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1 rusion method with 1, 3, and 5% w/v (PBAT to chloroform).
2 its (e.g., DAN.DeUG, Kassoc = 10(8) M(-1) in chloroform).
3 lipidated peptides in organic solvent (e.g., chloroform).
4 ger aggregates (in 80% methylcyclohexane/20% chloroform).
5 ions were avoided in the less polar solvent (chloroform).
6  filled with nanoink (10 wt % of AgNPs-OA in chloroform).
7 nd accompanied by a photochemical process in chloroform.
8 ing and often employs toxic solvents such as chloroform.
9 ith dithioerythritol, ethanol, and isooctane/chloroform.
10 e they are not extracted by rapid dipping in chloroform.
11 (5) M(-1), determined by UV-vis titration in chloroform.
12  GEO12CF that tolerated 83 muM (10 mg.L(-1)) chloroform.
13 l carbene C-H insertion into the C-H bond of chloroform.
14 ls when the data were acquired in deuterated chloroform.
15 ganglion (DRG) neurons that are activated by chloroform.
16 was extracted successively with n-hexane and chloroform.
17 ene blue (MB) and ca. 30 equiv of aspirin in chloroform.
18 oroethene to ethene in 14 muM (1.6 mg.L(-1)) chloroform.
19 at control the chlorine isotope signature of chloroform.
20 mportant role in the biosynthesis of natural chloroform.
21 eated with a 10-fold excess of NOBF4 salt in chloroform.
22 system does not act as a sink or a source of chloroform.
23 s (VOCs), such as formaldehyde, benzene, and chloroform.
24 ide, (alkyl=butyl, hexyl and octyl group) in chloroform.
25 lamine, DBU, and dimethylphenylphosphine) in chloroform.
26 ed solvents, such as 1,2-dichlorobenzene and chloroform.
27 d brominated analogues were formed alongside chloroform.
28                     The delta(13)C values of chloroform (-22.8 to -26.2 per thousand) present in soil
29 ore enriched in (13)C compared to industrial chloroform (-43.2 to -63.6 per thousand).
30         Transcriptional analyses showed that chloroform (45 muM; 5.3 mg.L(-1)) in culture GEO12CF enh
31 rease of vcrA transcripts in the presence of chloroform (45 muM; 5.3 mg.L(-1)) in culture GEO12CF was
32 ation associated with alkaline hydrolysis of chloroform (-53 +/- 3 per thousand) and its independence
33 4, 2.8, 2.8, and 11% by cross-validation for chloroform (7 stocks), thionyl chloride (3 stocks), acet
34 m 435 and a binary solvent system of toluene/chloroform 9:1 (v/v) were found to be the most suitable
35                                   The use of chloroform, a much less polar solvent, limits the impact
36                   The environmental irritant chloroform, a naturally occurring small volatile organoh
37 ate that O-H...O hydrogen bonds in crystals, chloroform, acetone, and water have nearly identical len
38 on, followed by extraction with LESA using a chloroform-acetonitrile-water (49:49:2) mixture and dire
39                    The results revealed that chloroform activates DRG neurons via TRPV1 activation.
40                                 Furthermore, chloroform activates TRPV1, and it also activates TRPM8
41 al (TRP) channel family members in mediating chloroform activation and the molecular determinants of
42 l studies was carried out to investigate how chloroform acts as a hydrogen atom donor in Barton reduc
43                                              Chloroform acts as an effective hydrogen atom donor for
44                                          The chloroform-adapted culture GEO12CF provides insights int
45 isphino)butane (dppb), and syngas (CO/H2) in chloroform/alcohol.
46             Resorcinol, a major precursor of chloroform, also formed di/trichloroacetonitrile, di/tri
47 ghly 0.5 kcal/mol to the helix stability (in chloroform), although their strength is sensitive to sub
48 d by spin coating a 10 wt% solution of F8 in chloroform and 10:1 wt% solution of F8:CdSe QDs, respect
49 low pH led to a more significant increase of chloroform and a more significant short-term increase of
50 The closed forms of the dyes were soluble in chloroform and acetonitrile.
51 was associated with elevated blood levels of chloroform and BDCM.
