ライフサイエンスコーパス: chlorinate

1 tachlorophenol (PCP), but rather by the less chlorinated 2,3,5,6-tetrachlorophenol (2,3,5,6-TeCP), on

2 ith amino acid and eventual formation of the chlorinating agent in the form of the hydrochloride salt

3 it is not possible to preclude H2OCl(+) as a chlorinating agent, we were able to model our low-pH dat

4 l lineC bond as well hydrogen bonding to the chlorinating agent.

5 sium acyltrifluoroborates promoted by simple chlorinating agents that proceeds rapidly in water.

6 importance of different chlorine species as chlorinating agents.

7 remediation of groundwater contaminated with chlorinated aliphatic hydrocarbons such as perchloroethe

8 orm FeS, suggesting that, after oxidation by chlorinated aliphatics, FeS can be regenerated by additi

9 apid disinfection of the hospital WDS with a chlorinated, alkaline detergent and subsequent superchlo

10 SCCPs are complex mixtures of chlorinated alkanes with variable chain length and chlor

11 ancomycin, exclusive conversion of vicinally chlorinated alkanes, and tolerance to short-term oxygen

12 the presence of degradation products such as chlorinated alkenes (CP-enes).

13 moved toward alterative compounds including chlorinated alkyl and nonchlorinated aryl organophosphat

14 ions, N-chlorination and dechlorination of N-chlorinated amide links by hydroxyl ion are the two domi

15 ssion as a result of the hydrolysis of the N-chlorinated amidic N-C bond due to nucleophilic attack b

16 ally more cytotoxic and genotoxic than their chlorinated analogs.

17 Br-DBPs are generally more toxic than their chlorinated analogues.

18 For chlorinated and brominated aromatics, nucleophilic addit

19 The chlorinated and brominated byproduct concentration may b

20 Chlorinated and brominated standards and isotopically la

21 ce on calibration was not as significant for chlorinated and brominated substances as observed for hu

22 end=0.13; the ORs at the 95th percentile for chlorinated and brominated THMs were 1.77 (95% CI: 1.05,

23 xtracting nonvolatile and volatile DBPs from chlorinated and chloraminated drinking water to minimize

24 o experiments, this precursor is furthermore chlorinated and cyclized to merochlorin A and isomeric m

25 etermine second-order rate constants for the chlorinated and iodinated oxidants.

26 CNs), polychlorinated dibenzofurans (PCDFs), chlorinated and mixed brominated/chlorinated anthracenes

27 ely 150 molecular formulas, corresponding to chlorinated and mixed chloro/bromo compounds.

28 The detected chlorinated and nonchlorinated DD/Fs comprise dibenzo-p-

29 s from 16 California residents in 2011 for 6 chlorinated and nonchlorinated dialkyl or diaryl phospha

30 ransformations were intensively studied with chlorinated and simply structured compounds such as chlo

31 Formation of chlorate, perchlorate, chlorinated, and brominated organics may compromise the

32 lationship between bladder cancer and total, chlorinated, and brominated trihalomethanes (THMs) throu

33 m a water utility was concentrated 136-fold, chlorinated, and provided as drinking water to Sprague-D

34 ss spectral patterns was applied to identify chlorinated- and brominated-containing substances with m

35 ns (PCDFs), chlorinated and mixed brominated/chlorinated anthracenes/phenanthrenes, and pyrenes/fluor

36 other halogen atom siblings, the utility of chlorinated arenes and (hetero)arenes are twofold: they

37 ed a substantial biodegradation capacity for chlorinated aromatic compounds at the oxic/anoxic interf

38 oPhenol catalyzed aza-Darzens reaction using chlorinated aromatic ketones as nucleophilic partners fo

39 dapted to survive in sites contaminated with chlorinated aromatics and may be useful for in situ bior

40 pea (Pisum sativum) seeds, the level of the chlorinated auxin, 4-chloroindole-3-acetic acid (4-Cl-IA

41 pic, we investigated the distribution of the chlorinated auxin.

