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1 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate).
2 ntration range of 6.3x10(-7)-1.0x10(-3)mol/L perchlorate.
3 tate > methanesulfonate > trifluoroacetate > perchlorate.
4 he supporting electrolyte tetrabutylammonium perchlorate.
5 ion-exchange brines or resins exhausted with perchlorate.
6  different from those of the simple mercuric perchlorate.
7 cyl-3,3,3',3'-tetramethylindodicarbo-cyanine perchlorate.
8 sensitivity, or they possess toxic metals or perchlorate.
9 unambiguous methods are needed for measuring perchlorate.
10 de cattle with a degree of refractoriness to perchlorate.
11 ormation allowing the indefinite cycling for perchlorate.
12  everyone in the United States is exposed to perchlorate.
13 thus enabling prior pre-concentration of the perchlorate.
14 e approximately bromide > acetate > iodide > perchlorate.
15                      The addition of lithium perchlorate (1-2 equiv) as an additive to the alkaloid c
16 otosensitized by 3-cyano-N-methylquinolinium perchlorate (3-CN-NMQ(+)) has been investigated by stead
17 es sensitized by 3-cyano-N-methylquinolinium perchlorate (3-CN-NMQ(+)ClO4(-)).
18 o having two electron acceptors (nitrate and perchlorate), (3) competition between nitrate and perchl
19 wer concentrations (4.6(+/-1.3)x10(-10)mol/L perchlorate), a column packed with 70mg of sodium 2,5,8,
20 ilure to adequately account for the risks of perchlorate-a well-characterized endocrine-disrupting ch
21 shifts its donated H-bonds between water and perchlorate acceptors by means of large, prompt angular
22 chemical analysis revealed a relatively high perchlorate affinity (Km = 6 mum) and a characteristic s
23                   Treatment of 2 with silver perchlorate afforded a silver(I)/iron(III) heterodimetal
24 phoric or perchloric acid with 150 mM sodium perchlorate) affording excellent separation for all samp
25 ally available 9-mesityl-10-methylacridinium perchlorate and 2-phenylmalononitrile as a redox-cycling
26 ions between human exposure to low levels of perchlorate and adverse health effects.
27                               Respiration of perchlorate and chlorate [collectively, (per)chlorate] w
28 bility to grow by dissimilatory reduction of perchlorate and chlorate [denoted (per)chlorate].
29 loromonas aromatica abolished growth in both perchlorate and chlorate but not growth in nitrate, indi
30 f the corresponding porphyrin-manganese(III) perchlorate and chlorate complexes, respectively, permit
31 ons were identified between increasing log10 perchlorate and decreasing total thyroxine (T4) [regress
32 esults showed that strain P4B1 could utilize perchlorate and grow in the presence of 1.8% to 10.2% Na
33                                  The fate of perchlorate and its effect on animal health were studied
34 n electropolymerization (tetrabuthylammonium perchlorate and lithium perchlorate) has emerged demonst
35 pensions indicated that strain P4B1 had both perchlorate and nitrate reduction enzymes.
36 n were the most important mechanisms for the perchlorate and nitrate treatments, respectively, in the
37                                         When perchlorate and nitrate were both present, nitrate reduc
38         When the culture was exposed to both perchlorate and nitrate, the nitrate reduction enzyme ac
39                                              Perchlorate and other hydrophobic ions can be measured w
40 )6](3-), which was formed from chromium(III) perchlorate and pH adjusted with ethylenediamine.
41 sed to evaluate associations between urinary perchlorate and serum thyroid hormone concentrations in
42                            Mixing copper(II) perchlorate and sodium iodide solutions results in coppe
43 te, chloride, nitrate, etc.) and <10(-4) for perchlorate and thiocyanate are obtained.
