ライフサイエンスコーパス: trichloroethylene

1 toxicant and common environmental pollutant trichloroethylene.

2 metabolite of the environmental contaminant, trichloroethylene.

3 ins that constituted 12% of the reacted [14C]trichloroethylene.

4 covalently modified during the oxidation of trichloroethylene.

5 t also the chlorinated aliphatic hydrocarbon trichloroethylene.

6 degrading environmental pollutants, such as trichloroethylene, 2,4,5-trichlorophenoxyacetic acid (2,

7 ted ethenes (CEs) such as perchloroethylene, trichloroethylene and dichloroethylene are notorious gro

8 erformance with regards to the metabolism of trichloroethylene and the removal of a range of other to

9 redict concentration profiles of acetone and trichloroethylene and their intermediates and byproducts

10 lerant to the solvent effects of toluene and trichloroethylene at levels exceeding those of many radi

11 ulfonate, ethyl nitrosourea, benzo[a]pyrene, trichloroethylene, benzene, and sodium arsenate.

12 tive dehalogenation of perchloroethylene and trichloroethylene by vitamin B(12) produces approximatel

13 When the plants were exposed to gaseous trichloroethylene, chloroform, and benzene, they also de

14 Trichloroethylene-dependent inactivation of toluene 2-mo

15 ay all derive from the unstable intermediate trichloroethylene epoxide that was trapped by reaction w

16 s to have a high maximum intensity score for trichloroethylene exposure (OR 3.3, 95% CI 1.0-10.3).

17 studies were conducted to determine whether trichloroethylene exposure is neurotoxic to the nigrostr

18 studies showing that oral administration of trichloroethylene for 6 weeks instigated selective compl

19 biogenic catalysts were used to dechlorinate trichloroethylene in simulated marine environments.

20 Trichloroethylene is oxidized by several types of nonspe

21 and NADH were required to reconstitute full trichloroethylene oxidation activity in vitro.

22 rom Burkholderia cepacia G4 is implicated in trichloroethylene oxidation and is uniquely suggested to

23 xidation products, accounting for 84% of the trichloroethylene oxidized, were carbon monoxide, formic

24 inhalation and dermal exposure from handling trichloroethylene-soaked metal parts had Parkinson's dis

25 ee workers with workstations adjacent to the trichloroethylene source and subjected to chronic inhala

26 Coworkers more distant from the trichloroethylene source, receiving chronic respiratory

27 erse birth outcomes among mothers exposed to trichloroethylene (TCE) and tetrachloroethylene [or perc

28 ecting aqueous tetrachloroethylene (PCE) and trichloroethylene (TCE) as low as 80 and 74 microg/L in

29 Degradation studies were conducted with trichloroethylene (TCE) as the model contaminant.

30 eport the electrocatalytic dehalogenation of trichloroethylene (TCE) by single soft nanoparticles in

31 ies of oxidation of dichloroethene (DCE) and trichloroethylene (TCE) by three mutant strains of Pseud

32 agnetic field (AC EMF) to effectively remove trichloroethylene (TCE) from groundwater and saturated s

33 of aged (iron oxide coated) Fe(0) to degrade trichloroethylene (TCE) has revealed that, while neither

34 GC) adapted for the in situ determination of trichloroethylene (TCE) in indoor air in support of vapo

35 C mixtures composed of acetone, ethanol, and trichloroethylene (TCE) in pentane and methanol and acet

36 ted) Fe(0) was applied to the degradation of trichloroethylene (TCE) in seawater.

37 cy (EPA) completed a toxicological review of trichloroethylene (TCE) in September 2011, which was the

38 echlorination of perchloroethylene (PCE) and trichloroethylene (TCE) is a potential strategy for clea

39 Trichloroethylene (TCE) is a suspected renal carcinogen.

40 Trichloroethylene (TCE) is a widespread environmental po

41 Trichloroethylene (TCE) is one of the most widespread en

42 sorption/desorption behaviors of vapor phase trichloroethylene (TCE) is presented.

43 Trichloroethylene (TCE) is the most frequently detected

44 ation variability for risk assessment, using trichloroethylene (TCE) metabolism as a case study.

45 e applied to the automated classification of trichloroethylene (TCE) signatures from passive Fourier

46 ontinuous, short-term measurements of indoor trichloroethylene (TCE) vapor concentrations related to

47 Trichloroethylene (TCE) volatilization from leaves, trun

48 Ever exposure to trichloroethylene (TCE) was associated with significantl

49 o detect parts-per-billion concentrations of trichloroethylene (TCE) with a detection sensitivity of

50 tion Agency has identified quantification of trichloroethylene (TCE), an industrial solvent, in breas

51 odel for the destruction of (1) acetone, (2) trichloroethylene (TCE), and (3) polyethylene glycol (PE

52 Chlorinated solvents, especially trichloroethylene (TCE), are the most widespread groundw

53 thesis of this study was that metabolites of trichloroethylene (TCE), dichloroethylene (DCE) and rela

54 and dosed with equivalent concentrations of trichloroethylene (TCE).

55 sulfonate, I2S), and (iii) dechlorination of trichloroethylene (TCE).

56 creases its reactivity to pollutants such as trichloroethylene (TCE).

57 ts toluene, 1,1,1-trichloroethane (TCE), and trichloroethylene (TCY) affect ligand-gated ion channel

58 ene, xylenes), and chlorinated hydrocarbons (trichloroethylene, tetrachloroethylene, etc).

59 sing four common environmental contaminants (trichloroethylene, tetrachloroethylene, methyl tert-buty

60 Trichloroethylene, used extensively in industry and the

61 Small, volatile hydrocarbons, including trichloroethylene, vinyl chloride, carbon tetrachloride,

62 Complete dehalogenation of 20 mg L(-1) trichloroethylene was achieved within 1 h using 50 mg L(

63 Trichloroethylene was associated with scleroderma both b

64 In this work, the oxidation of trichloroethylene was studied with purified toluene 2-mo

65 Neurotoxic actions of trichloroethylene were demonstrated in accompanying anim