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1  contaminants of practical importance (e.g., trichloroethylene).
2  toxicant and common environmental pollutant trichloroethylene.
3 metabolite of the environmental contaminant, trichloroethylene.
4 ins that constituted 12% of the reacted [14C]trichloroethylene.
5  covalently modified during the oxidation of trichloroethylene.
6 t also the chlorinated aliphatic hydrocarbon trichloroethylene.
7  degrading environmental pollutants, such as trichloroethylene, 2,4,5-trichlorophenoxyacetic acid (2,
8 ted ethenes (CEs) such as perchloroethylene, trichloroethylene and dichloroethylene are notorious gro
9 rtain pesticides, the dry-cleaning chemicals trichloroethylene and perchloroethylene, and air polluti
10 erformance with regards to the metabolism of trichloroethylene and the removal of a range of other to
11 redict concentration profiles of acetone and trichloroethylene and their intermediates and byproducts
12 findings suggested that the codegradation of trichloroethylene and toluene may involve multiple biode
13 ttent oxygen supply for the codegradation of trichloroethylene and toluene.
14 rganic compounds such as 1,2-dichloroethane, trichloroethylene, and tetrachloroethylene into ethylene
15 lerant to the solvent effects of toluene and trichloroethylene at levels exceeding those of many radi
16 ulfonate, ethyl nitrosourea, benzo[a]pyrene, trichloroethylene, benzene, and sodium arsenate.
17 contaminants (i.e., 1,1,1-trichloroethane or trichloroethylene), but were slowed by natural organic m
18 tive dehalogenation of perchloroethylene and trichloroethylene by vitamin B(12) produces approximatel
19      When the plants were exposed to gaseous trichloroethylene, chloroform, and benzene, they also de
20 populations with functional genes related to trichloroethylene cometabolism and aerobic and anaerobic
21                                              Trichloroethylene-dependent inactivation of toluene 2-mo
22 ay all derive from the unstable intermediate trichloroethylene epoxide that was trapped by reaction w
23 s to have a high maximum intensity score for trichloroethylene exposure (OR 3.3, 95% CI 1.0-10.3).
24  studies were conducted to determine whether trichloroethylene exposure is neurotoxic to the nigrostr
25  studies showing that oral administration of trichloroethylene for 6 weeks instigated selective compl
26 biogenic catalysts were used to dechlorinate trichloroethylene in simulated marine environments.
27                                              Trichloroethylene is oxidized by several types of nonspe
28  and NADH were required to reconstitute full trichloroethylene oxidation activity in vitro.
29 rom Burkholderia cepacia G4 is implicated in trichloroethylene oxidation and is uniquely suggested to
30 xidation products, accounting for 84% of the trichloroethylene oxidized, were carbon monoxide, formic
31 inhalation and dermal exposure from handling trichloroethylene-soaked metal parts had Parkinson's dis
32 ee workers with workstations adjacent to the trichloroethylene source and subjected to chronic inhala
33              Coworkers more distant from the trichloroethylene source, receiving chronic respiratory
34 erse birth outcomes among mothers exposed to trichloroethylene (TCE) and tetrachloroethylene [or perc
35 ecting aqueous tetrachloroethylene (PCE) and trichloroethylene (TCE) as low as 80 and 74 microg/L in
36      Degradation studies were conducted with trichloroethylene (TCE) as the model contaminant.
37 eport the electrocatalytic dehalogenation of trichloroethylene (TCE) by single soft nanoparticles in
38 ies of oxidation of dichloroethene (DCE) and trichloroethylene (TCE) by three mutant strains of Pseud
39                                              Trichloroethylene (TCE) degradation half-lives at PL and
40 agnetic field (AC EMF) to effectively remove trichloroethylene (TCE) from groundwater and saturated s
41 of aged (iron oxide coated) Fe(0) to degrade trichloroethylene (TCE) has revealed that, while neither
42 GC) adapted for the in situ determination of trichloroethylene (TCE) in indoor air in support of vapo
43 C mixtures composed of acetone, ethanol, and trichloroethylene (TCE) in pentane and methanol and acet
44 ted) Fe(0) was applied to the degradation of trichloroethylene (TCE) in seawater.
45 cy (EPA) completed a toxicological review of trichloroethylene (TCE) in September 2011, which was the
46 echlorination of perchloroethylene (PCE) and trichloroethylene (TCE) is a potential strategy for clea
47                                              Trichloroethylene (TCE) is a suspected renal carcinogen.
48                                              Trichloroethylene (TCE) is a widespread environmental po
49                                              Trichloroethylene (TCE) is one of the most widespread en
50 sorption/desorption behaviors of vapor phase trichloroethylene (TCE) is presented.
51                                              Trichloroethylene (TCE) is the most frequently detected
52 ation variability for risk assessment, using trichloroethylene (TCE) metabolism as a case study.
53 e applied to the automated classification of trichloroethylene (TCE) signatures from passive Fourier
54 ontinuous, short-term measurements of indoor trichloroethylene (TCE) vapor concentrations related to
55                                              Trichloroethylene (TCE) volatilization from leaves, trun
56                             Ever exposure to trichloroethylene (TCE) was associated with significantl
57 o detect parts-per-billion concentrations of trichloroethylene (TCE) with a detection sensitivity of
58  steer H* toward reductive dechlorination of trichloroethylene (TCE), a common groundwater contaminan
59 SNZVI during the reductive dechlorination of trichloroethylene (TCE), a hydrophobic groundwater conta
60 tion Agency has identified quantification of trichloroethylene (TCE), an industrial solvent, in breas
61 odel for the destruction of (1) acetone, (2) trichloroethylene (TCE), and (3) polyethylene glycol (PE
62 c C-Cl bonds in 1,2-dichloroethane (DCA) and trichloroethylene (TCE), are completely inactive for red
63             Chlorinated solvents, especially trichloroethylene (TCE), are the most widespread groundw
64 thesis of this study was that metabolites of trichloroethylene (TCE), dichloroethylene (DCE) and rela
65  and dosed with equivalent concentrations of trichloroethylene (TCE).
66 sulfonate, I2S), and (iii) dechlorination of trichloroethylene (TCE).
67 creases its reactivity to pollutants such as trichloroethylene (TCE).
68 ts toluene, 1,1,1-trichloroethane (TCE), and trichloroethylene (TCY) affect ligand-gated ion channel
69 ene, xylenes), and chlorinated hydrocarbons (trichloroethylene, tetrachloroethylene, etc).
70 sing four common environmental contaminants (trichloroethylene, tetrachloroethylene, methyl tert-buty
71                                              Trichloroethylene, used extensively in industry and the
72      Small, volatile hydrocarbons, including trichloroethylene, vinyl chloride, carbon tetrachloride,
73       Complete dehalogenation of 20 mg L(-1) trichloroethylene was achieved within 1 h using 50 mg L(
74                                              Trichloroethylene was associated with scleroderma both b
75               In this work, the oxidation of trichloroethylene was studied with purified toluene 2-mo
76                        Neurotoxic actions of trichloroethylene were demonstrated in accompanying anim