42 wo types of PCDD/F precursors, involving all chlorinated benzenes (CBz) and chlorinated phenols (CPh)

43 ophenol (2,4,6-TriCPh), but have detected no chlorinated benzenes (CBzs).

44 ylene (BTEX), and analysis of delta(13)C for chlorinated benzenes and ethenes.

45 Chlorinated benzenes are ubiquitous organic contaminants

46 und to be strongly dependent on the ratio of chlorinated benzenes to chlorinated phenols and oxygen c

47 ated and simply structured compounds such as chlorinated benzenes, ethenes, and ethanes.

48 PCDFs are formed predominantly from chlorinated benzenes, while chlorinated phenols are resp

49 In this study, we describe the screening for chlorinated biomolecules by the use of mass isotope rati

50 Hexa-chlorinated biphenyls dominated (40-100%) the PCB profil

51 abundance of MeO-BDEs, mirex/dechloranes and chlorinated bipyrroles in the Brazilian dolphins.

52 ptor (AhR) agonist activities of a series of chlorinated, brominated, and mixed bromo/chlorocarbazole

53 hat allows for the simultaneous detection of chlorinated, brominated, or mixed halogen-substituted co

54 There were no measured chlorinated byproducts of bisphenol A despite occasional

55 The Fe/2OG halogenase, SyrB2, chlorinates C4 of its native substrate, l-threonine appe

56 lic indices and the experimental profiles of chlorinated carbazole, phenoxazine, and phenazine sugges

57 was enriched and maintained using the highly chlorinated commercial PCB mixture Aroclor 1260 for orga

58 , and N2O emit chloroform and other volatile chlorinated compounds (VOCls) and are thus unsuitable in

59 Volatile chlorinated compounds are major pollutants in groundwate

60 vided information on the bioaccumulation for chlorinated compounds as well as for some polycyclic aro

61 s been efficiently used to treat many of the chlorinated compounds of concern.

62 ic isotope analysis (CSIA) is unsuitable for chlorinated compounds such as trichloroethene (TCE) and

63 Polar chlorinated compounds were found to be the main chloride

64 nowledge, this is the first time such highly chlorinated compounds were studied with the LC-IRMS syst

65 The higher relative abundance of non-chlorinated compounds, namely acylglycerols, in the firs

66 he main precursors, namely acylglycerols and chlorinated compounds, on the formation yield of MCPD es

67 s, the BTEX family of compounds, and several chlorinated compounds.

68 For individual lower-chlorinated congeners (e.g., PCBs 40+41+71, 52), inhalat

69 Because low-chlorinated congeners are more volatile, these observati

70 types were dominated by PCB 28/31 and higher-chlorinated congeners in both groups reflecting rapid me

71 Levels of both higher and lower chlorinated congeners were reduced throughout the sedime

72 usion of brominated congeners in addition to chlorinated congeners when computing the toxic equivalen

73 rs revolatilization is important, for higher-chlorinated congeners, the main processes are storage in

74 d analogs contributed 370% more TEQ than did chlorinated congeners, which indicates the need to inclu

75 North American ambient conditions and lower-chlorinated congeners.

76 ent with trends previously reported for less chlorinated congeners.

77 s of groundwater samples containing BTEX and chlorinated contaminants at microgram per liter concentr

78 singly used to assess natural attenuation of chlorinated contaminants, in which anaerobic reductive d

79 When bromide-containing waters are chlorinated, conventional wisdom typically assumes HOBr

80 to encode a new pathway to generate a novel chlorinated coumarin "non-natural" product in E. coli.

81 susceptibility to metabolism than their more-chlorinated counterparts.

82 We identified molecular formulas of chlorinated DBPs after chlorination and chloramination i

83 apacity and avoiding the formation of highly chlorinated degradation products.

