method approved by the Health and Safety Commission, namely— (a) where the exposure is to asbestos consisting of or containing any crocidolite or amosite, 48 fibre-hours per millilitre of air; or (b) where the exposure is to asbestos consisting of or containing any other types of asbestos but not crocidolite or amosite, 120 fibre-hours per millilitre of air; or (c) where both types of exposure are concerned, a proportionate number of fibre-hours per millilitre of air; “adequate” means adequate having regard only to the nature and degree of exposure to asbestos and “adequately” shall be construed accordingly; “approved” means approved for the time being in writing by the Health and Safety Commission or the Health and Safety Executive as the case may be; “asbestos” means any of the following minerals, that is to say, crocidolite, amosite, chrysotile, fibrous actinolite, fibrous anthophyllite, fibrous tremolite and any mixture containing any of those minerals; “asbestos area” and “respirator zone” shall be construed in accordance with regulation 14; “control limit” means one of the following concentrations of asbestos in the atmosphere when measured or calculated by a method approved by the Health and Safety Commission, namely— (a) for asbestos consisting of or containing any crocidolite or amosite— (i) 0.2 fibres per millilitre of air averaged over any continuous period of 4 hours, (ii) 0.6 fibres per millilitre of air averaged over any continuous period of 10 minutes; (b) for asbestos consisting of or containing other types of asbestos but not crocidolite or amosite— (i) 0.5 fibres per millilitre of air averaged over any continuous period of 4 hours, (ii) 1.5 fibres per millilitre of air averaged over any continuous period of 10 minutes; “the Executive” means the Health and Safety Executive. … 15.—(2) The employer shall keep a suitable record of any monitoring carried out in accordance with paragraph (1) and that record or a suitable summary thereof shall be kept— (a) in a case where exposure is such that a health record is required to be kept under regulation 16, for at least 30 years [amended to 40 years by paragraph 6 of the Schedule to the Control of Asbestos atWork (Amendment) Regulations 1992 ]; (b) in any other case, for at least five years.”
“(i) Mesothelioma is always, or almost always, caused by the inhalation of asbestos fibres. (ii) A significant proportion of those who contract mesothelioma have no record of occupational exposure to asbestos. The likelihood is that in their case the disease results from inhalation of asbestos dust that is in the environment. There is, however, a possibility that some cases of mesothelioma are “idiopathic”, i e attributable to an unknown cause other than asbestos. [Counsel for the appellant in that case] submitted that the Peto Report indicates that this is more than a possibility, but I do not so read it. I do not, however, think that it matters whether some cases of the disease are idiopathic. (iii) The more fibres that are inhaled, the greater the risk of contracting mesothelioma. (iv) There is usually a very long period between the exposure to asbestos and the development of the first malignant cell. Typically this can be at least 30 years. (v) There will be a lengthy period between the development of the first malignant cell and the point at which the disease can be diagnosed. At the time of Fairchild this was thought to be ten years, but is now thought to be at least five years. During this period, further exposure to asbestos fibres will have no causative effect. (vi) The mechanism by which asbestos fibres cause mesothelioma is still not fully understood. It is believed that a cell has to go through six or seven genetic mutations before it becomes malignant, and asbestos fibres may have causative effect on each of these. (vii) It is also possible that asbestos fibres have a causative effect by inhibiting the activity of natural killer cells that would otherwise destroy a mutating cell before it reaches the stage of becoming malignant.”
“I doubt whether it is ever possible to define, in quantitative terms, what for the purposes of the application of any principle of law is de minimis. This must be a question for the judge on the facts of the particular case. In the case of mesothelioma, a stage must be reached at which, even allowing for the possibility that exposure to asbestos can have a cumulative effect, a particular exposure is too insignificant to be taken into account, having regard to the overall exposure that has taken place.”
“The reality is that, in the current state of knowledge about the disease, the only circumstances in which a court will be able to conclude that wrongful exposure of a mesothelioma victim to asbestos dust did not materially increase the victim’s risk of contracting the disease will be where that exposure was insignificant compared to the exposure from other sources.”