52 and, may well be considered unacceptable for chloroform and benzene (upper IUR) and for the combinati
53  which we quantified the biotic formation of chloroform and bromoform.
54                           Cocontamination by chloroform and chloroethenes often confounds bioremediat
55                  The EtSeCN was extracted in chloroform and could be detected in electron ionization
56 t as the chlorine doses increased, levels of chloroform and DCAA in the heated water increased signif
57 s was employed to compare abiotic and biotic chloroform and dichloromethane degradation.
58 methods with the IEF-PCM solvation model for chloroform and ethanol.
59 BDs with 15 different anions were studied in chloroform and in acetonitrile.
60       Here we show that inhaled anesthetics (chloroform and isoflurane) activate TREK-1 through disru
61  channel are also required for activation by chloroform and isoflurane.
62 ene oxide and 3% (w v(-1)) AE solubilized in chloroform and methanol (3:1).
63  systems designed for CO2, CH4, and N2O emit chloroform and other volatile chlorinated compounds (VOC
64 1H NMR spectra of synthetic 26 in deuterated chloroform and pyridine were identical to those of authe
65  molecular basis of DRG neuron activation by chloroform and the opposing effects chloroform has on di
66 ome of the analytes showed high affinity for chloroform and the others were more efficiently extracte
67  4 THM in separate models, 4 THM in 1 model, chloroform and the sum of brominated THM in 1 model, and
68                                           In chloroform and THF solution the fluorescence maxima were
69  the delta(37)Cl value of naturally produced chloroform and to better understand the reaction steps t
70 cted using a biphasic method, with methanol, chloroform and water as the solvents.
71 amer pai-stack (in 75% methylcyclohexane/25% chloroform) and a subsequent self-assembly of pentamer 1
72 onformations in both low-dielectric solvent (chloroform) and high-dielectric solvent (DMSO) to experi
73  of triethanolamine (TEA), thionyl chloride, chloroform, and acetone.
74 ene, toluene, ethylbenzene, hexane, pentane, chloroform, and carbon tetrachloride.
75 lly infectious, sensitive to extraction with chloroform, and circulate in the blood of infected human
76 est performance using a mixture of n-hexane, chloroform, and dichloromethane (70 mL) for extraction.
77 oxidant activity, as compared to the hexane, chloroform, and n-butanol fractions, as well as the crud
78  polyphosphate extraction in water, methanol-chloroform, and phenol-chloroform followed by polyphosph
79 ground-based measurements of methane, methyl chloroform, and the C(13)/C(12) ratio in atmospheric met
80 them was observed to selectively encapsulate chloroform, and the other was observed to selectively en
81  1.56; 95% CI: 1.01, 2.43), as well as DBCM, chloroform, and THM4 (aOR range, 1.26-1.67).
82        The signal assignments (in deuterated chloroform) are thoroughly described, identifying for th
83  shell featuring two clearly distinguishable chloroform arrangements that undergo chemical exchange w
84  1,3,5-tris(pyren-2-yl)adamantane containing chloroform as a guest are also presented.
85                               The utility of chloroform as both a solvent and a hydrogen atom donor i
86 ion presented an optimal value for 600muL of chloroform as extraction solvent using acetonitrile as d
87 ed retentate with cold acetone and also with chloroform as precipitating reagents.
88 discovery that the use of ethanol-stabilized chloroform as solvent leads to the generation of alpha-e
89 o, and others on the reactivity of NHCs with chloroform as well as a simple organocatalytic method fo
90                  At higher concentrations in chloroform, as well as in the solid state, tweezers 1 se
91 e complex as a catalyst and triethylamine in chloroform at -45 degrees C proceeded in a new type of a
92                              The reaction in chloroform at 100 degrees C under Rh2(OAc)4 catalysis pr
93 re analyzed using a volatile solvent such as chloroform at elevated temperatures.
