understand. Fur<strong>the</strong>r, PM is qualitatively no different than <strong>the</strong> gaseous pollutants in this regard.There<strong>for</strong>e, it still makes sense to consider <strong>the</strong> gaseous pollutants as potential confounders <strong>of</strong> PM.Similarly, attempts to stop considering some <strong>of</strong> <strong>the</strong> co-pollutants as confounders, arguing, as isdone in <strong>the</strong> CD, that <strong>the</strong>y are merely steps in <strong>the</strong> mechanistic causal chain (see below), are notvalid.4. Regional heterogeneityThe emphasis in this CD on NMMAPS II is justified. The heterogeneity in <strong>the</strong> estimates<strong>of</strong> PM effect across US cities is obvious (28 <strong>of</strong> 88 cities having non-positive estimates <strong>of</strong> effect).This is <strong>the</strong> first good impression available <strong>of</strong> <strong>the</strong> degreee <strong>of</strong> heterogeneity that is present. Theheterogeneity might be due to random variation in estimates <strong>of</strong> effect (presumably supported by<strong>the</strong> CD in developing <strong>the</strong> argument that in general <strong>the</strong> absence <strong>of</strong> effect is observed <strong>for</strong> citieswith fewer observations, i.e., less power), or it may represent true regional differences. It shouldbe noted that <strong>the</strong> heterogeneity observed in <strong>the</strong> NMMAPS II study <strong>of</strong> 88 cities is present <strong>for</strong>single-pollutant models. PM effects from two-pollutant, or multipollutant models, would beexpected to have shown even more heterogeneity among <strong>the</strong> cities. Fur<strong>the</strong>r, interpreting <strong>the</strong>meaning <strong>of</strong> an estimate <strong>of</strong> overall effect (0.5% increase <strong>for</strong> a 10 mcg/m 3 increase at lag 1)assumes that <strong>the</strong> effects across city come from a single distribution <strong>of</strong> effects, which might notbe <strong>the</strong> case if heterogeneity <strong>of</strong> effects is real and due to some as yet to be identified factor(s) thatdistinguishes cities in which effects are detected from those in which <strong>the</strong>y are not. The cause(s)<strong>of</strong> this apparent heterogeneity (random variation or “real”) clearly has implications <strong>for</strong> settingUS-wide, health-based standards.An attempt is made to explain part <strong>of</strong> <strong>the</strong> observed heterogeneity <strong>of</strong> effect by noting thatnegative or absent effects were more likely to be seen in cities with <strong>the</strong> lower concentrations <strong>of</strong>PM (6-263, line 30-). This is unjustified given that <strong>the</strong> NMMAPS investigators explicitly testedthat hypo<strong>the</strong>sis and found no support <strong>for</strong> it.5. Chronic effectsAlthough <strong>the</strong> cohort studies are invariably referred to as studies evaluating <strong>the</strong> effects <strong>of</strong>“long-term”, or “chronic”, exposure, this is an assumption. The title <strong>of</strong> section 6.2.3 (“MortalityEffects <strong>of</strong> Long-Term Exposure to Ambient <strong>Particulate</strong> <strong>Matter</strong>”) already makes this assumption.Merely because exposure in <strong>the</strong>se studies is specified in terms <strong>of</strong> long-term averages, this doesnot imply that <strong>the</strong> observed associations are in fact due to <strong>the</strong>se long-term averages. Analternative is that <strong>the</strong>se effects are simply a cumulation <strong>of</strong> acute effects. It is argued that simpleaccumulation <strong>of</strong> acute effects cannot account <strong>for</strong> <strong>the</strong> size <strong>of</strong> effects estimated in <strong>the</strong> cohortstudies. However, <strong>the</strong>se estimates are somewhat sensitive to covariates and analytic approach(e.g., adjustment <strong>for</strong> population mobility, spatial correlation and control <strong>for</strong> SO 2 as demonstratedin <strong>the</strong> ACS Reanalysis Study). There<strong>for</strong>e, confidence in <strong>the</strong> size <strong>of</strong> <strong>the</strong>se reported effectestimates is not great. Reflecting even more confusion is <strong>the</strong> statement in <strong>the</strong> CD (p.6-80, line31) that chronic effects must be present since effect estimates <strong>for</strong> chronic PM exposure are muchhigher than those <strong>for</strong> <strong>the</strong> time series studies; this point is irrelevant and in no way argues that achronic effect above that observed in <strong>the</strong> time series studies must be present (this is an “applesand oranges” comparison). The comparison <strong>of</strong> <strong>the</strong> spatial features <strong>of</strong> effects from NMMAPS IIand <strong>the</strong> Cohort Reanalysis Project (6-265, line 24-31) does not necessarily enhance <strong>the</strong> argument<strong>for</strong> consistency, given <strong>the</strong> above.Effects <strong>of</strong> acute exposures can <strong>the</strong>oretically be approximated by calculating a cumulation<strong>of</strong> acute effects, something which has been attempted previously. I recommend revisiting <strong>the</strong>issue <strong>of</strong> cumulating time series effects (incorporating <strong>the</strong> impact <strong>of</strong> multiple days) to compare to<strong>the</strong> range <strong>of</strong> estimates <strong>of</strong> PM effect from <strong>the</strong> cohort studies (esp. <strong>the</strong> ranges <strong>of</strong> effects estimatedin <strong>the</strong> ACS reanalyses based on different models). If this argument is convincing in showingthat acute effects could not conceivably reproduce findings from <strong>the</strong> cohort studies, <strong>the</strong>n <strong>the</strong>above points become moot. The lung cancer findings, if valid, would provide a strong argument<strong>for</strong> chronic effects, but this discussion is largely lacking from this version <strong>of</strong> <strong>the</strong> CD.In my opinion, given <strong>the</strong> above, <strong>the</strong> conclusion regarding “long-term exposure to PM”(6-94) needs to be qualified.A - 13