84 is based on halogen bonding using, e.g., the chlorinated derivatives as reference compounds.

85 s of these complexes and their corresponding chlorinated derivatives have been characterized by NMR s

86 d access to their hitherto under-represented chlorinated derivatives.

87 Their chlorinated dialkylresorcinol (DAR) core presented a maj

88 Targeted analysis of mixed brominated/chlorinated dibenzo-p-dioxins and dibenzofurans (PXDD/PX

89 ed kinetic calculations for the formation of chlorinated dibenzothiophenes and chlorinated thianthren

90 cterized by a lower contribution of the less chlorinated dioxins in comparison with the furans, consi

91 hese applications include the measurement of chlorinated dioxins in soil samples, the identification

92 These results suggest that the N-chlorinated dipeptides are produced by chlorination.

93 We report the identification of N-chlorinated dipeptides as chlorination products in drink

94 This study has identified N-chlorinated dipeptides as new disinfection byproducts in

95 To enable sensitive detection of N-chlorinated dipeptides in authentic water, we developed

96 clearly detected in the raw water, but the N-chlorinated dipeptides were at background levels.

97 These identified N-chlorinated dipeptides were synthesized and found to be

98 as broadly selective for both brominated and chlorinated diphenylethers.

99 low with a limited formation of brominated (chlorinated) disinfection byproducts (DBPs).

100 ilic substitution of unaltered DOM sites and chlorinated DOM moieties.

101 tion of methyltrioxorhenium (MTO) onto these chlorinated domains serves to activate it as a low tempe

102 Under conditions representative of chlorinated drinking water, contributions to bromination

103 nt "whole" mixture of DBPs representative of chlorinated drinking water, including unidentified DBPs

104 DCAM or, more broadly speaking, N-Cl-HAMs in chlorinated drinking waters is of significance because t

105 dy as the actual DCAN degradation product in chlorinated drinking waters.

106 etailed parts of our analysis are focused on chlorinated drugs as a function of approval date, diseas

107 ewage, primary effluent, secondary effluent, chlorinated effluent, and wetland effluent.

108 With no chlorinated electron acceptor added, HupL transcripts fe

109 o a change in the ratio of electron donor to chlorinated electron acceptor in continuously stirred ta

110 Chlorinated electron-poor pyridines were not dechlorinat

111 Chlorinated ethene concentrations and Geobacter 16S rRNA

112 Total chlorinated ethene removal was 87% in the CYP2E1 bed, 85

113 We collected 95 groundwater samples across 6 chlorinated ethene-contaminated sites and searched for r

114 Chlorinated ethenes (CEs) such as perchloroethylene, tri

115 en in other hydrocarbon contaminants such as chlorinated ethenes and ethanes due to in situ degradati

116 ractionation was found to be smaller for the chlorinated ethenes and remarkably deviating from an inv

117 d by CMC led to the long-term degradation of chlorinated ethenes at this field site.

118 nes in flowing groundwater, mass transfer of chlorinated ethenes between mobile groundwater and stati

119 ed experimental results on dehalogenation of chlorinated ethenes both in well-mixed systems and in si

120 The nonexistent chlorine isotope effects of chlorinated ethenes in all aqueous OS-SET experiments co

121 model applied here accounts for transport of chlorinated ethenes in flowing groundwater, mass transfe

122 and unsuccessful reductive dechlorination of chlorinated ethenes in groundwater under different flow

123 hod to obtain high-frequency measurements of chlorinated ethenes in oak (Quercus rubra) and baldcypre

124 tion potential of hydrogen isotope ratios of chlorinated ethenes remains untapped.

125 Enhanced dechlorination of chlorinated ethenes to nontoxic ethene was observed long

126 ment factors for microbial dehalogenation of chlorinated ethenes vary considerably we studied the pot

127 Consequently, competitive inhibition among chlorinated ethenes was examined and then added to the m

128 ta(13)C were from 2 to 60 mug/L (MTBE, BTEX, chlorinated ethenes, and benzenes) and 60-97 mug/L for d

129 hat catalyze the reductive dechlorination of chlorinated ethenes.