94 iolates to diethyl acetylenedicarboxylate in chloroform at room temperature affords solely the meso d
95 boroles form spontaneously at equilibrium in chloroform at room temperature.
96 cules, in a parallel stacked arrangement (in chloroform at room temperature; concentration 1 mM-0.1 m
97                               Using a simple chloroform-based extraction, useful spectra were obtaine
98                               Using a simple chloroform-based extraction, we obtained classic low-fie
99 as obtained after protein precipitation with chloroform before different rinsing stages for removing
100 nzene (upper IUR) and for the combination of chloroform, benzene, and carbon tetrachloride.
101                In a subsample (n = 230), air chloroform better predicted blood chloroform than water
102                        Four THMs (bromoform, chloroform, bromodichloromethane, dibromochloromethane)
103 g bladder cancer risk associated with 4 THM (chloroform, bromodichloromethane, dibromochloromethane,
104 st that SA exists predominately as dimers in chloroform, but in the other five solvents there is no c
105 een measured for tetraethylammonium salts in chloroform by employing a variation of Cram's extraction
106 t reveal the presence of H bonds between the chloroform C-H group and an amide carbonyl oxygen atom i
107                 Furthermore, the significant chloroform carbon isotopic fractionation associated with
108 non, sulfur hexafluoride, nitrous oxide, and chloroform cause rapid increases of different magnitude
109  PBAT concentrations dissolved in deuterated chloroform (CDCl(3)), demonstrating accurate quantitatio
110                                              Chloroform (CF) is a widespread groundwater contaminant
111 characterization of PTB7 film formation from chloroform (CF), chlorobenzene (CB), and 1,2-dichloroben
112 ation for the common groundwater contaminant chloroform (CF), this study investigated for the first t
113 ce the formation of toxic byproducts such as chloroform (CF).
114 etween the new EA methods and an established chloroform (CH) method was carried out on 24 cheese samp
115  increased PBAT extraction efficiencies into chloroform (CHCl(3)) with methanol (MeOH) as cosolvent,
116 e (CH(2)Cl(2)), perchloroethene (C(2)Cl(4)), chloroform (CHCl(3)), and methyl chloride (CH(3)Cl), are
117  AA at a pH of 13 (>pKa(2, AA) of 11.79) and chloroform (CHCl3) was a transformation byproduct of CCl
118                 Their similar NMR spectra in chloroform clearly suggest the same 1,3-alternate geomet
119                                         When chloroform comes in contact with skin or is ingested, it
120 tocols are provided for the synthesis of the chloroform-compatible poly(methyl methacrylate) and dime
121                                     The same chloroform concentration effectively inhibited dechlorin
122                                     When the chloroform concentration in pentane is >/=5 ppm, the col
123                                              Chloroform concentrations in the heated water remained c
124 rized sampling probe that enables the use of chloroform-containing extraction solvents for efficient
125 f cyclohexene-1,2-dicarboxylate monoanion in chloroform-d and on the (19)F NMR chemical shifts of dif
126  of different polarities such as benzene-d6, chloroform-d, acetonitrile-d3, acetone-d6, methanol-d4,
127 m exchange reactions between pseudoacids and chloroform-d1, while the analogous saturated NHC 1,3-bis
128 ation of pseudoacids (pKa,DMSO = 14-19) with chloroform-d1.
129 he NH/SH ratio of OH with the help of methyl chloroform data (a proxy for OH concentrations) and an a
130 ility, which currently rely purely on methyl chloroform data and its uncertain emissions estimates.
