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1 tachlorophenol (PCP), but rather by the less chlorinated 2,3,5,6-tetrachlorophenol (2,3,5,6-TeCP), on
2 remediation of groundwater contaminated with chlorinated aliphatic hydrocarbons such as perchloroethe
3 orm FeS, suggesting that, after oxidation by chlorinated aliphatics, FeS can be regenerated by additi
4 apid disinfection of the hospital WDS with a chlorinated, alkaline detergent and subsequent superchlo
5                SCCPs are complex mixtures of chlorinated alkanes with variable chain length and chlor
6 ancomycin, exclusive conversion of vicinally chlorinated alkanes, and tolerance to short-term oxygen
7 the presence of degradation products such as chlorinated alkenes (CP-enes).
8  moved toward alterative compounds including chlorinated alkyl and nonchlorinated aryl organophosphat
9 ions, N-chlorination and dechlorination of N-chlorinated amide links by hydroxyl ion are the two domi
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  Br-DBPs are generally more toxic than their chlorinated analogues.
13                                          For chlorinated and brominated aromatics, nucleophilic addit
14                                          The chlorinated and brominated byproduct concentration may b
15                                              Chlorinated and brominated standards and isotopically la
16 ce on calibration was not as significant for chlorinated and brominated substances as observed for hu
17 end=0.13; the ORs at the 95th percentile for chlorinated and brominated THMs were 1.77 (95% CI: 1.05,
18 xtracting nonvolatile and volatile DBPs from chlorinated and chloraminated drinking water to minimize
19 o experiments, this precursor is furthermore chlorinated and cyclized to merochlorin A and isomeric m
20 etermine second-order rate constants for the chlorinated and iodinated oxidants.
21 CNs), polychlorinated dibenzofurans (PCDFs), chlorinated and mixed brominated/chlorinated anthracenes
22 ely 150 molecular formulas, corresponding to chlorinated and mixed chloro/bromo compounds.
23                                 The detected chlorinated and nonchlorinated DD/Fs comprise dibenzo-p-
24 s from 16 California residents in 2011 for 6 chlorinated and nonchlorinated dialkyl or diaryl phospha
25 ransformations were intensively studied with chlorinated and simply structured compounds such as chlo
26          Formation of chlorate, perchlorate, chlorinated, and brominated organics may compromise the
27 lationship between bladder cancer and total, chlorinated, and brominated trihalomethanes (THMs) throu
28 m a water utility was concentrated 136-fold, chlorinated, and provided as drinking water to Sprague-D
29 ss spectral patterns was applied to identify chlorinated- and brominated-containing substances with m
30 ns (PCDFs), chlorinated and mixed brominated/chlorinated anthracenes/phenanthrenes, and pyrenes/fluor
31  other halogen atom siblings, the utility of chlorinated arenes and (hetero)arenes are twofold: they
32 ed a substantial biodegradation capacity for chlorinated aromatic compounds at the oxic/anoxic interf
33 oPhenol catalyzed aza-Darzens reaction using chlorinated aromatic ketones as nucleophilic partners fo
34 dapted to survive in sites contaminated with chlorinated aromatics and may be useful for in situ bior
35  pea (Pisum sativum) seeds, the level of the chlorinated auxin, 4-chloroindole-3-acetic acid (4-Cl-IA
36 pic, we investigated the distribution of the chlorinated auxin.
37 wo types of PCDD/F precursors, involving all chlorinated benzenes (CBz) and chlorinated phenols (CPh)
38 ophenol (2,4,6-TriCPh), but have detected no chlorinated benzenes (CBzs).
39 le bioremediation of sites contaminated with chlorinated benzenes and benzene.
40 ylene (BTEX), and analysis of delta(13)C for chlorinated benzenes and ethenes.
41                                              Chlorinated benzenes are ubiquitous organic contaminants
42 und to be strongly dependent on the ratio of chlorinated benzenes to chlorinated phenols and oxygen c
43 ated and simply structured compounds such as chlorinated benzenes, ethenes, and ethanes.
44          PCDFs are formed predominantly from chlorinated benzenes, while chlorinated phenols are resp
45 In this study, we describe the screening for chlorinated biomolecules by the use of mass isotope rati
46                                         Hexa-chlorinated biphenyls dominated (40-100%) the PCB profil
47 abundance of MeO-BDEs, mirex/dechloranes and chlorinated bipyrroles in the Brazilian dolphins.