44 uction of inorganic byproducts (chlorate and perchlorate) and indicator organic byproducts (haloaceti
45 ate, methanesulfonate, trifluoroacetate, and perchlorate), and the apparent elution strength was foun
46 barium salts (acetate, trifluoroacetate, and perchlorate), and the thermodynamic parameters governing
47 ransport model of a new candidate inhibitor, perchlorate, and compared it with the commonly used inhi
48 solutions of phosphate buffer saline, sodium perchlorate, and in choline chloride plus oxalic acid, u
49   We investigated the formation of chlorate, perchlorate, and organic chlorination byproducts (OCBPs)
50 butyl-, tetrahexyl-, and tetraoctylammonium, perchlorate, and tetraphenylborate).
51 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate; and 3) TRPV1 currents and electrophysiologi
52 is work, we used a case study focused on the perchlorate anion (ClO4(-)) to highlight the value of th
53 ted is that the counterion, in this case the perchlorate anion, competes with water molecules for the
54 zation of the CS state, whereas weakly bound perchlorate anions gave no improvement.
55 f the chloride receptor is templated by five perchlorate anions.
56 used on developing replacements for ammonium perchlorate (AP), a primary choice for solid rocket and
57 ure of a mimetic of Martian water, magnesium perchlorate aqueous solution at its eutectic composition
58                          Trace quantities of perchlorate are being increasingly detected in food and
59 uffered aqueous solution, whereas iodide and perchlorate are ineffective with electrothermal supercha
60 s and inhibition coefficients of nitrate and perchlorate are optimized by fitting data from experimen
61 naceous chondrite Murchison with chloride or perchlorate as chlorine source and confirm unequivocally
62 trile containing 0.1 M tetra-n-butylammonium perchlorate as electrolyte.
63 ounterion and (2.64 +/- 0.88) x 102 s-1 with perchlorate as the counterion.
64 trans-cis isomerization, using cresyl violet perchlorate as the sensitizer, also led to similar resul
65 s invoked herein, to the potential origin of perchlorates as found on Mars.
66 lectrochemical detection of "redox-inactive" perchlorate at a nanomolar level without its electrolysi
67 s contaminated from an industrial plant with perchlorate at levels near the 2007 California regulator
68 irradiated with a simulated Martian UV flux, perchlorates become bacteriocidal.
69 . L(-1) on TDIROF) resulting in chlorate and perchlorate being the dominant CBPs (>90% of initial chl
70 es has fueled much speculation that flows of perchlorate brines might be the cause of the observed ch
71 (N(CH3)3)Br) allows for the determination of perchlorate by electrospray ionization mass spectrometry
72  mechanisms: simultaneous use of nitrate and perchlorate by PRB and competition for H(2), the same re
73 ite, tellurate, tellurite, nitrate, nitrite, perchlorate, chlorate, monofluorophosphate, vanadate, mo
74 crA expression regardless of the presence of perchlorate, chlorate, or nitrate.
75 d cation sulfates, phosphates, and chlorides-perchlorates-chlorates), and has minor TiO2 and Fe2O3T o
76                       Formation of chlorate, perchlorate, chlorinated, and brominated organics may co
77 s that occur inherently as oxo-anions (e.g., perchlorate, chromate, arsenate, pertechnetate, etc.) or
78 s sensitivity to the environmental pollutant perchlorate (ClO(4)(-)) and its implication in radioiodi
79                                              Perchlorate (ClO(4)(-)) competitively inhibits the uptak
80                                              Perchlorate (ClO(4)(-)) is a well known competitive inhi
81                            Recent reports of perchlorate (ClO(4)(-)) production-a well-known thyroid
82 fRs) designed to reduce nitrate (NO3(-)) and perchlorate (ClO4(-)) in contaminated groundwater.
83 ly 10 mM of dissolved salts with 0.4 to 0.6% perchlorate (ClO4) by mass leached from each sample.