131 missions and mean OH abundance to fit methyl chloroform data from two surface-measurement networks an
132                                The resulting chloroform degradation after 28 days was 94, 96, 99, and
133 ere performed to evaluate the feasibility of chloroform degradation by alkaline hydrolysis and the po
134 allowed the calculation of the percentage of chloroform degradation in field-scale pilot experiments
135         A maximum of approximately 30-40% of chloroform degradation was achieved during the two studi
136 tegorical DBP exposures including bromoform, chloroform, dibromochloromethane (DBCM), bromodichlorome
137 id extractions (i.e., methanol combined with chloroform, dichloromethane, and methyl-tert butyl ether
138                                   In a 1:100 chloroform dilution, the presence of the plasma was negl
139  of soluble lipids can be extracted by rapid chloroform dipping of roots.
140                                              Chloroform emission from soil has been reported from div
141                                        Crude chloroform, ethanol and acetone extracts of nineteen sea
142 es increasingly more difficult in the order: chloroform, ethyl acetate acetonitrile, acetone, methano
143        Extraction was performed with hexane, chloroform, ethyl acetate, methanol, and water.
144 he PBPK model successful reproduced observed chloroform exhaled air concentrations resulting from an
145 8) and betulinic acid (9) were isolated from chloroform extract by column chromatography over silica
146      In the oral glucose tolerance test, the chloroform extract exerted the highest response (33.3%),
147 st levels of total saponins were observed in chloroform extract of the Chinese bitter melon pericarp
148  14-day administration in diabetic rats, the chloroform extract recorded the highest blood (23.5%) an
149                        GC-MS analysis of the chloroform extract revealed high levels of linoleic acid
150 ing solvents: water extract>methanol extract>chloroform extract>and petroleum ether extracts.
151 ydroperoxide compounds in water-methanol and chloroform extracted phases.
152  shown to be catalyzed by both synthetic and chloroform-extracted phospholipid surfaces, it is instea
153 to achieve the optimal conditions: 300 uL of chloroform (extracting solvent), 1500 uL of acetonitrile
154  proposed on-line SPE was compared against a chloroform extraction from aqueous extracts.
155 antities of DNA (p < 0.001), with the phenol-chloroform extraction method producing the highest total
156 crude yeast cell lysate compared to a phenol/chloroform extraction method.
157                                   The phenol-chloroform extraction of C. vulgaris followed by ethanol
158 200 muL of this extract along with 50 muL of chloroform (extraction solvent) and 10 muL of IBCF was r
159  Optimum extraction conditions were: 200 muL chloroform (extraction solvent), 1.0 mL acetonitrile (di
160 n of nicotine and its metabolite cotinine in chloroform extracts.
161 he isotope enrichment factor for the abiotic chloroform/Fe(0) reaction was large at -29.4 +/- 2.1 per
162 study describes a system designed to measure chloroform flux from terrestrial systems, providing a re
163 rences of approximately 50 ng m(-2) h(-1) in chloroform fluxes.
164 nic arsenic present in the acid medium using chloroform followed by back-extraction to acidic medium.
165 on in water, methanol-chloroform, and phenol-chloroform followed by polyphosphate purification by bin
166 ng two immiscible solvents such as water and chloroform for extraction.
167                         In situ emissions of chloroform from soil in nine Arctic and subarctic ecosys
168 ,3-thiazol- and 1,3,4-thiadiazol-2-amines in chloroform gives a mixture of two regioisomeric binuclea
169 rocess (GLE-S) or dechlorophyllization using chloroform (GLE-Ch) were prepared.
170 mine, hydroxythiol, and dithiol compounds in chloroform has been investigated by (1)H NMR spectroscop
171 ation by chloroform and the opposing effects chloroform has on different TRP channel family members,
172      The competitive process took place in a chloroform-hexane 50% (V/V) mixture, while the subsequen
173                                    Fluxes of chloroform in a forest clear-cut on the east coast of Va
174 n film sensors have been developed to detect chloroform in aqueous and nonaqueous solutions.