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                       There were no measured chlorinated byproducts of bisphenol A despite occasional
51 lic indices and the experimental profiles of chlorinated carbazole, phenoxazine, and phenazine sugges
52 was enriched and maintained using the highly chlorinated commercial PCB mixture Aroclor 1260 for orga
53 , and N2O emit chloroform and other volatile chlorinated compounds (VOCls) and are thus unsuitable in
54                                     Volatile chlorinated compounds are major pollutants in groundwate
55 vided information on the bioaccumulation for chlorinated compounds as well as for some polycyclic aro
56 s been efficiently used to treat many of the chlorinated compounds of concern.
57 ic isotope analysis (CSIA) is unsuitable for chlorinated compounds such as trichloroethene (TCE) and
58                                        Polar chlorinated compounds were found to be the main chloride
59 nowledge, this is the first time such highly chlorinated compounds were studied with the LC-IRMS syst
60         The higher relative abundance of non-chlorinated compounds, namely acylglycerols, in the firs
61 he main precursors, namely acylglycerols and chlorinated compounds, on the formation yield of MCPD es
62 s, the BTEX family of compounds, and several chlorinated compounds.
63                         For individual lower-chlorinated congeners (e.g., PCBs 40+41+71, 52), inhalat
64                                  Because low-chlorinated congeners are more volatile, these observati
65 types were dominated by PCB 28/31 and higher-chlorinated congeners in both groups reflecting rapid me
66              Levels of both higher and lower chlorinated congeners were reduced throughout the sedime
67 usion of brominated congeners in addition to chlorinated congeners when computing the toxic equivalen
68 rs revolatilization is important, for higher-chlorinated congeners, the main processes are storage in
69 d analogs contributed 370% more TEQ than did chlorinated congeners, which indicates the need to inclu
70  North American ambient conditions and lower-chlorinated congeners.
71 ent with trends previously reported for less chlorinated congeners.
72 s of groundwater samples containing BTEX and chlorinated contaminants at microgram per liter concentr
73 singly used to assess natural attenuation of chlorinated contaminants, in which anaerobic reductive d
74           When bromide-containing waters are chlorinated, conventional wisdom typically assumes HOBr
75  to encode a new pathway to generate a novel chlorinated coumarin "non-natural" product in E. coli.
76 susceptibility to metabolism than their more-chlorinated counterparts.
77 rine bacterial natural products containing a chlorinated cyclopenta[a]indene core of suspected enediy
78          We identified molecular formulas of chlorinated DBPs after chlorination and chloramination i
79 apacity and avoiding the formation of highly chlorinated degradation products.
80 in drinking water may react with BPA to form chlorinated derivatives (ClxBPA), which have indeed been
81 is based on halogen bonding using, e.g., the chlorinated derivatives as reference compounds.
82 s of these complexes and their corresponding chlorinated derivatives have been characterized by NMR s
83 d access to their hitherto under-represented chlorinated derivatives.
84                                        Their chlorinated dialkylresorcinol (DAR) core presented a maj
85        Targeted analysis of mixed brominated/chlorinated dibenzo-p-dioxins and dibenzofurans (PXDD/PX
86 ed kinetic calculations for the formation of chlorinated dibenzothiophenes and chlorinated thianthren
87 cterized by a lower contribution of the less chlorinated dioxins in comparison with the furans, consi
88 hese applications include the measurement of chlorinated dioxins in soil samples, the identification
89             These results suggest that the N-chlorinated dipeptides are produced by chlorination.
90            We report the identification of N-chlorinated dipeptides as chlorination products in drink
91                  This study has identified N-chlorinated dipeptides as new disinfection byproducts in
92           To enable sensitive detection of N-chlorinated dipeptides in authentic water, we developed
93 clearly detected in the raw water, but the N-chlorinated dipeptides were at background levels.
94                           These identified N-chlorinated dipeptides were synthesized and found to be
95 as broadly selective for both brominated and chlorinated diphenylethers.
96  low with a limited formation of brominated (chlorinated) disinfection byproducts (DBPs).
97 ilic substitution of unaltered DOM sites and chlorinated DOM moieties.