130 erentiate between transformation pathways of chlorinated ethenes.

131 nisms), in studies of in situ attenuation of chlorinated ethenes.

132 een explored for reductive dehalogenation of chlorinated ethenes.

133 the rule in environmental transformations of chlorinated ethenes.

134 , Dehalococcoides) and biotic degradation of chlorinated ethenes.

135 stone approach to remedy sites impacted with chlorinated ethenes.

136 al with known isotope composition, including chlorinated ethylene, chloromethane, hexachlorocyclohexa

137 hosphate esters (OPEs) and 45 brominated and chlorinated flame retardants (BFRs) were measured in par

138 A method for the determination of chlorinated flame retardants: Dechlorane Plus, Dechloran

139 able to effectively beta-brominate and beta-chlorinate for the first time cyclic enones with differe

140 HO-PCBs profile after weight loss with lower chlorinated HO-PCBs increasingly gaining importance.

141 e was verified by their presence in in vitro chlorinated human BALF.

142 ladium-based remediation method for reducing chlorinated hydrocarbons from marine environments by emp

143 eling study aims to reveal if degradation of chlorinated hydrocarbons in low permeability sediments c

144 Higher abundances of chlorinated hydrocarbons in the mudstone compared with R

145 mudstone; however, the carbon source for the chlorinated hydrocarbons is not definitively of martian

146 Concurrent evolution of O2 and chlorinated hydrocarbons suggests the presence of oxychl

147 on and CSIA profiles were determined for the chlorinated hydrocarbons that had diffused into the clay

148 H2O, CO2, SO2, O2, H2, H2S, HCl, chlorinated hydrocarbons, NO, and other trace gases were

149 formation was promoted by UV254 exposure of chlorinated imidazole and guanidine compounds, which sug

150 d 1,4-dioxane is employed as a stabilizer of chlorinated industrial solvents and is a widespread envi

151 by UV/FC and SS/FC and minimal formation of chlorinated intermediates and disinfection byproducts.

152 After all free chlorine was consumed, the chlorinated intermediates autodecomposed slowly with a f

153 s results in the accumulation of the harmful chlorinated intermediates dichloroethene (DCE) and vinyl

154 The chlorinated intermediates were found to further react wi

155 3 min(-1); when a reductant was added, these chlorinated intermediates were then reduced back to BMAA

156 Upon chlorination, four chlorinated intermediates, each with one or two chlorine

157 Chlorinated lipids are generated as a result of myeloper

158 n contrast to North American marine mammals, chlorinated MBPs and DMBPs were more abundant than their

159 purification led to the isolation of several chlorinated metabolites, including two new natural produ

160 Together the results show that chlorinated methane-metabolizing organisms introduced in

161 e characterized in-house standards and eight chlorinated methanes, ethanes, and ethenes.

162 direct, mild, operationally simple, and safe chlorinating method is compatible with a range of nitrog

163 xy-brominated diphenyl ethers (MeO-BDEs) and chlorinated methyl- and dimethyl bipyrroles (MBPs and DM

164 Although the formation of a chlorinated nitrile oxide intermediate was proved by tra

165 p-nitrophenylisocyanate and the formation of chlorinated nitrile oxide were chosen as plausible mecha

166 oom temperature conversion of brominated and chlorinated nucleobases or nucleobase precursors as star

167 a preference for N(3)-protonation for highly chlorinated O-linked 8-dG adducts in water.

168 While parent PCBs and higher-chlorinated OH-PCBs exhibited a low or nondetectable tox

169 bited a low or nondetectable toxicity, lower-chlorinated OH-PCBs significantly inhibited the germinat

170 similar and were dominated by mono- to penta-chlorinated OH-PCBs.

171 tion byproducts, known to be more toxic than chlorinated ones.

