ライフサイエンスコーパス: chloroform

1 its (e.g., DAN.DeUG, Kassoc = 10(8) M(-1) in chloroform).

2 lipidated peptides in organic solvent (e.g., chloroform).

3 med in the absence or presence of a solvent (chloroform).

4 ions were avoided in the less polar solvent (chloroform).

5 filled with nanoink (10 wt % of AgNPs-OA in chloroform).

6 ide, (alkyl=butyl, hexyl and octyl group) in chloroform.

7 l carbene C-H insertion into the C-H bond of chloroform.

8 ls when the data were acquired in deuterated chloroform.

9 ganglion (DRG) neurons that are activated by chloroform.

10 lamine, DBU, and dimethylphenylphosphine) in chloroform.

11 was extracted successively with n-hexane and chloroform.

12 ene blue (MB) and ca. 30 equiv of aspirin in chloroform.

13 at control the chlorine isotope signature of chloroform.

14 ed solvents, such as 1,2-dichlorobenzene and chloroform.

15 mportant role in the biosynthesis of natural chloroform.

16 eated with a 10-fold excess of NOBF4 salt in chloroform.

17 system does not act as a sink or a source of chloroform.

18 d brominated analogues were formed alongside chloroform.

19 ers in water, but merely di- or trimerize in chloroform.

20 in complexes with water, methanol, xenon or chloroform.

21 es were formed in the mixture of acetone and chloroform.

22 de counterions from an aqueous solution into chloroform.

23 ion, presented in the millimolar range, into chloroform.

24 found to be >20:1 with dimethyldioxirane in chloroform.

25 ith dithioerythritol, ethanol, and isooctane/chloroform.

26 e they are not extracted by rapid dipping in chloroform.

27 (5) M(-1), determined by UV-vis titration in 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 ation associated with alkaline hydrolysis of chloroform (-53 +/- 3 per thousand) and its independence

31 4, 2.8, 2.8, and 11% by cross-validation for chloroform (7 stocks), thionyl chloride (3 stocks), acet

32 The use of chloroform, a much less polar solvent, limits the impact

33 The environmental irritant chloroform, a naturally occurring small volatile organoh

34 ate that O-H...O hydrogen bonds in crystals, chloroform, acetone, and water have nearly identical len

35 The results revealed that chloroform activates DRG neurons via TRPV1 activation.

36 Furthermore, chloroform activates TRPV1, and it also activates TRPM8

37 al (TRP) channel family members in mediating chloroform activation and the molecular determinants of

38 l studies was carried out to investigate how chloroform acts as a hydrogen atom donor in Barton reduc

39 Chloroform acts as an effective hydrogen atom donor for

40 isphino)butane (dppb), and syngas (CO/H2) in chloroform/alcohol.

41 Resorcinol, a major precursor of chloroform, also formed di/trichloroacetonitrile, di/tri

42 ghly 0.5 kcal/mol to the helix stability (in chloroform), although their strength is sensitive to sub

43 low pH led to a more significant increase of chloroform and a more significant short-term increase of

44 which we quantified the biotic formation of chloroform and bromoform.

45 t as the chlorine doses increased, levels of chloroform and DCAA in the heated water increased signif

46 s was employed to compare abiotic and biotic chloroform and dichloromethane degradation.

47 methods with the IEF-PCM solvation model for chloroform and ethanol.

48 BDs with 15 different anions were studied in chloroform and in acetonitrile.

49 channel are also required for activation by chloroform and isoflurane.

50 Polar solvents such as chloroform and methanol increase the barrier to rotation

51 systems designed for CO2, CH4, and N2O emit chloroform and other volatile chlorinated compounds (VOC

52 A decane ether) (BA-C10) films prepared with chloroform and tetrahydrofuran as the solvents.

53 molecular basis of DRG neuron activation by chloroform and the opposing effects chloroform has on di

54 ome of the analytes showed high affinity for chloroform and the others were more efficiently extracte

55 4 THM in separate models, 4 THM in 1 model, chloroform and the sum of brominated THM in 1 model, and

56 In chloroform and THF solution the fluorescence maxima were

57 ted with the sources, transport, and fate of chloroform and three other trihalomethanes (THMs) in unt

58 the delta(37)Cl value of naturally produced chloroform and to better understand the reaction steps t

59 cted using a biphasic method, with methanol, chloroform and water as the solvents.