98 tion of methyltrioxorhenium (MTO) onto these chlorinated domains serves to activate it as a low tempe
99           Under conditions representative of chlorinated drinking water, contributions to bromination
100 nt "whole" mixture of DBPs representative of chlorinated drinking water, including unidentified DBPs
101 DCAM or, more broadly speaking, N-Cl-HAMs in chlorinated drinking waters is of significance because t
102 dy as the actual DCAN degradation product in chlorinated drinking waters.
103 etailed parts of our analysis are focused on chlorinated drugs as a function of approval date, diseas
104 ewage, primary effluent, secondary effluent, chlorinated effluent, and wetland effluent.
105                                      With no chlorinated electron acceptor added, HupL transcripts fe
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                                              Chlorinated ethene concentrations and Geobacter 16S rRNA
109 dehalorespiration provided a good fit to the chlorinated ethene concentrations measured in a cocultur
110                                        Total chlorinated ethene removal was 87% in the CYP2E1 bed, 85
111 We collected 95 groundwater samples across 6 chlorinated ethene-contaminated sites and searched for r
112                                              Chlorinated ethenes (CEs) such as perchloroethylene, tri
113 en in other hydrocarbon contaminants such as chlorinated ethenes and ethanes due to in situ degradati
114 ractionation was found to be smaller for the chlorinated ethenes and remarkably deviating from an inv
115 d by CMC led to the long-term degradation of chlorinated ethenes at this field site.
116 nes in flowing groundwater, mass transfer of chlorinated ethenes between mobile groundwater and stati
117 ed experimental results on dehalogenation of chlorinated ethenes both in well-mixed systems and in si
118  The nonexistent chlorine isotope effects of chlorinated ethenes in all aqueous OS-SET experiments co
119 model applied here accounts for transport of chlorinated ethenes in flowing groundwater, mass transfe
120 and unsuccessful reductive dechlorination of chlorinated ethenes in groundwater under different flow
121 hod to obtain high-frequency measurements of chlorinated ethenes in oak (Quercus rubra) and baldcypre
122 tion potential of hydrogen isotope ratios of chlorinated ethenes remains untapped.
123 one bacteria for reductive dechlorination of chlorinated ethenes to nontoxic ethene in contaminated a
124                   Enhanced dechlorination of chlorinated ethenes to nontoxic ethene was observed long
125 ment factors for microbial dehalogenation of chlorinated ethenes vary considerably we studied the pot
126   Consequently, competitive inhibition among chlorinated ethenes was examined and then added to the m
127           Inhibition of dehalorespiration by chlorinated ethenes was previously observed in cultures
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  we focus on the reductive dehalogenation of chlorinated ethenes.
133 een explored for reductive dehalogenation of chlorinated ethenes.
134 the rule in environmental transformations of chlorinated ethenes.
135 , Dehalococcoides) and biotic degradation of chlorinated ethenes.
136 stone approach to remedy sites impacted with chlorinated ethenes.
137 al with known isotope composition, including chlorinated ethylene, chloromethane, hexachlorocyclohexa
138 hosphate esters (OPEs) and 45 brominated and chlorinated flame retardants (BFRs) were measured in par
139            A method for the determination of chlorinated flame retardants: Dechlorane Plus, Dechloran
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 xy-brominated diphenyl ethers (MeO-BDEs) and chlorinated methyl- and dimethyl bipyrroles (MBPs and DM
163                  Although the formation of a chlorinated nitrile oxide intermediate was proved by tra
164 p-nitrophenylisocyanate and the formation of chlorinated nitrile oxide were chosen as plausible mecha
165 oom temperature conversion of brominated and chlorinated nucleobases or nucleobase precursors as star
166 a preference for N(3)-protonation for highly chlorinated O-linked 8-dG adducts in water.
167                 While parent PCBs and higher-chlorinated OH-PCBs exhibited a low or nondetectable tox
168 bited a low or nondetectable toxicity, lower-chlorinated OH-PCBs significantly inhibited the germinat
169 similar and were dominated by mono- to penta-chlorinated OH-PCBs.
170 tion byproducts, known to be more toxic than chlorinated ones.
171 ool/spa waters were 1.8x more mutagenic than chlorinated ones; spa waters were 1.7x more mutagenic th
172                            The most abundant chlorinated OPE was tris(1-chloro-2-propyl) phosphate (T
173   The composition profiles were dominated by chlorinated OPEs at the urban and rural sites and by non
174  studied for the reductive transformation of chlorinated or nitroaromatic compounds, no work exists e
175  resorcinol and catechol derivatives, either chlorinated or not.