84 iously developed and shown to reduce aqueous perchlorate (ClO4-) with H2 at a rate approximately 100
85                               Mining-related perchlorate [ClO4(-)] in the receiving environment was i
86            A series of ligand-copper(II) bis-perchlorate complexes were synthesized, characterized, a
87      For the same samples, the corresponding perchlorate concentration ratio was 1.37 (difference sig
88                           The median urinary perchlorate concentration was 6.5 mug/L, about two times
89 nt for assessing the environmental impact on perchlorate concentrations in milk and potential for rel
90                                              Perchlorate concentrations in the Great Lakes range from
91 fferent combinations of influent nitrate and perchlorate concentrations.
92  is required for the assessment of nanomolar perchlorate contamination in drinking water as an emergi
93                  There is great concern that perchlorate contamination may be far more widespread tha
94                                              Perchlorate contamination of water represents a serious
95 ements showing the decomposition of ammonium perchlorate, copper oxide nanoparticles, and sodium azot
96 tetrazine and triazolo-tetrazine ligands and perchlorate counteranions have been achieved.
97 /Na(+) ratio of approximately 0.11 optimized perchlorate degradation and cell growth.
98 explained by the presence of (36)Cl-enriched perchlorate deposited during the period of elevated atmo
99 as a likely repository of recent atmospheric perchlorate deposition.
100                      Selective and sensitive perchlorate detection was obtained by monitoring the 35C
101 hod using contact conductivity detection for perchlorate determination.
102 with dioctadecyl tetramethylindocarbocyanine perchlorate (DiI) and in situ hybridization using cloned
103 octadecyl-3,3,3'-tetramethylindocarbocyanine perchlorate (DiI) axonal labeling was used to define the
104 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate (DiI) bilaterally to nodose ganglia.
105 odecyl-3,3,3',3'-tetramethylindocarbocyamine perchlorate (DiI) labeling suggested reduced MET-IR neur
106 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate (DiI) was inserted into whole-mounted transg
107 decyl-3,3,3',3'-tetramethylindocarbo-cyanine perchlorate (DiI) was used to label selectively vagal pr
108 tadecyl-3,3,3'3'-tetramethylindocarbocyanine perchlorate (DiI) within authentic RPLC porous silica pa
109 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate (DiI), a lipophilic carbocyanine dye, which
110 odecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate (DiI), ranging in concentration from 1 to 30
111 adecyl-3,3,3'3'-testramethylindocarbocyanine perchlorate (DiI; n=49, 2x10(6) cells each) were injecte
112 cyl-3,3,3',3'-tetramethylindotricarbocyanine perchlorate [DiI], DiD, DiR, and PKH26) can give rise to
113 (ECFP-Mem) and 3'-dioctadecyloxacarbocyanine perchlorate [DiOC(18)(3)], were used to distinguish DHE
114 nmental impacts of conventional and emerging perchlorate drinking water treatment technologies were a
115    Thyroid hormones and moderate exposure to perchlorate during pregnancy in women in Southern Califo
116 ort of Na(+) and the environmental pollutant perchlorate electroneutrally, G93T/N/Q/E/D NIS, striking
117 tatively identified as porphyrin-iron(V)-oxo perchlorates, electronic isomers (or valence tautomers)
118                     This ion associates with perchlorate, even in the gas phase.
119 lications for public health given widespread perchlorate exposure and the importance of thyroid hormo
120  method to analyze neonatal DBS will improve perchlorate exposure assessments of this susceptible pop
121     These results suggest that environmental perchlorate exposures may affect thyroid hormone product
122            In addition, isotopic analyses of perchlorate extracted from groundwater and surface water
123 ed in lactating cows, ruminally infused with perchlorate for 5 weeks.
124 tion rates demonstrate greater inhibition of perchlorate formation (IPF).