6. Susceptible sub-populationsIt is surprising that <strong>the</strong> most important study to date on identifying susceptibility <strong>of</strong>populations subgroups based on pre-existing medical disorders is discussed so little (Goldberg2000), being presented last in a discussion <strong>of</strong> previous studies that, because <strong>of</strong> design, are limitedin <strong>the</strong> in<strong>for</strong>mation that <strong>the</strong>y provide in this regard. This study confirms many <strong>of</strong> <strong>the</strong> findings <strong>of</strong>studies that attempt to address <strong>the</strong> issue by stratifying on cause <strong>of</strong> death. However, it isinteresting that no increased risk was identified <strong>for</strong> <strong>the</strong> subgroup <strong>of</strong> subjects with chronicobstructive lung disease, a group considered to be at high risk based on cause-<strong>of</strong>-deathstratifications. Paren<strong>the</strong>tically, I believe <strong>the</strong> description <strong>of</strong> <strong>the</strong> Goldberg study gets it wrong.PM pollutant measures were associated with mortality, not with acute respiratory disease, etc.(p.6-74, line 24-30) as stated. The latter were <strong>the</strong> susceptibility subgroups (that is, <strong>for</strong> assessinginteraction effects, essentially).There is legitimate concern that <strong>the</strong> stratification <strong>of</strong> by cause <strong>of</strong> death is fraught withproblems misclassifying7. Miscellaneous “large” issuesGaseous pollutant effects: The summaries provide relatively balanced syn<strong>the</strong>ses <strong>of</strong>recent gaseous findings (p.6-75, line 14-23 & p. 6-76, line 24-). This balance is sometimeslacking in <strong>the</strong> descriptions <strong>of</strong> specific studies in which a “particle-centric” perspective ismaintained (see point 2 above). For example, <strong>the</strong> conclusion that fine PM effects oncardiovascular hospitalizations are most important (6-235, line 1) ignores <strong>the</strong> important findingsby Burnett and Moolgavkar on <strong>the</strong> role <strong>of</strong> gases in affecting estimates <strong>of</strong> PM effects.Threshold concentrations: The discussion <strong>of</strong> thresholds is unconvincing. The argumentattributed to Schwartz that a threshold is ma<strong>the</strong>matically impossible in <strong>the</strong> face <strong>of</strong> populationdifferences in sensitivity (p.6-246, line 3-5) holds only if <strong>the</strong> most sensitive members <strong>of</strong> apopulation are sensitive to very low concentrations, which may not be <strong>the</strong> case. Fur<strong>the</strong>r, <strong>the</strong> CDis not consistent in its support <strong>of</strong> a no-threshold concentration-response relationship. Theargument that heterogeneity in studies <strong>of</strong> PM composition is due to variable concentrations <strong>of</strong>PM components (with studies showing no effects having concentrations too low to show effects,6-78, line 1) is not consistent with <strong>the</strong> absence <strong>of</strong> thresholds. The same point can be made ifheterogeneity <strong>of</strong> effects in NMMAPS is argued to be due to variability in PM concentrationsacross city (see point 4 above).Measurement error: The description <strong>of</strong> <strong>the</strong> Zeger (2000) work on measurement error(6.249-252) is just about comprehensible. “Dumbing” this section down, if possible, would beallow it to have <strong>the</strong> impact that it deserves.Smaller issues <strong>for</strong> chapter 6 (by page number):Introduction6-2 I don’t believe Rothman would assign more inferential strength to case-control studiesthan cohort studies (line 14).6-3 The prospective cohort studies in this setting do not make use <strong>of</strong> “individual exposure”(line 2). The subjects in a cohort study do not need to be recruited independent <strong>of</strong>exposure (line 4), and in fact were not (e.g., 6-Cities Study).6-4 Line 19-25. The discussion <strong>of</strong> causal pathways, although correct, is not relevant in thiscontext. Because SO 2 contributes to sulfate <strong>for</strong>mation does not imply that SO 2 effectscannot be separated from sulfate effects, if correlations are not too strong. But, this is anissue <strong>of</strong> collinearity.6-5 One gets <strong>the</strong> impression here that meteorology is acting solely as an effect modifier (line1), when in fact <strong>the</strong> more important issue is its role as a potential confounder (see“Confounding” section above).A - 14
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Günter Oberdörster, PhDChapter 7
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