175                    The frequent detection of chloroform in groundwater in absence of other contaminan
176 rther research is required, the treatment of chloroform in groundwater through the use of concrete-ba
177 ttle is known about the formation pathway of chloroform in soil.
178 nt, we measured field NO emissions, and used chloroform in the laboratory to reduce microbial activit
179         This is well below the solubility of chloroform in water (ca. 5,800 ppm).
180 though foldamer self-association in nonpolar chloroform increased with length, with a approximately 1
181             NMR studies on these peptides in chloroform indicated a left-handed 10/12-helix, while th
182 ) and Cl(-) concentrations, the formation of chloroform induces a smaller AKIE (1.005-1.006) likely a
183 Hg methylation assays following molybdate or chloroform inhibition (a specific inhibitor of the acety
184 ts suggest that culture GEO12CF may overcome chloroform inhibition by rdh upregulation.
185 o polymers with functional groups at a water-chloroform interface using microfluidic technology.
186             Back-extraction of parabens from chloroform into a 50mM sodium hydroxide solution within
187 s the median delta(37)Cl value of industrial chloroform is -3.0 per thousand, the present study sugge
188 ed to fight chloroethene contamination where chloroform is a cocontaminant.
189                                              Chloroform is an example of a halogenated organic compou
190               Here, we present evidence that chloroform is formed through the hydrolysis of trichloro
191  (-)-DMEBr, the phase transfer from water to chloroform is incomplete.
192  absence of other contaminants suggests that chloroform is likely produced naturally.
193              Inhibition of dehalogenation by chloroform is often seen in Dehalococcoides, but the mec
194    We combined four filters in a 5 mL Phenol-Chloroform-Isoamyl (PCI) procedure to allow for larger v
195                 General anesthetics, such as chloroform, isoflurane, diethyl ether, xenon, and propof
196 d and used to extract F(-) from water into a chloroform layer with high efficiency.
197 the transport of CsOH through an intervening chloroform layer.
198 strain GEO12 in increasing concentrations of chloroform led to culture GEO12CF that tolerated 83 muM
199                                 Median blood chloroform levels (25th-75th percentiles) were 16.2 (9.1
200 d white muscle extracts of aqueous polar and chloroform lipid phases were collected.
201 extracts obtained by maceration with hexane, chloroform, methanol, and ethanol were screened for thei
202 ere extracted from frozen sperm in 1:2 (v/v) chloroform-methanol solvent, fractionated into neutral a
203                     Extraction of MtbWL with chloroform-methanol-water (10:10:3) resulted in a polar
204                Gangliosides are extracted by chloroform-methanol-water mixture, where an upper aqueou
205 ete extraction of inner membrane lipids with chloroform-methanol-water, revealing that one-half of hy
206 edia containing 100% butanol or a mixture of chloroform/methanol (2:1, v/v) can be used to solubilise
207  a complex environment - comprising urea and chloroform/methanol (CHCl(3)/MeOH) mixture.
208 extracted with n-hexane (Soxhlet method) and chloroform/methanol (Folch method) from coriander, caraw
209                           The application of chloroform/methanol and three different food grade solve
210                                   Therefore, chloroform/methanol could be used to lower beany or gras
211 12, 11, and 10 kDa were first detected after chloroform/methanol extraction in the flow through of hy
212  0.5 and 3 mum were obtained upon spraying a chloroform/methanol matrix solution.