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 U.S. EPA) regarding the use of strontium and chlorinated organic materials.
179 ese formulations do not contain strontium or chlorinated organic materials.
180 ) from cheese is generally carried out using chlorinated organic solvents.
181 oduct, and minimizes the formation of toxic, chlorinated organic waste.
182 d be considered when determining the fate of chlorinated organics at contaminated sites.
183 D), tetrabromobisphenol A (TBBPA), and three chlorinated organophosphate flame retardants (ClOPFRs),
184  base-induced aromatization of the resulting chlorinated oxanorborn(adi)enes 2 afford N-free-dihydroi
185 action for producing H2O2, which can replace chlorinated oxidants in industrial processes.
186                                              Chlorinated paraffins (CPs) are high production volume c
187                                              Chlorinated paraffins (CPs) are high production volume c
188                           Temporal trends of chlorinated paraffins (CPs) were analyzed in three sedim
189                                  Short-chain chlorinated paraffins (SCCPs) are of concern due to thei
190       Accurate quantification of short-chain chlorinated paraffins (SCCPs) poses an exceptional chall
191 analyte signal of a polychlorinated alkanes (chlorinated paraffins) technical mixture that contains 7
192                                While a lower-chlorinated PCB congener is mainly deposited by dry depo
193 ely revolatilized after deposition, a higher-chlorinated PCB congener is predominantly transferred to
194 with the more volatile, non-dioxin-like, low-chlorinated PCB congeners and HCB.
195 s, this behavior can only be seen for higher-chlorinated PCB congeners on Fiescherhorn glacier.
196                              While for lower-chlorinated PCB congeners revolatilization is important,
197 bing the concentration profiles of the lower-chlorinated PCB congeners.
198 ty of OCPs and PBDEs, and a sink for the low chlorinated PCBs and gamma-hexachlorocyclohexane.
199            All PAHs, PCB 11, and other lower chlorinated PCBs and PCDD/Fs did not magnify.
200  sum PCBs in obese individuals, while higher chlorinated PCBs had a higher contribution for the contr
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 s of ClO2 on C. parvum oocyst infectivity in chlorinated recreational water venues (e.g., pools).
227 rination for inactivating Cryptosporidium in chlorinated recreational water venues, but further studi
228 exyl-4-methoxycinnamate, and octocrylene, in chlorinated seawater swimming pools.
229 the transformation products of oxybenzone in chlorinated seawater swimming pools; especially that use
230 s showed that only octocrylene was stable in chlorinated seawater.
231 of the long term health effects of the lower-chlorinated, semi-volatile PCBs in the indoor environmen
232        Mutagenic potencies of samples from a chlorinated site correlated best with brominated haloace
233 advantage of this approach is the use of non-chlorinated solvent and small amounts of organic solvent
234                   These results suggest that chlorinated solvent bioattenuation rates could be impede
235 dy may also have implications for optimizing chlorinated solvent bioremediation.
236            1,2-Dichloroethane (1,2-DCA) is a chlorinated solvent classified as a probable human carci
237 O and D2O batch systems as a function of pH, chlorinated solvent concentration, Pd surface loading, P
238 tificially contaminated by a three component chlorinated solvent mixture (tetrachloroethene (PCE) 45
239 dation by bacterial pure cultures exposed to chlorinated solvent mixtures as well as in environmental
240 n, evidence that multiple pathways exist for chlorinated solvent reduction.
241 set of sites, there was little evidence that chlorinated solvent remedial efforts (e.g., chemical oxi
242 mplications of these findings for monitoring chlorinated solvent sites are discussed.
243                            Bioremediation at chlorinated solvent sites often leads to groundwater aci
244 ous film-forming foams (AFFFs) to extinguish chlorinated solvent-fueled fires has led to the co-conta
245 euterated) and nonlabeled isotopologues) and chlorinated solvents (trichloroethene, TCE, and cis-dich
246 ples collected from a site contaminated with chlorinated solvents and 1,4-dioxane.
247 ental pollutants like nitrate, hydrocarbons, chlorinated solvents and heavy metals.
248 study investigated the impacts of individual chlorinated solvents and their mixtures on aerobic 1,4-d
249 cles can contribute to the transformation of chlorinated solvents and various other contaminants into
250 ane bioremediation strategies at sites where chlorinated solvents are present as co-contaminants.
