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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
6 ancomycin, exclusive conversion of vicinally chlorinated alkanes, and tolerance to short-term oxygen
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
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
21 CNs), polychlorinated dibenzofurans (PCDFs), chlorinated and mixed brominated/chlorinated anthracenes
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
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
37 wo types of PCDD/F precursors, involving all chlorinated benzenes (CBz) and chlorinated phenols (CPh)
42 und to be strongly dependent on the ratio of chlorinated benzenes to chlorinated phenols and oxygen c
45 In this study, we describe the screening for chlorinated biomolecules by the use of mass isotope rati
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
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
55 vided information on the bioaccumulation for chlorinated compounds as well as for some polycyclic aro
57 ic isotope analysis (CSIA) is unsuitable for chlorinated compounds such as trichloroethene (TCE) and
59 nowledge, this is the first time such highly chlorinated compounds were studied with the LC-IRMS syst
61 he main precursors, namely acylglycerols and chlorinated compounds, on the formation yield of MCPD es
65 types were dominated by PCB 28/31 and higher-chlorinated congeners in both groups reflecting rapid me
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
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
75 to encode a new pathway to generate a novel chlorinated coumarin "non-natural" product in E. coli.
77 rine bacterial natural products containing a chlorinated cyclopenta[a]indene core of suspected enediy
80 in drinking water may react with BPA to form chlorinated derivatives (ClxBPA), which have indeed been
82 s of these complexes and their corresponding chlorinated derivatives have been characterized by NMR s
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
98 tion of methyltrioxorhenium (MTO) onto these chlorinated domains serves to activate it as a low tempe
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
103 etailed parts of our analysis are focused on chlorinated drugs as a function of approval date, diseas
106 o a change in the ratio of electron donor to chlorinated electron acceptor in continuously stirred ta
109 dehalorespiration provided a good fit to the chlorinated ethene concentrations measured in a cocultur
111 We collected 95 groundwater samples across 6 chlorinated ethene-contaminated sites and searched for r
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
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
123 one bacteria for reductive dechlorination of chlorinated ethenes to nontoxic ethene in contaminated a
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
128 ta(13)C were from 2 to 60 mug/L (MTBE, BTEX, chlorinated ethenes, and benzenes) and 60-97 mug/L for d
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
140 HO-PCBs profile after weight loss with lower chlorinated HO-PCBs increasingly gaining importance.
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
145 mudstone; however, the carbon source for the chlorinated hydrocarbons is not definitively of martian
147 on and CSIA profiles were determined for the chlorinated hydrocarbons that had diffused into the clay
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
155 3 min(-1); when a reductant was added, these chlorinated intermediates were then reduced back to BMAA
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
162 xy-brominated diphenyl ethers (MeO-BDEs) and chlorinated methyl- and dimethyl bipyrroles (MBPs and DM
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
168 bited a low or nondetectable toxicity, lower-chlorinated OH-PCBs significantly inhibited the germinat
171 ool/spa waters were 1.8x more mutagenic than chlorinated ones; spa waters were 1.7x more mutagenic th
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
177 efore, utilizing enzymes in the synthesis of chlorinated organic compounds is important, and providin
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
191 analyte signal of a polychlorinated alkanes (chlorinated paraffins) technical mixture that contains 7
193 ely revolatilized after deposition, a higher-chlorinated PCB congener is predominantly transferred to
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
206 ngest CL was produced not by the most-highly chlorinated pentachlorophenol (PCP), but rather by the l
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
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
221 coides mccartyi strain JNA detoxifies highly chlorinated polychlorinated biphenyl (PCB) mixtures via
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
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
229 the transformation products of oxybenzone in chlorinated seawater swimming pools; especially that use
231 of the long term health effects of the lower-chlorinated, semi-volatile PCBs in the indoor environmen
233 advantage of this approach is the use of non-chlorinated solvent and small amounts of organic solvent
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
241 set of sites, there was little evidence that chlorinated solvent remedial efforts (e.g., chemical oxi
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
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.
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
256 ation approaches for sites contaminated with chlorinated solvents requires a fundamental understandin
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
262 are a common photoisomerization mechanism in chlorinated solvents with notable differences in kinetic
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
273 ed to a stronger interaction between MTO and chlorinated surface regions, as well as extensive deplet
276 o-beta-aminoketone intermediates featuring a chlorinated tetrasubstituted stereocenter can be isolate
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
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
290 atment aimed predominantly at remediation of chlorinated volatile organic compounds (cVOCs) and perfl
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
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
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