172 ool/spa waters were 1.8x more mutagenic than chlorinated ones; spa waters were 1.7x more mutagenic th

173 The most abundant chlorinated OPE was tris(1-chloro-2-propyl) phosphate (T

174 The composition profiles were dominated by chlorinated OPEs at the urban and rural sites and by non

175 studied for the reductive transformation of chlorinated or nitroaromatic compounds, no work exists e

176 resorcinol and catechol derivatives, either chlorinated or not.

177 The abundance of chlorinated organic compounds frequently exceeds chlorid

178 efore, utilizing enzymes in the synthesis of chlorinated organic compounds is important, and providin

179 U.S. EPA) regarding the use of strontium and chlorinated organic materials.

180 ese formulations do not contain strontium or chlorinated organic materials.

181 ) from cheese is generally carried out using chlorinated organic solvents.

182 oduct, and minimizes the formation of toxic, chlorinated organic waste.

183 d be considered when determining the fate of chlorinated organics at contaminated sites.

184 D), tetrabromobisphenol A (TBBPA), and three chlorinated organophosphate flame retardants (ClOPFRs),

185 base-induced aromatization of the resulting chlorinated oxanorborn(adi)enes 2 afford N-free-dihydroi

186 action for producing H2O2, which can replace chlorinated oxidants in industrial processes.

187 Chlorinated paraffins (CPs) are high production volume c

188 Chlorinated paraffins (CPs) are high production volume c

189 Temporal trends of chlorinated paraffins (CPs) were analyzed in three sedim

190 Short-chain chlorinated paraffins (SCCPs) are of concern due to thei

191 Accurate quantification of short-chain chlorinated paraffins (SCCPs) poses an exceptional chall

192 analyte signal of a polychlorinated alkanes (chlorinated paraffins) technical mixture that contains 7

193 While a lower-chlorinated PCB congener is mainly deposited by dry depo

194 ely revolatilized after deposition, a higher-chlorinated PCB congener is predominantly transferred to

195 with the more volatile, non-dioxin-like, low-chlorinated PCB congeners and HCB.

196 s, this behavior can only be seen for higher-chlorinated PCB congeners on Fiescherhorn glacier.

197 While for lower-chlorinated PCB congeners revolatilization is important,

198 bing the concentration profiles of the lower-chlorinated PCB congeners.

199 ty of OCPs and PBDEs, and a sink for the low chlorinated PCBs and gamma-hexachlorocyclohexane.

200 All PAHs, PCB 11, and other lower chlorinated PCBs and PCDD/Fs did not magnify.

201 ollowing initial hydroxylation of these less-chlorinated PCBs, metabolic sulfation to form PCB sulfat

202 oils were found to be a source of PAHs, high chlorinated PCBs, the majority of OCPs and PBDEs, and a

203 s reflecting rapid metabolism of other lower-chlorinated PCBs.

204 the measurements for PAHs, OCPs, and the low chlorinated PCBs.

205 The relative lack of tetra- and penta-chlorinated PCDD/Fs suggested that dechlorination procee

206 ngest CL was produced not by the most-highly chlorinated pentachlorophenol (PCP), but rather by the l

207 to DDE (p,p'-DDE), a major metabolite of the chlorinated pesticide DDT.

208 ammals, including mercury (whole blood), sum chlorinated pesticides (comprised of approximately 95% D

209 (PCBs) congeners, congener groups and three chlorinated pesticides [dichlorodiphenyldichloroethylene

210 ted biphenyl (PCB) congener groups and three chlorinated pesticides in a Native American population.

211 lycyclic aromatic hydrocarbons (PAHs), three chlorinated pesticides, and five metals in Norwegian wat

212 s, a new poster showcasing the structures of chlorinated pharmaceuticals was created specifically for

213 involving all chlorinated benzenes (CBz) and chlorinated phenols (CPh).

