ライフサイエンスコーパス: chlorinate

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 ults show that while HOCl is the predominant chlorinating agent for the most reactive alkene, Cl(2) a

5 ide is used as a cheap and readily available chlorinating agent in combination with trioctylphosphane

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

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

8 cid (TCCA) as a cheap and noncorrosive solid chlorinating agent.

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

10 mechanism and a possible regeneration of the chlorinating agent.

11 e pH, Cl(-) concentration, and the resulting chlorinating agents (e.g., Cl(2), HOCl, OCl(-), and Cl(2

12 The behavior of these chlorinating agents differed for each reactive site such

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

14 importance of different chlorine species as chlorinating agents.

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

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

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

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

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

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

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

22 ally more cytotoxic and genotoxic than their chlorinated analogs.

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

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

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

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

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

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

29 The chlorinated and brominated byproduct concentration may b

30 Chlorinated and brominated standards and isotopically la

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

57 ly leading to the irritation associated with chlorinated bleach.

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

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

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

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

62 Chlorinated byproducts should be carefully monitored dur

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

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

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

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

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

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

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

70 the commingled contamination of dioxane and chlorinated compounds.

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

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

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

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

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

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

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

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

79 ent with trends previously reported for less chlorinated congeners.

80 North American ambient conditions and lower-chlorinated congeners.

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

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

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

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

85 susceptibility to metabolism than their more-chlorinated counterparts.

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

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

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

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

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

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

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

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

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

95 Their chlorinated dialkylresorcinol (DAR) core presented a maj

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

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

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

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

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

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

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

103 as broadly selective for both brominated and chlorinated diphenylethers.

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

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

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

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

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

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

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

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

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

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

114 Chlorinated electron-poor pyridines were not dechlorinat

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

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

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

118 Chlorinated ethenes (CEs) such as perchloroethylene, tri

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

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

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

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

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

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

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

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

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

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 een explored for reductive dehalogenation of chlorinated ethenes.

130 the rule in environmental transformations of chlorinated ethenes.

131 , Dehalococcoides) and biotic degradation of chlorinated ethenes.

132 stone approach to remedy sites impacted with chlorinated ethenes.

133 hat catalyze the reductive dechlorination of chlorinated ethenes.

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

135 ication of chlorinated pollutants, including chlorinated ethenes.

136 hlorination in groundwater contaminated with chlorinated ethenes.

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

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

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

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

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

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

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

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

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

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

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

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

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

150 The chlorinated intermediates were found to further react wi

151 3 min(-1); when a reductant was added, these chlorinated intermediates were then reduced back to BMAA

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

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

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

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

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

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

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

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

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

161 Non-chlorinated mobile phase composition was optimized for s

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

163 crin, the most common HNM, is synthesized by chlorinating nitromethane, suggesting that nitromethane

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

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

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

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

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

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

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

171 dent tryptophan halogenases regioselectively chlorinate or brominate trypto-phan's indole moiety at C

172 pended to its carrier protein but can either chlorinate or hydroxylate C4 and (ii) two bifunctional e

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

174 resorcinol and catechol derivatives, either chlorinated or not.

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

176 The abundance of chlorinated organic compounds frequently exceeds chlorid

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

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

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

180 hromatography-mass spectroscopy detected two chlorinated organic products.

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

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

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

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

185 Chlorinated paraffins (CPs) are high production volume c

186 Chlorinated paraffins (CPs) are high production volume c

187 Chlorinated paraffins (CPs) are industrial chemicals, su

188 Chlorinated paraffins (CPs) are used in various products

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

222 The chlorinated phloroglucinols function as intra- and inter

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

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

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

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

227 Chlorinated polyethylene accounted for the largest propo

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

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

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

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

232 thereafter, leading to dimeric and trimeric chlorinated products.

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

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

235 In chlorinating real waters with elevated [Cl(-)], formatio

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

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

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

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

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

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

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

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

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

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

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

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

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

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

250 1,2-Dichloroethane (1,2-DCA) is a chlorinated solvent classified as a probable human carci

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

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

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

254 Bioremediation at chlorinated solvent sites often leads to groundwater aci

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

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

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

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

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

260 Chlorinated solvents are by far the most treated compoun

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

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

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

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

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

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

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

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

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

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

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

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

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

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

275 lectron process and extend this technique to chlorinated solvents.

276 sheet conformations were shown to prevail in chlorinated solvents.

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

278 and groundwater contaminated with fuels and chlorinated solvents.

279 sustainable catalytic removal of co-existing chlorinated solvents.

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

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

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

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

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

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

286 roperty evaluation of several brominated and chlorinated tetraazapentacenes.

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

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

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

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

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

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

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

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

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

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

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

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

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.