60 tional exposure of the nitrobenzene layer to chloroform and water gives 3 in its uncomplexed, ion-fre

61 of triethanolamine (TEA), thionyl chloride, chloroform, and acetone.

62 lly infectious, sensitive to extraction with chloroform, and circulate in the blood of infected human

63 ration by a factor of three upon addition of chloroform, and decrease another order of magnitude for

64 est performance using a mixture of n-hexane, chloroform, and dichloromethane (70 mL) for extraction.

65 oxidant activity, as compared to the hexane, chloroform, and n-butanol fractions, as well as the crud

66 polyphosphate extraction in water, methanol-chloroform, and phenol-chloroform followed by polyphosph

67 ground-based measurements of methane, methyl chloroform, and the C(13)/C(12) ratio in atmospheric met

68 them was observed to selectively encapsulate chloroform, and the other was observed to selectively en

69 1.56; 95% CI: 1.01, 2.43), as well as DBCM, chloroform, and THM4 (aOR range, 1.26-1.67).

70 The signal assignments (in deuterated chloroform) are thoroughly described, identifying for th

71 in methylcyclohexane (MCH) upon addition of chloroform as a good solvent is shown to proceed with a

72 The utility of chloroform as both a solvent and a hydrogen atom donor i

73 ion presented an optimal value for 600muL of chloroform as extraction solvent using acetonitrile as d

74 ed retentate with cold acetone and also with chloroform as precipitating reagents.

75 discovery that the use of ethanol-stabilized chloroform as solvent leads to the generation of alpha-e

76 o, and others on the reactivity of NHCs with chloroform as well as a simple organocatalytic method fo

77 At higher concentrations in chloroform, as well as in the solid state, tweezers 1 se

78 e complex as a catalyst and triethylamine in chloroform at -45 degrees C proceeded in a new type of a

79 The reaction in chloroform at 100 degrees C under Rh2(OAc)4 catalysis pr

80 re analyzed using a volatile solvent such as chloroform at elevated temperatures.

81 boroles form spontaneously at equilibrium in chloroform at room temperature.

82 cules, in a parallel stacked arrangement (in chloroform at room temperature; concentration 1 mM-0.1 m

83 The delta(13)C values of chloroform at the water table (-22.0 per thousand) corre

84 Using a simple chloroform-based extraction, useful spectra were obtaine

85 Using a simple chloroform-based extraction, we obtained classic low-fie

86 as obtained after protein precipitation with chloroform before different rinsing stages for removing

87 ltrafast infrared spectroscopy shows that in chloroform, beta-lactam is formed immediately after the

88 In a subsample (n = 230), air chloroform better predicted blood chloroform than water

89 Four THMs (bromoform, chloroform, bromodichloromethane, dibromochloromethane)

90 g bladder cancer risk associated with 4 THM (chloroform, bromodichloromethane, dibromochloromethane,

91 ls across the United States and analyzed for chloroform, bromodichloromethane, dibromochloromethane,

92 und that in the presence of hexane-buffer or chloroform-buffer interfaces LFAOs are able to associate

93 rominated THMs occurred less frequently than chloroform but more frequently in public-well samples th

94 st that SA exists predominately as dimers in chloroform, but in the other five solvents there is no c

95 een measured for tetraethylammonium salts in chloroform by employing a variation of Cram's extraction

96 Furthermore, the significant chloroform carbon isotopic fractionation associated with

97 non, sulfur hexafluoride, nitrous oxide, and chloroform cause rapid increases of different magnitude

98 Chloroform (CF) is a widespread groundwater contaminant

99 In the current study, biotic degradation of chloroform (CF) to dichloromethane (DCM) was carried out

100 characterization of PTB7 film formation from chloroform (CF), chlorobenzene (CB), and 1,2-dichloroben

101 Minor formation of chloroform (CF), the only chlorinated degradation produc

102 ation for the common groundwater contaminant chloroform (CF), this study investigated for the first t

103 ce the formation of toxic byproducts such as chloroform (CF).

