ライフサイエンスコーパス: chlorinated

1 A newly developed annulated 5-chlorinated 1,3,2,5-diazadiborinine derivative (4) selec

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

3 rs within the water samples and polyethylene-chlorinated (31%) in sediments.

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

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

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

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

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

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

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

11 ally more cytotoxic and genotoxic than their chlorinated analogs.

12 d dialdehyde 2-butene-1,4-dial (BDA) and its chlorinated analogue, chloro-2-butene-1,4-dial (Cl-BDA),

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

14 etrahydrofuran, and cyclohexane), as well as chlorinated and aromatic pollutants, including vinyl chl

15 the simultaneous determination of up to nine chlorinated and brominated acetic acids by HPLC-ICPMS/MS

16 ug Cl L(-1) and 0.8-1.5 mug Br L(-1) for the chlorinated and brominated acetic acids, respectively.

17 ncreased antimicrobial activity, we designed chlorinated and brominated analogues of a known peptoid

18 The chlorinated and brominated byproduct concentration may b

19 Chlorinated and brominated standards and isotopically la

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

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

22 omers, with complementary strategies to both chlorinated and brominated variants, formed with high di

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

24 report elevated levels of gaseous inorganic chlorinated and nitrogenated compounds in indoor air whi

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

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

27 sing these seed profiles to isolate relevant chlorinated and/or brominated compounds.

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

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

30 A total of 52 brominated, chlorinated, and organophosphorus compounds were identif

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

32 of site-selective cross-coupling of multiply chlorinated arenes.

33 comparison and formation and degradation of chlorinated aromatic intermediates using the same non-ch

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

35 uperfamily associated with dehalogenation of chlorinated aromatics and appears to represent a new sub

36 ) to have their drinking water automatically chlorinated at the point of collection by a solid tablet

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

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

39 ectronic and geometrical influences of ortho-chlorinated azobenzenes on their photophysical propertie

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

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

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

43 l) of two polychlorinated biphenyls and four chlorinated benzenes were below a factor of 2 in the pla

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

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

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

47 ly leading to the irritation associated with chlorinated bleach.

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

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

50 Ag ink was printed and chlorinated by NaClO printing, forming a Ag/AgCl pseudor

51 This research investigated chlorinated byproduct formation at Ti(4)O(7) anodes.

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

53 Chlorinated byproducts should be carefully monitored dur

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

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

56 stigated the relationship between persistent chlorinated compounds and hypertension in residents livi

57 f the minimal formation of free chlorine and chlorinated compounds in photocatalytic degradation is d

58 As a consequence potentially toxic chlorinated compounds might be generated.

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

60 The reductive dechlorination of other chlorinated compounds with an activated carbon atom was

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

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

63 the commingled contamination of dioxane and chlorinated compounds.

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

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

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

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

68 e colorant while more than 75% of the higher chlorinated congeners remained in the sample.

69 By the end of the experiment, all the lower chlorinated congeners were absent from the colorant whil

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

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

72 ent with trends previously reported for less chlorinated congeners.

73 North American ambient conditions and lower-chlorinated congeners.

74 he colorant at a faster rate than the higher chlorinated congeners.

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

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

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

78 susceptibility to metabolism than their more-chlorinated counterparts.

79 ure and contains novel high molecular weight chlorinated DBPs that are detected via high-resolution m

80 nt) after exposure to six brominated and two chlorinated DBPs: bromoacetic acid (BAA), bromoacetonitr

81 tosis and necroptosis, while the analogously chlorinated derivative exerted only necroptosis.

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

83 ater, chlorination leads to the formation of chlorinated derivatives of Bisphenol A (ClxBPA), that ha

84 In this study, lower chlorinated derivatives of triclosan were synthesized to

85 our lipids, the latter presumably by forming chlorinated derivatives.

86 the parent diacid was calculated for all 15 chlorinated diacids and shows a dramatic increase with s

87 n provides access to five of the 15 possible chlorinated diacids.