125 ses ((37)Cl/(35)Cl and (18)O/(17)O/(16)O) of perchlorate from known synthetic and natural sources rev
126                                Resolution of perchlorate from more abundant ions was achieved using z
127 ding the use of these surfactants to resolve perchlorate from other anions, are discussed in this wor
128 tion resembling that measured for indigenous perchlorate from preindustrial groundwaters of the weste
129                        delta(37)Cl values of perchlorate from the Great Lakes range from +3.0 per tho
130        Here, the authors show that magnesium perchlorate has a major impact on water structure in sol
131                                              Perchlorate has been detected recently in a variety of s
132                                  Great Lakes perchlorate has mass-independent oxygen isotopic variati
133 (tetrabuthylammonium perchlorate and lithium perchlorate) has emerged demonstrating its effect on sen
134        Both natural and synthetic sources of perchlorate have been identified in water samples from s
135                                  Nitrate and perchlorate have considerable use in technology, synthet
136                                              Perchlorates have been identified on the surface of Mars
137 , benzoate, perrhenate, nitrate, triflimide, perchlorate, hexafluorophosphate, hydrogen sulfate, meth
138        The dissolved components are nitrate, perchlorate, hydrogen (H(2)), substrate-utilization-asso
139 ron(IV) tetramesitylporphyrin radical cation perchlorate in acetonitrile were measured in single turn
140  ng/mL) was sufficiently sensitive to detect perchlorate in all human urine samples evaluated to date
141 radiation of 1,2-cyclopenta-fused pyridinium perchlorate in aqueous base promotes a remarkably regios
142 chlorate reducer Azospira suillum PS grew on perchlorate in co-culture, but not individually.
143                               Measurement of perchlorate in DBS indicated good precision (relative st
144 y to give low detection limits of 0.2-0.5 nM perchlorate in deionized water, commercial bottled water
145 ecently proposed a health advisory limit for perchlorate in drinking water of 15 parts per billion (p
146  has been developed for the determination of perchlorate in drinking water.
147 or routine online monitoring applications of perchlorate in drinking water.
148 nomical in production laboratory analysis of perchlorate in environmental water and soil samples.
149 simpler alternative for the determination of perchlorate in foods, nowadays only allowed by sophistic
150 ed isotope fractionation, as illustrated for perchlorate in groundwater.
151 nsitive and selective method for quantifying perchlorate in human urine using ion chromatography coup
152   We report the capture of ppm-level aqueous perchlorate in record capacity and kinetics via the comp
153 hlorate, we developed a method for analyzing perchlorate in the dried blood spots (DBS) of newborns.
154    The stable isotopic results indicate that perchlorate in the Great Lakes is dominantly of natural
155 are consistent with an atmospheric origin of perchlorate in the Great Lakes.
156 el for simultaneous reduction of nitrate and perchlorate in the H(2)-based membrane biofilm reactor (
157 ed for simultaneous reduction of nitrate and perchlorate in the H(2)-based membrane biofilm reactor.
158 es caused by the recently discovered ~1 wt % perchlorate in the Martian soil.
159 s carried out chemically using thianthrenium perchlorate in the presence of anisole it was shown to p
160 ars, where the existence of large amounts of perchlorate in the soil needs to be confirmed.
161                         The mass transfer of perchlorate in the thin-layer liquid membrane and aqueou
162 m determinations of the emergent contaminant perchlorate in vegetable matrices down to nanomolar conc
163 new method was developed for the analysis of perchlorate in water by using reversed-phase liquid chro
164 heterogeneous catalysts for the reduction of perchlorate in water with dihydrogen have been prepared
165  the Phoenix Lander of calcium and magnesium perchlorates in Martian soil samples has fueled much spe
166 es show that the presence of lanthanide(III) perchlorate increases the mechano-responsiveness of the
167 rchlorate levels were highly correlated with perchlorate intake, but milk iodine was unaffected, and
168 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate (internal reference dye), and 14 mmol/kg sod
169 ental concerns resulting from the release of perchlorate into groundwater systems [corrected].
170 ar shaped potentiometric sensor selective to perchlorate ion was constructed with a PVC membrane cont
171 vesicle interior is determined relative to a perchlorate-ion internal standard, preloaded into the ve
172                                              Perchlorate is a goitrogenic anion that competitively in
173                                              Perchlorate is a persistent and mobile contaminant in th
174                                              Perchlorate is an important ion on both Earth and Mars.
175 e cultured in milk, spiked with perchlorate, perchlorate is consumed.