214 The widespread use of chlorinated phenols (CPs) as a wood preservative has led

215 dent on the ratio of chlorinated benzenes to chlorinated phenols and oxygen content.

216 Pentachlorophenol and other chlorinated phenols are highly toxic ubiquitous environm

217 edominantly from chlorinated benzenes, while chlorinated phenols are responsible for majority of PCDD

218 em was demonstrated for the determination of chlorinated phenoxyacetic acid herbicides in spiked rive

219 The chlorinated phloroglucinols function as intra- and inter

220 e pyoluteorin gene cluster into mono- and di-chlorinated phloroglucinols.

221 coides mccartyi strain JNA detoxifies highly chlorinated polychlorinated biphenyl (PCB) mixtures via

222 Chlorinated polyethylene accounted for the largest propo

223 Subsequent diverse transformations of the chlorinated products demonstrate the versatility of meta

224 d through monitoring of formation of HMF and chlorinated products under pyrolytic conditions using gl

225 Here we show that not only chlorinated quinoid intermediates, but more interestingl

226 eport the invention of a new guanidine-based chlorinating reagent, CBMG or "Palau'chlor", inspired by

227 onditions, this compound outperforms typical chlorinating reagents for organic synthesis, facilitates

228 Comparisons with other known chlorinating reagents revealed CBMG to be the premier re

229 s of ClO2 on C. parvum oocyst infectivity in chlorinated recreational water venues (e.g., pools).

230 rination for inactivating Cryptosporidium in chlorinated recreational water venues, but further studi

231 exyl-4-methoxycinnamate, and octocrylene, in chlorinated seawater swimming pools.

232 the transformation products of oxybenzone in chlorinated seawater swimming pools; especially that use

233 s showed that only octocrylene was stable in chlorinated seawater.

234 of the long term health effects of the lower-chlorinated, semi-volatile PCBs in the indoor environmen

235 Mutagenic potencies of samples from a chlorinated site correlated best with brominated haloace

236 hloride in surface soils, and the ability to chlorinate soil organic matter (SOM) appears widespread

237 advantage of this approach is the use of non-chlorinated solvent and small amounts of organic solvent

238 These results suggest that chlorinated solvent bioattenuation rates could be impede

239 dy may also have implications for optimizing chlorinated solvent bioremediation.

240 1,2-Dichloroethane (1,2-DCA) is a chlorinated solvent classified as a probable human carci

241 tificially contaminated by a three component chlorinated solvent mixture (tetrachloroethene (PCE) 45

242 dation by bacterial pure cultures exposed to chlorinated solvent mixtures as well as in environmental

243 n, evidence that multiple pathways exist for chlorinated solvent reduction.

244 set of sites, there was little evidence that chlorinated solvent remedial efforts (e.g., chemical oxi

245 mplications of these findings for monitoring chlorinated solvent sites are discussed.

246 Bioremediation at chlorinated solvent sites often leads to groundwater aci

247 ous film-forming foams (AFFFs) to extinguish chlorinated solvent-fueled fires has led to the co-conta

248 euterated) and nonlabeled isotopologues) and chlorinated solvents (trichloroethene, TCE, and cis-dich

249 ples collected from a site contaminated with chlorinated solvents and 1,4-dioxane.

250 ental pollutants like nitrate, hydrocarbons, chlorinated solvents and heavy metals.

251 study investigated the impacts of individual chlorinated solvents and their mixtures on aerobic 1,4-d

252 cles can contribute to the transformation of chlorinated solvents and various other contaminants into

253 ane bioremediation strategies at sites where chlorinated solvents are present as co-contaminants.

254 ved recalcitrance at groundwater sites where chlorinated solvents are present.

255 ion that abiotic natural attenuation (NA) of chlorinated solvents can be important has created demand

256 ng reactants for reductive dechlorination of chlorinated solvents due to high reaction rates and the

257 erovalent iron (Fe(0)) in the degradation of chlorinated solvents in subsurface environments is of in

258 e of the enhanced rate of degradation of the chlorinated solvents in the inoculated trees.