88 Their chlorinated dialkylresorcinol (DAR) core presented a maj

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

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

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

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

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

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

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

96 as broadly selective for both brominated and chlorinated diphenylethers.

97 Cl(2) may enhance the formation kinetics of chlorinated disinfection byproducts (DBPs) and exacerbat

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

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

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

101 ed water can increase taste acceptability of chlorinated drinking water while still reducing the risk

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

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

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

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

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

107 Chlorinated electron-poor pyridines were not dechlorinat

108 s might contribute to abiotic degradation of chlorinated ethene (CE) plumes.

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

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

111 Chlorinated ethenes (CEs) such as perchloroethylene, tri

112 ultures coinjection for in situ treatment of chlorinated ethenes and ClO(4)(-).

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

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

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

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

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

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

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

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

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

122 een explored for reductive dehalogenation of chlorinated ethenes.

123 the rule in environmental transformations of chlorinated ethenes.

124 , Dehalococcoides) and biotic degradation of chlorinated ethenes.

125 stone approach to remedy sites impacted with chlorinated ethenes.

126 hat catalyze the reductive dechlorination of chlorinated ethenes.

127 (PW4) and river sediment (TC) impacted with chlorinated ethenes.

128 ication of chlorinated pollutants, including chlorinated ethenes.

129 hlorination in groundwater contaminated with chlorinated ethenes.

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

131 er structured than in gels prepared from non-chlorinated flour.

132 igh catalytic activity to reduce alachlor, a chlorinated herbicide, in the aqueous medium at differen

133 chlorine isotope analysis (Cl-CSIA) of three chlorinated herbicides, atrazine, acetochlor, and metola

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

135 he lower ppt(v) range for different ketones, chlorinated hydrocarbons and methyl salicylate that form

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

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

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

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

140 s of free chlorine (hypochlorite, Cl(2)) and chlorinated hydrocarbons were formed in solution, while

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

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

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

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

145 The chlorinated intermediates were found to further react wi

146 3 min(-1); when a reductant was added, these chlorinated intermediates were then reduced back to BMAA

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

148 ulfonates, and bromosultone sulfonates, with chlorinated/iodinated analogues formed to a lesser exten

149 Feeding Drosophila with lower chlorinated (LC) PCB congeners 28, 52 or 101 resulted in

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

151 ed metabolomics analysis revealed a group of chlorinated metabolites produced by the well-studied mod

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

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

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

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

156 Non-chlorinated mobile phase composition was optimized for s

157 at catalytic system capable of detoxifying a chlorinated model compound with turnover numbers of up t

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

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

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

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

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

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

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

165 -OPEs (Cl-OPEs) concentrations exceeded Enon-chlorinated-OPEs (non-Cl-OPEs) with median concentration

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

167 resorcinol and catechol derivatives, either chlorinated or not.

168 ty-two-year record of in situ degradation of chlorinated organic compounds by a granular iron permeab

169 The abundance of chlorinated organic compounds frequently exceeds chlorid

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

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

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

173 hromatography-mass spectroscopy detected two chlorinated organic products.

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

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

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

177 Chlorinated paraffins (CPs) are a complex family of cont

178 Chlorinated paraffins (CPs) are high production volume c

179 Chlorinated paraffins (CPs) are high production volume c

180 Chlorinated paraffins (CPs) are industrial chemicals, su

181 Chlorinated paraffins (CPs) are used in various products

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

183 Due to their likely similarity with chlorinated paraffins (CPs), Br-Cl PXAs may pose a simil

184 Bs and OCPs biomagnified (TMF >1), while all chlorinated paraffins (CPs), PAHs, and phthalates underw

185 additional characterization of medium-chain chlorinated paraffins (MCCPs, C14-17) in oven-baked past

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

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

188 r simultaneous quantification of short-chain chlorinated paraffins (SCCPs, C10-13) and an additional

189 Short-, medium-, and long-chain chlorinated paraffins (SCCPs, MCCPs, and LCCPs) have a w

190 Long-chain C(18) chlorinated paraffins are also present, although they re

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

192 medium chain (MCCPs), and long chain (LCCPs) chlorinated paraffins.