176 he toluene phase and when tetrabutylammonium perchlorate is introduced into the water phase, implying
177 nce significant, p < 0.001), indicating that perchlorate is lost.
178 d a good fit to the data, which suggest that perchlorate is more effective than nitrate on a per mole
179                                              Perchlorate is, thus, detected as DClO(4)(+) in the posi
180 enzymatic step in the bacterial reduction of perchlorate, is catalyzed by perchlorate reductase.
181 n is 4.13 +/- 0.09 (SEM); in the presence of perchlorate it is 4.35 +/- 0.09 (SEM).
182                                              Perchlorate (K(i,app) = 0.6 +/- 0.05 microM) and iodide
183 ich has a relatively much lower affinity for perchlorate (Km = 1.1 mm) and no substrate inhibition.
184 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate) labeling to assess the pathfinding of commi
185 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate LDL cell-based assays on the stable knockdow
186 on tandem mass spectrometry to measure blood perchlorate levels in DBS samples as low as 0.10 ng/mL.
187 pport the utility of this method to quantify perchlorate levels in DBS samples.
188                                         Milk perchlorate levels were highly correlated with perchlora
189                             The triflate and perchlorate ligands tend to stabilize the quintet state
190 ditions (H(2) pressure, nitrate loading, and perchlorate loading) affect nitrate and perchlorate remo
191 rtant operating conditions (nitrate loading, perchlorate loading, and H(2) pressure) affect nitrate a
192  complex with 18-crown-6 in both nitrate and perchlorate media.
193 dex grains, visualized in a weakly adsorbing perchlorate medium, show that there is higher activity o
194  the internal standard oxygen-labeled sodium perchlorate (NaCl18O4).
195        After 14 days of incubation in sodium perchlorate (NaClO4) or perchloric acid (HClO4) solution
196 e been identified in water samples from some perchlorate occurrences in the United States by the isot
197 al effects of low environmental exposures to perchlorate on thyroid function.
198 artian surface being converted to CH3Cl with perchlorate or chloride in Martian soil.
199           MLHE-1 was unaffected by magnesium perchlorate or low atmospheric pressure (10 mbar).
200 nes can transfer metal cations with picrate, perchlorate, or chloride counterions from an aqueous sol
201 E), dioctadecyl-tetramethylindo carbocyanine perchlorate, or chloromethyl tetramethylrhodamine.
202 een developed without the need for barium or perchlorate oxidizers.
203 dobacteria are cultured in milk, spiked with perchlorate, perchlorate is consumed.
204                        Nitrate, thiocyanate, perchlorate, perfluorooctanoic acid (PFOA), halogenated
205                             MOCA can use the perchlorate present in the Martian soil to its advantage
206 , wild-type PDA and a Deltacld mutant of the perchlorate reducer Azospira suillum PS grew on perchlor
207  suggested that competition by heterotrophic perchlorate reducers and direct inhibition by nitrite pr
208 ntation, and MFP is tolerated by nitrate and perchlorate reducing microorganisms.
209    Perchlorate reduction and accumulation of perchlorate-reducing bacteria (PRB) in the biofilm are a
210 ial group, i.e., denitrifying bacteria (DB), perchlorate-reducing bacteria (PRB), and sulfate-reducin
211                                        While perchlorate-reducing bacteria (PRB), assayed by qPCR tar
212                                Salt-tolerant perchlorate-reducing bacteria can be used to regenerate
213 totrophic denitrifying bacteria, autotrophic perchlorate-reducing bacteria, heterotrophic bacteria, i
214                              A salt-tolerant perchlorate-reducing Marinobacter vinifirmus strain P4B1
215                                              Perchlorate-reducing microorganisms employ a separate en
216                                              Perchlorate reductase (PcrAB), a specialized member of t
217                           The genes encoding perchlorate reductase (pcrABCD) in two Dechloromonas spe
218                            The separation of perchlorate reductase as an activity distinct from chlor
219  of the DMSO reductase family indicated that perchlorate reductase forms a monophyletic group separat
220 um bifidum include perchlorate reduction via perchlorate reductase.