104 adicals and is diagnosed by analyzing methyl chloroform (CH(3)CCl(3)) measurements.

105 etween the new EA methods and an established chloroform (CH) method was carried out on 24 cheese samp

106 AA at a pH of 13 (>pKa(2, AA) of 11.79) and chloroform (CHCl3) was a transformation byproduct of CCl

107 Their similar NMR spectra in chloroform clearly suggest the same 1,3-alternate geomet

108 When chloroform comes in contact with skin or is ingested, it

109 When the chloroform concentration in pentane is >/=5 ppm, the col

110 Chloroform concentrations in the heated water remained c

111 rized sampling probe that enables the use of chloroform-containing extraction solvents for efficient

112 d CsNO(3), in solution (10% methanol-d(4) in chloroform-d) as inferred from (1)H NMR spectroscopic an

113 of different polarities such as benzene-d6, chloroform-d, acetonitrile-d3, acetone-d6, methanol-d4,

114 m exchange reactions between pseudoacids and chloroform-d1, while the analogous saturated NHC 1,3-bis

115 ation of pseudoacids (pKa,DMSO = 14-19) with chloroform-d1.

116 he NH/SH ratio of OH with the help of methyl chloroform data (a proxy for OH concentrations) and an a

117 ility, which currently rely purely on methyl chloroform data and its uncertain emissions estimates.

118 missions and mean OH abundance to fit methyl chloroform data from two surface-measurement networks an

119 The resulting chloroform degradation after 28 days was 94, 96, 99, and

120 ere performed to evaluate the feasibility of chloroform degradation by alkaline hydrolysis and the po

121 allowed the calculation of the percentage of chloroform degradation in field-scale pilot experiments

122 A maximum of approximately 30-40% of chloroform degradation was achieved during the two studi

123 responded well to the delta(13)C of soil gas chloroform, demonstrating that the isotope signature of

124 tegorical DBP exposures including bromoform, chloroform, dibromochloromethane (DBCM), bromodichlorome

125 id extractions (i.e., methanol combined with chloroform, dichloromethane, and methyl-tert butyl ether

126 of soluble lipids can be extracted by rapid chloroform dipping of roots.

127 librium of 25 using (1)H NMR spectroscopy in chloroform, DMSO, and water demonstrated that the pyrrol

128 Chloroform emission from soil has been reported from div

129 constants were derived for the complexes in chloroform, especially for the divalent cation Mg(2+).

130 Crude chloroform, ethanol and acetone extracts of nineteen sea

131 es increasingly more difficult in the order: chloroform, ethyl acetate acetonitrile, acetone, methano

132 Extraction was performed with hexane, chloroform, ethyl acetate, methanol, and water.

133 he PBPK model successful reproduced observed chloroform exhaled air concentrations resulting from an

134 8) and betulinic acid (9) were isolated from chloroform extract by column chromatography over silica

135 In the oral glucose tolerance test, the chloroform extract exerted the highest response (33.3%),

136 An isoprenoid-containing chloroform extract of tomato fruit and most individual i

137 14-day administration in diabetic rats, the chloroform extract recorded the highest blood (23.5%) an

138 GC-MS analysis of the chloroform extract revealed high levels of linoleic acid

139 ing solvents: water extract>methanol extract>chloroform extract>and petroleum ether extracts.

140 ydroperoxide compounds in water-methanol and chloroform extracted phases.

141 shown to be catalyzed by both synthetic and chloroform-extracted phospholipid surfaces, it is instea

142 rus cultures of conventionally processed and chloroform-extracted stool samples, as well as conventio

143 Sheared chromatin is subjected to phenol/chloroform extraction and the isolated DNA, typically en

144 proposed on-line SPE was compared against a chloroform extraction from aqueous extracts.

145 crude yeast cell lysate compared to a phenol/chloroform extraction method.

146 The phenol-chloroform extraction of C. vulgaris followed by ethanol

147 200 muL of this extract along with 50 muL of chloroform (extraction solvent) and 10 muL of IBCF was r

148 750 muL acetonitrile (disperser) and 50 muL chloroform (extraction solvent) into a 5 mL aqueous hone

149 Optimum extraction conditions were: 200 muL chloroform (extraction solvent), 1.0 mL acetonitrile (di

150 n of nicotine and its metabolite cotinine in chloroform extracts.