“The present position, exemplified by the facts of these very appeals, can be simply stated as follows: any person who negligently or in breach of duty exposes another more than minimally to the inhalation of asbestos fibres will be liable to make full compensation if that other develops mesothelioma…”
“a dose of asbestos which was properly capable of being neglected could be defined as a dose which a medical practitioner who is aware of the medical risks would define as something that the average patient should not worry about.”
“H&D’s primary purpose was not to deal with low doses…” “[t]he problem comes when trying to apply it to exposures anything between 100 and 1000 times smaller than the data on which the model is built…” “the problem is ‘untestable assumptions…’” “Professor Norrie had never seen extrapolation down 100 or 1000 times from reliable data….”, “[he] cautioned against accepting the view of others that H&D is ‘the best we have got’ so that it is safe to use”. “[he] considered H&D not fit for purpose for extrapolating down.” “As to H&D, he too made reference to the WATCH Committee’s cautioning about the use of that meta-analysis, with a detailed critique setting out the reliability difficulties of using the paper in the way suggested in this case…”
“WATCH considers that all of these uncertainties impose limitations on the reliability of risk estimates produced by the H&D model, particularly when it is extrapolated to exposure situations and populations beyond those covered by observed data. Hence WATCH confirms the statement in its 2008 conclusion that risk estimates derived by extrapolation of the model should not be taken to be reliable absolute risk values. The limitations on the reliability of risk estimates derived using the H&D model become more pronounced the further the model is extrapolated from the occupational exposure scenarios and data on which it is based. Therefore, as recommended in the WATCH position of 2008, WATCH considers that extrapolated risk estimates might be most useful as rough indicators of the magnitude of risk that might be involved in different situations; and hence the relative extent of concern and prompting towards risk management action that can be justified in different situations. WATCH observes that deriving risk estimates by extrapolating the H&D model is a straightforward process; however, there was a variation of opinions across the committee, with no clear majority or consensus view as to the appropriateness of presenting such estimates in numerical form or using them for decision-making in a way that might be taken by others to imply confidence in their numerical accuracy.”
“A useless model is as good as tossing a coin … I would not use a model that was close to useless.” “I mean, I do not want to be melodramatic, but you probably could get pretty much any answer you wanted, depending on how you did the extrapolation.”
“I accept the thrust of Professor Norrie’s evidence which I interpret to be the exercise of significant caution when seeking to extrapolate down to low doses from H&D’s model equation. His generalised reference to any useless model being as good as ‘tossing a coin’ seemed to me to be an attempt to put into layman’s terms the potential outcome if that significant caution were not exercised.”
“I found Professor Jones’ insightful observations and opinions on the issues of lifetime risk, his worked models and his conclusions highly persuasive.”
“But you have got to be careful with that argument about: “okay, it is the best that we have got and therefore we are safe to proceed”
“I mean, having thought about it quite a bit during trial, I think I would probably now say that 0.5 is too high but that maybe taking account of (inaudible) figure for (inaudible) spontaneous, probably it’s going to be somewhere in the region of 0.1 to 0.5, so somewhere in that region. I think 0.5 probably is rather too high, although, of course, it depends on (inaudible) risk. Yes, somewhere in the region of 0.1 to 0.5 would be a range.”
“Having thought that 0.5 was a little too high, and taking account of spontaneous cases the figure would be somewhere in the region of 0.1 – 0.5, depending on the magnitude of the environmental risk.”
“where there is epidemiological evidence of association, the court should not proceed to find a causal relationship without further, non-statistical evidence.”
“Finally, nothing which I have said is intended to discourage the use of epidemiological evidence or to depreciate its value in cases where a claimant has to prove his case on the balance of probabilities. Far from it. Obviously, for example, epidemiology is likely to lie behind much of the evidence on which a court determines whether an exposure has materially increased the risk of the claimant developing a disease. Epidemiological evidence may also be relevant when deciding whether it would have been reasonable for a defendant to take precautions to avoid the risk of the claimant suffering a particular injury - say, the side-effect of a drug. And, of course - it must be emphasised once more - epidemiological and statistical evidence may form an important element in proof of causation. I have simply emphasised the point made by Phipson on Evidence, 17th ed (2010), para 34-27, that, unless a special rule applies, “Where there is epidemiological evidence of association, the court should not proceed to find a causal relationship without further, non-statistical evidence”
“Obviously … epidemiology is likely to lie behind much of the evidence on which a court determines whether an exposure has materially increased the risk of the claimant developing a disease.”
