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1 izations of cis-enediynes (see scheme; DCE = 1,2-dichloroethane).
2 ith BF3.Et2O and excess pyrrole in refluxing 1,2-dichloroethane.
3 basic solvents benzene, dichloromethane, and 1,2-dichloroethane.
6 both aerobic and anaerobic biodegradation of 1,2-dichloroethane (1,2-DCA) using five microbial cultur
7 tionation during anaerobic biodegradation of 1,2-dichloroethane (1,2-DCA) via dihaloelimination by De
8 actionation during aerobic biodegradation of 1,2-dichloroethane (1,2-DCA) via oxidative cleavage of a
9 ollutants under laboratory conditions, e.g., 1,2-dichloroethane, 1,2,3-trichloropropane and gamma-hex
11 on of other environmental pollutants such as 1,2-dichloroethane (72 years), paraoxon (13 months), atr
13 hancements were also obtained in the solvent 1,2-dichloroethane, although the analysis of the system
15 ransfer voltammetry at the interface between 1,2-dichloroethane and an aqueous buffer solution or und
16 conditions induced by osmocene dissolved in 1,2-dichloroethane and the subsequent water splitting by
17 that were made for 4-chlorotetrahydropyran, 1,2-dichloroethane, and benzyl alcohol have also confirm
19 methylsulfoxide, acetonitrile, nitromethane, 1,2-dichloroethane, and dichloromethane, carried out usi
22 s are uncompetitive inhibitors of XaDHL with 1, 2-dichloroethane as the varied substrate at pH 8.2 (C
23 uCl2(p-cymene)}2], AgSbF6, and (NH4)2S2O8 in 1,2-dichloroethane at 100 degrees C for 24 h to afford o
26 ydes in the presence of 30 mol % BF3.OEt2 in 1,2-dichloroethane at 80 degrees C affords a novel class
28 inetic tests revealed that dechlorination of 1,2-dichloroethane by the consortium was strongly inhibi
32 , has been used to elucidate the reaction of 1, 2-dichloroethane (DCE) with the carboxylate of Asp-12
33 S(N)2 displacement reaction of chloride from 1,2-dichloroethane (DCE) by nucleophilic attack of the c
34 phthalenesulfonate (DNNS) at polarized water/1,2-dichloroethane (DCE) interfaces, i.e., sDNNS(-) (DCE
35 ) dissolved in a tetrahydrofuran (THF) and a 1,2-dichloroethane (DCE) solution, respectively, using p
37 are reported in the current-time response of 1,2-dichloroethane(DCE)|water(W) submilli-interfaces aft
38 nors and 1,2,4,5-tetracyanobenzene (TCNB) in 1,2-dichloroethane (DCLE) exhibit a mirror image relatio
39 transformed to ethene, prolonged exposure to 1,2-dichloroethane diminished the vinyl chloride transfo
41 ly varying polarities: cyclohexane, toluene, 1,2-dichloroethane, ethyl acetate, acetone, acetonitrile
42 ur detectable reductive dehalogenases during 1,2-dichloroethane exposure, suggesting that it catalyze
45 1) Ru(bpy)(3)(2+) transfer through the water/1,2-dichloroethane interface and (2) electrodeposition o
48 resence of scandium or ytterbium triflate in 1,2-dichloroethane or a cosolvent mixture of 1/9 THF/dic
52 ned in good to excellent yield by stirring a 1,2-dichloroethane solution of the starting triazene wit
56 stereochemical memory effect in toluene and 1,2-dichloroethane, the reactions in these solvents can
60 served that increasing the influent ratio of 1,2-dichloroethane to trichloroethene was associated wit
61 (tetrachloromethane) and on TDIROF for 90% (1,2-dichloroethane) to 100% (trichloromethane) of what w
62 lytic amount of anhydrous FeCl3 in refluxing 1,2-dichloroethane underwent tandem Conia-ene and Friede
63 ased and subsequent exposure of the films to 1,2-dichloroethane vapor led to a significant increase i
64 emical extraction of rubidium at micro water|1,2-dichloroethane (w|DCE) and water|room-temperature io
69 tions across the interface between water and 1,2-dichloroethane were measured by steady-state voltamm
70 onger chained OCBPs (1,2-dichloropropane and 1,2-dichloroethane) were more frequently found on TDIROF
71 n tobacco resulting in the dehalogenation of 1,2-dichloroethane, which was otherwise recalcitrant.
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