151 the sterol content, support a model in which chloroform favors solvation of the phospholipids and a c

152 he isotope enrichment factor for the abiotic chloroform/Fe(0) reaction was large at -29.4 +/- 2.1 per

153 study describes a system designed to measure chloroform flux from terrestrial systems, providing a re

154 rences of approximately 50 ng m(-2) h(-1) in chloroform fluxes.

155 nic arsenic present in the acid medium using chloroform followed by back-extraction to acidic medium.

156 on in water, methanol-chloroform, and phenol-chloroform followed by polyphosphate purification by bin

157 In situ emissions of chloroform from soil in nine Arctic and subarctic ecosys

158 ,3-thiazol- and 1,3,4-thiadiazol-2-amines in chloroform gives a mixture of two regioisomeric binuclea

159 Chloroform has been for a long time considered only as a

160 mine, hydroxythiol, and dithiol compounds in chloroform has been investigated by (1)H NMR spectroscop

161 ation by chloroform and the opposing effects chloroform has on different TRP channel family members,

162 determined THMs individually; bromoform and chloroform have been successfully quantitated in 30 min

163 The competitive process took place in a chloroform-hexane 50% (V/V) mixture, while the subsequen

164 Fluxes of chloroform in a forest clear-cut on the east coast of Va

165 n film sensors have been developed to detect chloroform in aqueous and nonaqueous solutions.

166 The presence of chloroform in forest soil and groundwater has been widel

167 The frequent detection of chloroform in groundwater in absence of other contaminan

168 rther research is required, the treatment of chloroform in groundwater through the use of concrete-ba

169 ttle is known about the formation pathway of chloroform in soil.

170 nt, we measured field NO emissions, and used chloroform in the laboratory to reduce microbial activit

171 This is well below the solubility of chloroform in water (ca. 5,800 ppm).

172 though foldamer self-association in nonpolar chloroform increased with length, with a approximately 1

173 NMR studies on these peptides in chloroform indicated a left-handed 10/12-helix, while th

174 ) and Cl(-) concentrations, the formation of chloroform induces a smaller AKIE (1.005-1.006) likely a

175 Hg methylation assays following molybdate or chloroform inhibition (a specific inhibitor of the acety

176 o polymers with functional groups at a water-chloroform interface using microfluidic technology.

177 Back-extraction of parabens from chloroform into a 50mM sodium hydroxide solution within

178 s the median delta(37)Cl value of industrial chloroform is -3.0 per thousand, the present study sugge

179 Chloroform is an example of a halogenated organic compou

180 Generally, the isotope signature of chloroform is conserved also during longer range transpo

181 Here, we present evidence that chloroform is formed through the hydrolysis of trichloro

182 (-)-DMEBr, the phase transfer from water to chloroform is incomplete.

183 absence of other contaminants suggests that chloroform is likely produced naturally.

184 demonstrating that the isotope signature of chloroform is maintained during transport through the un

185 delta(13)C data support the hypothesis that chloroform is naturally formed in some forest soils.

186 mn, and then ligand-assisted extraction into chloroform is performed.

187 though not noted in the original paper, when chloroform is used to extract the acetone there is slow

188 the transport of CsOH through an intervening chloroform layer.

189 d white muscle extracts of aqueous polar and chloroform lipid phases were collected.

190 roceed with a minimum rate around a critical chloroform/MCH solvent ratio.

191 extracts obtained by maceration with hexane, chloroform, methanol, and ethanol were screened for thei

192 The lenses also underwent two separate 2:1 chloroform-methanol extractions.

193 were removed and underwent two separate 2:1 chloroform-methanol extractions.