193 ed aromatic intermediates using the same non-chlorinated parent compound, 4-ethylphenol (4EP).

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

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

196 Even the fully chlorinated PCB209 was emitted from green colorant.

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

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

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

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

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

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

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

204 +, which is even better than the most-highly chlorinated PCP, and much better than its two other TeCP

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

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

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

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

209 ersistent organic pollutants, such as highly chlorinated pesticides and polychlorinated biphenyls.

210 In general, the loss rates of vapor phase chlorinated pesticides have slowed by about a factor of

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

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

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

214 zed C-O-selective Suzuki-Miyaura coupling of chlorinated phenol derivatives where the oxygen-containi

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

216 it is a general phenomenon for other highly chlorinated phenols (HCPs); and if so, what are the majo

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

218 The chlorinated phloroglucinols function as intra- and inter

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

220 or studies have focused on legacy persistent chlorinated pollutants (POPs), while the effects of poly

221 in the transformation and detoxification of chlorinated pollutants, including chlorinated ethenes.

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

223 Chlorinated polyethylene accounted for the largest propo

224 An empty glass Petri dish (control), a chlorinated polypropylene-coated glass Petri dish (contr

225 dered to be associated with the formation of chlorinated potentially toxic compounds, such as chlorop

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

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

228 thereafter, leading to dimeric and trimeric chlorinated products.

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

230 ntibiotic activity of the parent compound in chlorinated samples at 2.0, 3.0, and 4.0 mgCl(2)/L, resp

231 in line with the decrease of bioactivity in chlorinated samples, an increase of bioactivity after co

232 ld contribute to the overall toxicity of the chlorinated samples.

233 uting to the acute toxic effects measured in chlorinated samples.

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

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

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

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

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

239 lity, indicating strong interactions between chlorinated soft wheat flour (CSWF) components and solve

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

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

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

243 1,2-Dichloroethane (1,2-DCA) is a chlorinated solvent classified as a probable human carci

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

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

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

247 Bioremediation at chlorinated solvent sites often leads to groundwater aci

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

249 g., 250 to 1000 mug/L) with co-occurrence of chlorinated solvents (e.g., 0.5 to 8 mg/L), underscoring

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

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

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

253 Chlorinated solvents are by far the most treated compoun

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

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

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

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

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

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

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

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

262 n occur in groundwater plumes comingled with chlorinated solvents such as trichloroethene (TCE).

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

264 Chlorinated solvents were once, and in many places are s

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

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

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

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

269 lectron process and extend this technique to chlorinated solvents.

270 sheet conformations were shown to prevail in chlorinated solvents.

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

272 and groundwater contaminated with fuels and chlorinated solvents.

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

274 sustainable catalytic removal of co-existing chlorinated solvents.

275 long with other regulated compounds, such as chlorinated solvents.

276 ic variability and any unexpected changes in chlorinated source gas emissions.

277 ed stereodivergent synthesis of all possible chlorinated stereoisomers while also demonstrating diast

278 idase (Tar16) enzymes that are selective for chlorinated substrates.

279 Together, these results suggest chlorinated sulfone carbofluoresceins can be promising c

280 New, chlorinated sulfone carbofluoresceins have low p K(a) va

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

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

283 roperty evaluation of several brominated and chlorinated tetraazapentacenes.

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

285 ial of ERD, the exact microstructure of the (chlorinated) TFC membranes should be better understood.

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

287 ion of bioactive samples identified that the chlorinated TP296 (generated from the destruction of the

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

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

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

291 ant CP homologue groups were hepta- and octa-chlorinated undecanes and dodecanes.

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

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

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

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

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

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

298 Silver ink was printed and chlorinated with bleach solution.

299 six of its carbon-carbon double bonds become chlorinated within 1-2 h.

300 ve control), fresh water (negative control), chlorinated WW, and HPC WW.