221 al reduction of perchlorate, is catalyzed by perchlorate reductase.
222                                              Perchlorate reduction and accumulation of perchlorate-re
223 ading, and H(2) pressure) affect nitrate and perchlorate reduction and biomass distribution in these
224 e difficult to conclude definitively whether perchlorate reduction does or does not occur.
225 lorate), (3) competition between nitrate and perchlorate reduction for the same resources in the PRB:
226                                 Importantly, perchlorate reduction occurred even in the presence of 5
227 ts of Na(+) and Mg(2+) concentrations on the perchlorate reduction rate of P4B1.
228  the pcrABCD genes play a functional role in perchlorate reduction separate from nitrate reduction.
229 pathways for Bifidobacterium bifidum include perchlorate reduction via perchlorate reductase.
230 to the culture showed significant effects on perchlorate reduction when perchlorate was the sole elec
231 ral insight into the mechanism of biological perchlorate reduction, a critical component of the chlor
232     Lower NaCl concentrations allowed faster perchlorate reduction.
233                          With less stringent perchlorate regulatory limits, ion exchange technologies
234                         Existing methods for perchlorate remediation are hampered by the common co-oc
235 -based technologies could prove effective at perchlorate removal from water cocontaminated with nitra
236              In this work, the potential for perchlorate removal using cell-free bacterial enzymes as
237 loading of >0.6 g N/m(2)-d begins to inhibit perchlorate removal, as the competition effects become d
238  loading (<0.1 g N/m(2)-d) slightly promotes perchlorate removal, because of the beneficial effect fr
239 ological reduction) and emerging (catalysis) perchlorate-removal technologies was evaluated through a
240  and perchlorate loading) affect nitrate and perchlorate removals: (1) competition for H(2), (2) prom
241 amily, catalyzes the first step of microbial perchlorate respiration, but little is known about the b
242 odecyl-3,3,3',3'-tetramethylindocarbecyanine perchlorate) retrograde labelling and intracellular elec
243                                       Sodium perchlorate salt (NaClO(4)) is commonly used as an inter
244  atmosphere.Significant amounts of different perchlorate salts have been discovered on the surface of
245 e found that the host rotaxanes transfer the perchlorate salts poorly when compared to B18C6, but the
246      Additionally, the prepared oxadiazolium perchlorate salts showed excellent moisture stability, a
247 the exchange, forming silver 4,4'-bipyridine perchlorate (SBP).
248                                          The perchlorate-selective electrode is based on the submicro
249  with periodic regeneration using brines and perchlorate-selective IX without regeneration) at an exi
250 selective IX, which shows higher impact than perchlorate-selective IX.
251 adecyl-3,3,3'3'-tetramethylindo-carbocyanine perchlorate showed that pCRLPs are taken up at a faster
252 iodide, nitrate, chloride, dihydrophosphate, perchlorate) showed the highest response to KI.
253 ries have generated considerable interest in perchlorate source identification.
