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1 thod of choice that could be adapted to real smelters.
3 erties of particles next to an active copper smelter and mine tailings by the towns of Hayden and Win
4 erm exposure to PM2.5 in cohorts of aluminum smelters and fabrication workers in the United States wh
5 ticulate matter emissions near active copper smelters and mine tailings in the southwestern United St
6 y prior exposure, was documented only in the smelters and required the use of marginal structural Cox
7 smelting facilities, herein referred to as "smelters" and workers in fabrication facilities, herein
8 Soils in the vicinity of nonferrous metal smelters are often highly polluted by inorganic contamin
10 l scaling of soil Hg emissions following the smelter closure indicated that the landscape impacted by
11 elevated TGM concentrations before and after smelter closure was from surface-air fluxes from mercury
14 examined within a Kitimat, Canada, aluminum smelter cohort (n = 7,026) linked to a national mortalit
15 ure indicated that the landscape impacted by smelter deposition emitted or re-emitted almost 100 kg p
16 hs or more prior to 1957 at a Montana copper smelter from January 1, 1938 through December 31, 1989.
20 emistry data collected from seven lakes near smelters in Sudbury (Ontario, Canada) we examined the li
21 our Se-contaminated lakes located near metal smelters in the eastern Canadian cities of Sudbury and R
22 a for the hourly population at 6 US aluminum smelters, injuries that occurred from January 1, 1996, t
23 chemical composition of industrial aluminum smelter is a challenge mainly for physicochemical reason
24 e of respiratory symptoms among employees in smelters is positively associated with dust exposure.
25 ltiple lines of evidence point to the Asarco smelter, located in the Main Basin of Puget Sound, as th
26 were studies of lead and arsenic toxicity at smelters, mercury in paint and beauty creams, dioxin in
28 tly elevated during the time period when the smelter operated (4.1 +/- 3.7 ng m(-3)), decreased only
29 were collected at three sites: (i) an active smelter operation in Hayden, AZ, (ii) a legacy mining si
31 orewaters from Harjavalta (HAR, near a Cu-Ni smelter), Outokumpu (OUT, near a Cu-Ni mine), and Hietaj
32 ic acid (PA) or rock phosphate were added to smelter (PP2), nonferrous slag (SH15), and shooting rang
33 tudy results showed that deposition from the smelter resulted in the surrounding soil being enriched
34 g particulate matter emitted from the Asarco smelter's main stack at the peak of production, and (3)
35 veral lines of evidence indicated that while smelter stack emissions would occasionally mix down to t
36 ) mine tailings from Iron King Mine Humboldt Smelter Superfund site when amended with a range of comp
39 ts (OR = 1.9, 95% CI: 0.5, 6.5), foundry and smelter workers (OR = 2.6, 95% CI: 0.5, 13.1), petroleum
40 se mortality among 2,802 Tacoma, Washington, smelter workers by using 1) internal comparisons to cont
42 ced significantly in the thalamus and PCC of smelter workers compared to controls (p = 0.030 and p =
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