259 ation approaches for sites contaminated with chlorinated solvents requires a fundamental understandin

260 rile as the solvent, thus avoiding hazardous chlorinated solvents such as CCl4.

261 beneficial properties in comparison to other chlorinated solvents such as dichloroethane.

262 es used for the bioremediation of co-mingled chlorinated solvents such as trichloroethene (TCE).

263 ition of 1,4-dioxane biodegradation rates by chlorinated solvents was attributed to delayed ATP produ

264 At sites where dioxane and chlorinated solvents were present, the median value of a

265 are a common photoisomerization mechanism in chlorinated solvents with notable differences in kinetic

266 drocarbons, single ring aromatics, terpenes, chlorinated solvents, formaldehyde, and acrolein.

267 bacterium involved in the bioremediation of chlorinated solvents, reveal homologous genes encoding a

268 s 1-7 exhibit moderate-to-good solubility in chlorinated solvents, such as 1,2-dichlorobenzene and ch

269 and groundwater contaminated with fuels and chlorinated solvents.

270 date carried out in non-donor hydrocarbon or chlorinated solvents.

271 sheet conformations were shown to prevail in chlorinated solvents.

272 l of an alkaline AA solution for remediating chlorinated solvents.

273 d oxygen and the co-occurrence of inhibiting chlorinated solvents.

274 ange of 8.6-51 g g(-1) and in agreement with chlorinated substances.

275 ed to a stronger interaction between MTO and chlorinated surface regions, as well as extensive deplet

276 absorption in a standard diet, as well as a chlorinated tap water sample.

277 roperty evaluation of several brominated and chlorinated tetraazapentacenes.

278 o-beta-aminoketone intermediates featuring a chlorinated tetrasubstituted stereocenter can be isolate

279 Indoor air PCBs are generally less chlorinated than PCBs that are absorbed via the diet, or

280 rmation of chlorinated dibenzothiophenes and chlorinated thianthrenes that could be applied to predic

281 r, concerns about the potential formation of chlorinated transformation products require an understan

282 n, the antimicrobial agent in handsoaps, and chlorinated triclosan derivatives (CTDs, formed during d

283 kidneys, levels of HOCl-derived oxidized and chlorinated tryptophan residues W(28) and W(192) are sig

284 acute coronary syndrome had higher levels of chlorinated tyrosine 192 and oxidized methionine 148 com

285 Levels of chlorinated tyrosine and oxidized methionine associated

286 The absence of lysine increased yields of chlorinated tyrosines and decreased yields of brominated

287 HOCl is present, the SiF fluorophores become chlorinated, via an intermediate halohydrin, resulting i

288 oroaldehydes, kinetic resolutions of complex chlorinated vinyl epoxide intermediates, and Z-selective

289 excess of 4% decreased the decomposition of chlorinated VOCs as a result of ozone and nitrogen oxide

290 lted in increasing the removal efficiency of chlorinated VOCs in plasma.

291 tive field site contaminated with a range of chlorinated volatile organic compounds (cVOC).

292 atment aimed predominantly at remediation of chlorinated volatile organic compounds (cVOCs) and perfl

293 The migration of chlorinated volatile organic compounds from groundwater

294 ted, e.g., chloromethane (CH3Cl), and higher chlorinated VOX compounds such as trichloromethane (CHCl

295 ing may lead to higher DBP concentrations in chlorinated water with lower distribution system tempera

296 se in concentration was only notable for the chlorinated water with very high chlorine dose.

297 levels of NTM in chloraminated water than in chlorinated water.

298 vated DBP formation during transportation of chlorinated waters in copper-containing distribution sys

299 ncluding BrCl, Br2, BrOCl, Br2O) can form in chlorinated waters, albeit at generally lower concentrat

300 Silver ink was printed and chlorinated with bleach solution.