“the employers should be liable for an injury, squarely within the risk which they created and that they, not the pursuer, should suffer the consequence of the impossibility, foreseeability inherent in the nature of his injury, of segregating the precise consequences of their default.”
“109. Leaving to one side their stated opinions about H&D, I consider the evidence of Professors Norrie and Jones to be, in many ways, complementary. Professor Norrie provides the epidemiologist’s overview from an entirely ‘clinical’ or academic assessment, whilst Professor Jones provides practical application, borne of many years’ experience. Professor Norrie’s evidence that the exposure metric of f/m-y could have one meaning when applied to occupational exposure and another when describing ambient exposure was surprising given his apparent familiarity with the studies referred to in his report. This was though his first foray into the world of asbestos-related disease and that misunderstanding alone does not automatically undermine the value of the remainder of his evidence. Professor Jones, on the other hand, was able to draw on extensive, relevant experience, applied to the factual matrix in this case and producing worked models in tables to illustrate his opinion. 110. I accept the thrust of Professor Norrie’s evidence which I interpret to be the exercise of significant caution when seeking to extrapolate down to low doses from H&D’s model equation. His generalised reference to any useless model being as good as ‘tossing a coin’ seemed to me to be an attempt to put into layman’s terms the potential outcome if that significant caution were not exercised. In any event, Professor Jones did indeed, in my judgment, pay proper heed to the need for caution in addressing H&D. In his report and in his oral evidence he gave persuasive evidence about the formulations within his report and the range of calculations. As already indicated, there is an inadequacy of evidence to reach absolute figures in this case and the Court is dealing with likely ranges and orders of magnitude. 111. Where I do part company with Professor Norrie is the suggestion in his report, when considering P&R [Peto Report], that as EJ [Mrs Johnstone] contracted MMP and she had had occupational exposure at D that she would be more likely to be in that one third of the cohort of cases in women (recognised occupational exposure). That was a rather simplistic approach, borne I expect of unfamiliarity with this area of industrial disease, bar the role he undertook in this case. On the other hand, Professor Jones in his evidence demonstrated fairly compellingly why the level of EJ’s exposure was such that she would more likely be within one or other of the remaining groups (either ambient/unrecognised occupational exposure or idiopathic). His observations must now be seen in the context of my findings that Mr Stear’s calculations are to be preferred. This leads to 0.1% or less increase in risk of developing mesothelioma. 112. I found Professor Jones’ insightful observations and opinions on the issues of lifetime risk, his worked models and his conclusions highly persuasive. Added to this was the evidence of Dr Moore-Gillon. The Court does not reach conclusions in any case purely on the grounds of an expert’s qualifications and/or experience, but Dr Moore-Gillon’s extensive, recent involvement in mesothelioma research is a matter of which the Court can properly take note in assessing the medical opinion that he expressed. Moreover, having concluded that reliance should be placed on Mr Stear’s estimates, there was no material divergence of opinion between the two medical experts. 113. Having considered carefully all of the expert evidence, I return to the observation I made much earlier that the fact that a person suffers some level of asbestos exposure and subsequently develops MMP does not without careful analysis of the individual circumstances establish a material increase in risk. I have reached the overall conclusion that any increase in risk in relation to EJ is in the order of 0.1% or less and that such a small increase does not satisfy the test of materiality.”
“We agree that during this time she will have been exposed to some extent to chrysotile asbestos. We agree that exposure to chrysotile asbestos is an established risk factor for pleural mesothelioma. We also agree that chrysotile asbestos is less potent in its effect on increasing mesothelioma risk than amosite or crocidolite, other forms of asbestos that have been used in the UK. The ratio of relative effect at occupational exposure levels may be around 1:100:500 for chrysotile (white), amosite (brown) and crocidolite (blue) asbestos, respectively (Hodgson & Darnton, 2000).”
“The asbestos used in drum brake and clutch linings was chrysotile (albeit commercial chrysotile generally contained tremolite, an amphibole form of asbestos)”