194 The adsorbed lipids were extracted with chloroform-methanol, which underwent assay quantificatio

195 Extraction of MtbWL with chloroform-methanol-water (10:10:3) resulted in a polar

196 Gangliosides are extracted by chloroform-methanol-water mixture, where an upper aqueou

197 ete extraction of inner membrane lipids with chloroform-methanol-water, revealing that one-half of hy

198 edia containing 100% butanol or a mixture of chloroform/methanol (2:1, v/v) can be used to solubilise

199 Using saturated DT in chloroform/methanol (2:1, v/v), with 1% formic acid in t

200 extracted with n-hexane (Soxhlet method) and chloroform/methanol (Folch method) from coriander, caraw

201 Protein fractions were extracted with chloroform/methanol and analyzed with electrospray ioniz

202 ns, comparing two different solvent systems (chloroform/methanol and aqueous methanol) and six differ

203 The application of chloroform/methanol and three different food grade solve

204 Therefore, chloroform/methanol could be used to lower beany or gras

205 The c subunit was purified by chloroform/methanol extraction and determined to be 15.8

206 12, 11, and 10 kDa were first detected after chloroform/methanol extraction in the flow through of hy

207 pid was obtained from 10 g of F. novicida by chloroform/methanol extraction, followed by DEAE-cellulo

208 0.5 and 3 mum were obtained upon spraying a chloroform/methanol matrix solution.

209 e also used ammonium sulfate ((NH4)2SO4) and chloroform/methanol precipitation of heart effluents to

210 with desalting/delipidation of the sample by chloroform/methanol precipitation with extra water washi

211 Under the optimal temperature, chloroform/methanol showed the highest lipid removal (87

212 stard and coriander seed oils extracted with chloroform/methanol was higher than in their counterpart

213 In general, chloroform/methanol was the most effective in inactivati

214 f total fatty acids (TFA), was in the order: chloroform/methanol>ethanol>hexane>ethanol/hexane for bo

215 urations of exposure to extraction solvents (chloroform/methanol), physical disruption (homogenizatio

216 FAs) during 12, 24, 48, 72 and 96 h, in 2 mL chloroform: methanol mixture (2:1); (2) acid methylation

217 HPTLC plates using mobile phase consisted of chloroform:methanol:acetone:25% ammonium hydroxide (75:1

218 A mixture design revealed that the chloroform:methanol:water proportion of 15:59:26 was glo

219 -coated TLC plates, mobile phase composed of chloroform:methanol:water:25% ammonium hydroxide (70:30:

220 d DNA from the teeth using a modified phenol-chloroform method.

221 ggests that chlorine isotopic composition of chloroform might be used to discriminate industrial and

222 s, together with the fact that the number of chloroform molecules that are absorbed per phospholipid

223 32 total THM; n = 4,080 bromoform; n = 4,582 chloroform; n = 4,374 bromodichloromethane; n = 4,464 di

224 study show that hydrogen atom transfer from chloroform occurs directly under kinetic control and is

225 The addition of chloroform only impacted Hg methylation in biofilm cultu

226 n equilibrium of (a, a)/(e, e) conformers in chloroform or acetonitrile.

227 infused with one of two ionization reagents, chloroform or ammonium hydroxide, to aid in ionization.

228 methylformamide (DMF) compared with those in chloroform or dichloromethane (DCM).

229 p electrophysiology to assess the effects of chloroform or the VGA isoflurane on TRP channel activati

230 ate data analyses (PCA and OPLS-DA) of liver chloroform phase showed that high levels of sesamin affe

231 Sample volume - 3muL of chloroform phase was directly injected into the HPLC sys

232 um (A336(+)) salt) from aqueous media into a chloroform phase with significantly improved efficiency

233 ly transferred from the aqueous phase to the chloroform phase, is proposed as titration end point.

234 eral hundred attoliters in volume and a bulk chloroform phase.

235 ely back-extraction of the analytes into the chloroform phase.

236 s, after which an immiscible organic (phenol-chloroform) phase was introduced in a headspace channel

237 The point at which the aqueous and chloroform phases appear equally blue is called Epton's

238 During APCI in negative ion mode, chloroform produces chloride anions that are known to re

239 eported time-dependent air concentrations of chloroform released during showering and of 2-butyoxyeth

240 molecular basis for the pain associated with chloroform remains unknown.

241 t -29.4 +/- 2.1 per thousand, while that for chloroform respiration by Dehalobacter was minimal at -4

242 traints obtained for alpha/gamma-peptides in chloroform reveal that AMCP-containing oligomers are con

243 respectively, and 0% for a validation set of chloroform samples.