213 e also used ammonium sulfate ((NH4)2SO4) and chloroform/methanol precipitation of heart effluents to
214 with desalting/delipidation of the sample by chloroform/methanol precipitation with extra water washi
215               Under the optimal temperature, chloroform/methanol showed the highest lipid removal (87
216  led to the identification of CM inhibitors (chloroform/methanol soluble proteins) as main contributo
217 stard and coriander seed oils extracted with chloroform/methanol was higher than in their counterpart
218                                  In general, chloroform/methanol was the most effective in inactivati
219 f total fatty acids (TFA), was in the order: chloroform/methanol>ethanol>hexane>ethanol/hexane for bo
220 urations of exposure to extraction solvents (chloroform/methanol), physical disruption (homogenizatio
221 FAs) during 12, 24, 48, 72 and 96 h, in 2 mL chloroform: methanol mixture (2:1); (2) acid methylation
222 HPTLC plates using mobile phase consisted of chloroform:methanol:acetone:25% ammonium hydroxide (75:1
223 -coated TLC plates, mobile phase composed of chloroform:methanol:water:25% ammonium hydroxide (70:30:
224 o RNA extraction using a conventional phenol-chloroform method, the LMJ-based method provided a 3-fol
225 d DNA from the teeth using a modified phenol-chloroform method.
226 ggests that chlorine isotopic composition of chloroform might be used to discriminate industrial and
227 wo distinct solvation shells formed by three chloroform molecules, where one thermally undergoes hydr
228 32 total THM; n = 4,080 bromoform; n = 4,582 chloroform; n = 4,374 bromodichloromethane; n = 4,464 di
229  study show that hydrogen atom transfer from chloroform occurs directly under kinetic control and is
230                              The addition of chloroform only impacted Hg methylation in biofilm cultu
231 plant cell walls in organic solvents such as chloroform or acetonitrile, which can then be analyzed b
232 infused with one of two ionization reagents, chloroform or ammonium hydroxide, to aid in ionization.
233 methylformamide (DMF) compared with those in chloroform or dichloromethane (DCM).
234 p electrophysiology to assess the effects of chloroform or the VGA isoflurane on TRP channel activati
235 ate data analyses (PCA and OPLS-DA) of liver chloroform phase showed that high levels of sesamin affe
236                      Sample volume - 3muL of chloroform phase was directly injected into the HPLC sys
237 um (A336(+)) salt) from aqueous media into a chloroform phase with significantly improved efficiency
238 ly transferred from the aqueous phase to the chloroform phase, is proposed as titration end point.
239 ely back-extraction of the analytes into the chloroform phase.
240 s, after which an immiscible organic (phenol-chloroform) phase was introduced in a headspace channel
241           The point at which the aqueous and chloroform phases appear equally blue is called Epton's
242  fluorescent switching behaviors in toluene, chloroform, poly(methyl methacrylate) (PMMA) film, and p
243 ished a protocol for AAV production based on chloroform-precipitation, which allows for fast in-house
244            During APCI in negative ion mode, chloroform produces chloride anions that are known to re
245 eported time-dependent air concentrations of chloroform released during showering and of 2-butyoxyeth
246 molecular basis for the pain associated with chloroform remains unknown.
247 t -29.4 +/- 2.1 per thousand, while that for chloroform respiration by Dehalobacter was minimal at -4
248 ystem of immiscible solvents (here water and chloroform) results in a 3D constitutional dynamic netwo
249 traints obtained for alpha/gamma-peptides in chloroform reveal that AMCP-containing oligomers are con
250 respectively, and 0% for a validation set of chloroform samples.
251                Differently, NCs in hexane or chloroform self-assemble into only a single bcc superlat
252 r thousand, the delta(37)Cl value of natural chloroform should vary between -5 per thousand and -8 pe
253 ns D-K (4-11), were isolated from the active chloroform-soluble extract of the root bark of Sphenosty
254 diate is stable for a period of ~20 hours in chloroform solution at 0 degrees C, allowing for an expl
255 ins that vary in length and base sequence in chloroform solution by means of femtosecond time-resolve
256 tion of DABCO to the porphyrin macrocycle in chloroform solution leads to the formation of a stable 2
257                                   In aqueous chloroform solution, reaction in the sol-gel sensor film
258 stacking balances and 21 control balances in chloroform solution.
