ライフサイエンスコーパス: smelter

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1 thod of choice that could be adapted to real smelters.

2 minum manufacturing workers, particularly in smelters, after adjustment for survivor bias.

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

9 icted the outcome and subsequent exposure in smelters but not in fabricators.

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

12 Following the smelter closure, air Hg(0) concentrations were reduced,

13 en the soil and the air before and after the smelter closure.

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.

17 ormation of fly ash (FA) from a secondary Pb smelter in acidic soil profiles.

18 Prior to its closure, the base-metal smelter in Flin Flon, Manitoba, Canada was one of the No

19 ted lake (Lake Dufault) located near a metal smelter in Rouyn-Noranda, Quebec.

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

27 cents in Torreon, a town in Mexico with a Pb smelter near residential areas.

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

30 During the period of smelter operation, air concentrations were elevated (30

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

37 In smelters, the Cox MSM hazard ratio comparing those alway

38 The Flin Flon, Manitoba copper smelter was Canada's largest point source of mercury emi

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

41 ic GABA level was significantly increased in smelter workers compared to controls (p = 0.009).

42 ced significantly in the thalamus and PCC of smelter workers compared to controls (p = 0.030 and p =

43 A cohort of nine Mn-exposed male smelter workers from an Mn-iron alloy factory and 23 gen

44 Using a cohort of 8,014 male copper smelter workers who were hired between 1938 and 1955 and

45 Physicians and surgeons, foundry and smelter workers, petroleum and gas workers, and painters

46 00) in the full and restricted subcohorts of smelter workers, respectively.

47 f all scores R(2) = 0.902, p = 0.001) in the smelter workers.

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