244 Differently, NCs in hexane or chloroform self-assemble into only a single bcc superlat

245 r thousand, the delta(37)Cl value of natural chloroform should vary between -5 per thousand and -8 pe

246 nts that were carried out in the presence of chloroform showed a leveling effect, where moderate ster

247 ments and Raman spectra have also shown that chloroform significantly loosens both cholesterol-poor a

248 ns D-K (4-11), were isolated from the active chloroform-soluble extract of the root bark of Sphenosty

249 diate is stable for a period of ~20 hours in chloroform solution at 0 degrees C, allowing for an expl

250 ins that vary in length and base sequence in chloroform solution by means of femtosecond time-resolve

251 air oxidation both in the solid state and in chloroform solution is described.

252 tion of DABCO to the porphyrin macrocycle in chloroform solution leads to the formation of a stable 2

253 Reaction of a chloroform solution of 7 with an alkene in the presence

254 mice were quickly extracted with a methanol/chloroform solution, and the crude extract was directly

255 In aqueous chloroform solution, reaction in the sol-gel sensor film

256 stacking balances and 21 control balances in chloroform solution.

257 tyric acid methyl ester ([70]PCBM) cast from chloroform solution.

258 pplements preparations (capsules,tablets) to chloroform solution.

259 as a receptor for the pyrophosphate anion in chloroform solution.

260 gold surfaces with dilute tetrahydrofuran or chloroform solutions of tetraalkylstannanes (alkyl = met

261 Specifically, the chloroform solvent molecules are very ordered around the

262 rth 5.45 and 3.08 kcal/mol, respectively (in chloroform solvent).

263 In chloroform solvent, hydrogen-bonding to anions is accomp

264 ted of ethanol, acetone, dichloromethane and chloroform solvents and their binary, ternary and quater

265 ons of impurities unique to specific TEA and chloroform stocks, and thus indicative of their use, wer

266 better predicted blood chloroform than water chloroform, suggesting showering/bathing was a more impo

267 In chloroform supplemented with AgTFA, trifluoroacetate-ter

268 5 vol %, trichloroethene (TCE) 45 vol %, and chloroform (TCM) 10 vol %).

269 Blood SigmaTHM [sum of chloroform (TCM), bromodichloromethane (BDCM), dibromo-c

270 230), air chloroform better predicted blood chloroform than water chloroform, suggesting showering/b

271 comprising an amphiphilic imine dissolved in chloroform that catalyses its own formation by bringing

272 icts an annual mean NH-SH gradient of methyl chloroform that is a tight linear function of the modell

273 These two receptors also solubilize into chloroform the otherwise insoluble sulfate salt, (TMA)2S

274 A switch of the processing solvent from chloroform to 2-MeTHF leads to no negative impacts on th

275 roacetyl compounds in soil to the release of chloroform to the atmosphere varied between 1 and 116 ac

276 e a variety of oil-water mixtures, including chloroform, toluene, kerosene and other contaminations.

277 Chloroform transformation and dichloromethane formation

278 amatically depending on whether samples were chloroform treated or filtered to remove microbial conta

279 NO emission pulses were up to 19x greater in chloroform-treated soils than in the controls, and these

280 Chloroform (trichloromethane) was the primary THMs prese

281 As dilute solutions in chloroform, tweezers 1 displays both pyrene monomer and

282 ,2-dicarboxylate monoanion was determined in chloroform using the NMR method of isotopic perturbation

283 lies of P3BHT was greatly improved following chloroform vapor annealing, resulting in a fourfold incr

284 e DNA extraction method based on CTAB-phenol-chloroform was best for walnut.

285 Using an assessment level of 0.02 mug/L, chloroform was detected in 36.5% of public-well samples

286 Compound-specific isotope analysis of chloroform was performed on soil-gas and groundwater sam

287 e DNA extraction method based on CTAB-phenol-chloroform was the best for hazelnut.

288 osen for the extraction of the compounds and chloroform was used at the preconcentration stage.

289 and their light-triggered organization at a chloroform-water interface.

290 A high separation efficiency up to 98.5% for chloroform-water mixture was achieved when used for grav

291 es of metabolites, a combination of methanol/chloroform/water and methanol/water being the extraction

292 The sedimented organic phase (chloroform) were analysed directly by GC-IT/MS or evapor

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