259 tyric acid methyl ester ([70]PCBM) cast from chloroform solution.
260 pplements preparations (capsules,tablets) to chloroform solution.
261 rocycle for 11 different Q(+).Cl(-) salts in chloroform solution.
262 gold surfaces with dilute tetrahydrofuran or chloroform solutions of tetraalkylstannanes (alkyl = met
263                            Specifically, the chloroform solvent molecules are very ordered around the
264 rth 5.45 and 3.08 kcal/mol, respectively (in chloroform solvent).
265 ted of ethanol, acetone, dichloromethane and chloroform solvents and their binary, ternary and quater
266 ons of impurities unique to specific TEA and chloroform stocks, and thus indicative of their use, wer
267 better predicted blood chloroform than water chloroform, suggesting showering/bathing was a more impo
268                                           In chloroform supplemented with AgTFA, trifluoroacetate-ter
269 5 vol %, trichloroethene (TCE) 45 vol %, and chloroform (TCM) 10 vol %).
270 ed for biomarkers of trihalomethanes (THMs): chloroform (TCM), bromodichloromethane, dibromochloromet
271  230), air chloroform better predicted blood chloroform than water chloroform, suggesting showering/b
272 comprising an amphiphilic imine dissolved in chloroform that catalyses its own formation by bringing
273 icts an annual mean NH-SH gradient of methyl chloroform that is a tight linear function of the modell
274     These two receptors also solubilize into chloroform the otherwise insoluble sulfate salt, (TMA)2S
275      A switch of the processing solvent from chloroform to 2-MeTHF leads to no negative impacts on th
276 ent detoxifying activity against benzene and chloroform to suggest that biofilters using transgenic p
277 roacetyl compounds in soil to the release of chloroform to the atmosphere varied between 1 and 116 ac
278 e a variety of oil-water mixtures, including chloroform, toluene, kerosene and other contaminations.
279                                              Chloroform transformation and dichloromethane formation
280 NO emission pulses were up to 19x greater in chloroform-treated soils than in the controls, and these
281                                              Chloroform (trichloromethane) was the primary THMs prese
282                       As dilute solutions in chloroform, tweezers 1 displays both pyrene monomer and
283 folded monomeric and dimeric MC subunits (in chloroform) up to the full pentamer pai-stack (in 75% me
284 ,2-dicarboxylate monoanion was determined in chloroform using the NMR method of isotopic perturbation
285 lies of P3BHT was greatly improved following chloroform vapor annealing, resulting in a fourfold incr
286 e DNA extraction method based on CTAB-phenol-chloroform was best for walnut.
287     Using an assessment level of 0.02 mug/L, chloroform was detected in 36.5% of public-well samples
288 e DNA extraction method based on CTAB-phenol-chloroform was the best for hazelnut.
289 osen for the extraction of the compounds and chloroform was used at the preconcentration stage.
290  and their light-triggered organization at a chloroform-water interface.
291 A high separation efficiency up to 98.5% for chloroform-water mixture was achieved when used for grav
292 tion solvents consisting of 10% methanol and chloroform were evaluated under dynamic and static extra
293 DFT calculations (GIAO/B3LYP/6-31G(d,p)/PCM, chloroform), were readily applied to these structures, p
294 arly relevant for authorities' regulation of chloroform which in the case of Denmark was very strict
295 annel (ELIC) in complex with a derivative of chloroform, which reveals important features of anesthet
296 ically inert cyclic tetramers is observed in chloroform, while in toluene an equilibrium between tetr
297 amples of food supplements were dissolved in chloroform with help of saponification with 1M solution
298 ows the crystal to take up 2.5 mmol g(-1) of chloroform with high adsorption selectivity (CHCl3 /EA >
299                       In dichloromethane and chloroform without an additive the 2,7-diamino-3,6-dibro
300 material in organic solvents such as THF and chloroform yields sheet- and belt-like nanostructures wi

 
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