251 ved recalcitrance at groundwater sites where chlorinated solvents are present.
252 ion that abiotic natural attenuation (NA) of chlorinated solvents can be important has created demand
253 ng reactants for reductive dechlorination of chlorinated solvents due to high reaction rates and the
254 erovalent iron (Fe(0)) in the degradation of chlorinated solvents in subsurface environments is of in
255 e of the enhanced rate of degradation of the chlorinated solvents in the inoculated trees.
256 ation approaches for sites contaminated with chlorinated solvents requires a fundamental understandin
257 rile as the solvent, thus avoiding hazardous chlorinated solvents such as CCl4.
258 beneficial properties in comparison to other chlorinated solvents such as dichloroethane.
259 es used for the bioremediation of co-mingled chlorinated solvents such as trichloroethene (TCE).
260 ition of 1,4-dioxane biodegradation rates by chlorinated solvents was attributed to delayed ATP produ
261                   At sites where dioxane and chlorinated solvents were present, the median value of a
262 are a common photoisomerization mechanism in chlorinated solvents with notable differences in kinetic
263 drocarbons, single ring aromatics, terpenes, chlorinated solvents, formaldehyde, and acrolein.
264  bacterium involved in the bioremediation of chlorinated solvents, reveal homologous genes encoding a
265 s 1-7 exhibit moderate-to-good solubility in chlorinated solvents, such as 1,2-dichlorobenzene and ch
266  and groundwater contaminated with fuels and chlorinated solvents.
267 date carried out in non-donor hydrocarbon or chlorinated solvents.
268 l of an alkaline AA solution for remediating chlorinated solvents.
269 sheet conformations were shown to prevail in chlorinated solvents.
270 d oxygen and the co-occurrence of inhibiting chlorinated solvents.
271 ange of 8.6-51 g g(-1) and in agreement with chlorinated substances.
272                          Additionally, lower chlorinated substituted PCBs had a higher percentage con
273 ed to a stronger interaction between MTO and chlorinated surface regions, as well as extensive deplet
274  absorption in a standard diet, as well as a chlorinated tap water sample.
275 roperty evaluation of several brominated and chlorinated tetraazapentacenes.
276 o-beta-aminoketone intermediates featuring a chlorinated tetrasubstituted stereocenter can be isolate
277           Indoor air PCBs are generally less chlorinated than PCBs that are absorbed via the diet, or
278 rmation of chlorinated dibenzothiophenes and chlorinated thianthrenes that could be applied to predic
279 r, concerns about the potential formation of chlorinated transformation products require an understan
280 n, the antimicrobial agent in handsoaps, and chlorinated triclosan derivatives (CTDs, formed during d
281 kidneys, levels of HOCl-derived oxidized and chlorinated tryptophan residues W(28) and W(192) are sig
282 acute coronary syndrome had higher levels of chlorinated tyrosine 192 and oxidized methionine 148 com
283                                    Levels of chlorinated tyrosine and oxidized methionine associated
284    The absence of lysine increased yields of chlorinated tyrosines and decreased yields of brominated
285 HOCl is present, the SiF fluorophores become chlorinated, via an intermediate halohydrin, resulting i
286 oroaldehydes, kinetic resolutions of complex chlorinated vinyl epoxide intermediates, and Z-selective
287  excess of 4% decreased the decomposition of chlorinated VOCs as a result of ozone and nitrogen oxide
288 lted in increasing the removal efficiency of chlorinated VOCs in plasma.
289 tive field site contaminated with a range of chlorinated volatile organic compounds (cVOC).
290 atment aimed predominantly at remediation of chlorinated volatile organic compounds (cVOCs) and perfl
291                             The migration of chlorinated volatile organic compounds from groundwater
292                             The migration of chlorinated volatile organic compounds from groundwater
293 ted, e.g., chloromethane (CH3Cl), and higher chlorinated VOX compounds such as trichloromethane (CHCl
294 ing may lead to higher DBP concentrations in chlorinated water with lower distribution system tempera
295 se in concentration was only notable for the chlorinated water with very high chlorine dose.
296 levels of NTM in chloraminated water than in chlorinated water.
297 ichlorophenol, triclosan, and bisphenol A in chlorinated waters containing I(-).
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.

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