254 adioactive isotope (36)Cl were used to trace perchlorate sources and behavior in the Laurentian Great
255 r demonstrate the feasibility of identifying perchlorate sources in contaminated environments on the
256 f aluminate and aluminosilicate species with perchlorate species that most likely inhibit the formati
257 bservation, tetramethylrhodamine ethyl ester perchlorate staining revealed that mitochondrial membran
258 ion (2 g/L) with different anions (chloride, perchlorate, sulfate, carbonate, nitrate), anion concent
259 these studies were conducted using nitrate-, perchlorate-, sulfate-, and chloride-based electrolyte s
260  hexafluorophosphate, tetrafluoroborate, and perchlorate supporting electrolytes prevent the encapsul
261 tion rate constants, kf, for the nitrate and perchlorate systems are (3.82 +/- 0.89) x 107 and (5.92
262 MeCN containing 0.10 M tetra-n-butylammonium perchlorate (TBAP), the complex displayed a reversible,
263 omethanesulfonyl)imide, hexafluorophosphate, perchlorate, tetrafluoroborate, and dicyanamide on the s
264 t sensitive analytical methods for detecting perchlorate, that is, ion chromatography coupled with a
265                                              Perchlorate, thiocyanate, and nitrate are sodium/iodide
266                               At high doses, perchlorate, thiocyanate, and nitrate inhibit iodide upt
267                         Thyroid antagonists (perchlorate, thiocyanate, and nitrate) and childhood gro
268 osure group (3.6, 626, and 500 mg/gC, median perchlorate, thiocyanate, and nitrate, respectively) gir
269  exposure (9.6, 2,343, and 955 mg/gC, median perchlorate, thiocyanate, and nitrate, respectively) had
270 ones and anti-thyroid antibodies and urinary perchlorate, thiocyanate, nitrate, and iodide concentrat
271 e positive free energies of hydration (e.g., perchlorate, thiocyanate, nitrate, etc.).
272 ent dye and tetramethylrhodamine-ethyl-ester-perchlorate (TMRE) and imaged by confocal microscopy.
273 th the dye tetramethylrhodamine methyl ester perchlorate (TMRM) to evaluate the kinetics of the mitoc
274                             The reduction of perchlorate to chlorite, the first enzymatic step in the
275 thoxyethoxymethyl-3-pivaloxymethylpyridinium perchlorate to generate a bicyclic-aziridine intermediat
276  addition of hexafluorophosphate could cause perchlorate to shift from capsule 2 to capsule 1 and tri
277 them are chemically oxidized with copper(II) perchlorate to the respective cation species, which show
278 gen peroxide, act in synergy with irradiated perchlorates to cause a 10.8-fold increase in cell death
279 nstitution on receipt of one anionic signal (perchlorate) to create a tight binding pocket for anothe
280 and could enhance the efficacy of nitrate or perchlorate treatments.
281 alpha-D-glucosyl)-3-pivaloxymethylpyridinium perchlorate undergoes photocyclization to generate separ
282 ation, high production rates of chlorate and perchlorate (up to approximately 4 and 25 muM) made them
283  nanoparticles is reported in aqueous sodium perchlorate using the nanoimpact method.
284                       The (36)Cl/Cl ratio of perchlorate varies widely from 7.4 x 10(-12) (Lake Ontar
285 ecyl-3,3,3',3'-tetramethylindodicarbocyanine perchlorate)-VLDL binding to cells, and shed syndecan-1
286 e field effect transistor, but ethylviologen perchlorate was added to provide a redox counter-reactio
287  reduction did not start significantly until perchlorate was below 100 mg/L.
288                                              Perchlorate was detectable in 100% of the DBS collected
289 e provide evidence that up to 80% of dietary perchlorate was metabolized, most likely in the rumen, w
290                                              Perchlorate was only formed at higher specific charges (
291  of the batch experiments, the production of perchlorate was prevented by competing active chlorine a
292                                              Perchlorate was quantified using a stable isotope-labele
293                                              Perchlorate was removed by the soluble protein fraction
294 ficant effects on perchlorate reduction when perchlorate was the sole electron acceptor.
295 urrounding in utero and neonatal exposure to perchlorate, we developed a method for analyzing perchlo
296  concerns surrounding widespread exposure to perchlorate, we developed a sensitive and selective meth
297 r Green and tetramethylrhodamine-ethyl-ester-perchlorate were examined live with confocal microscopy.
298 adecyl-3,3,3',3'-tetramethylindocarbocyanine perchlorate, which preferentially incorporates into orde
299 adecyl -3,3,3,3-tetramethyl-indocarbocyanine perchlorate with acetylated low-density lipoprotein (DiI
300  isotope-labeled internal standard ((18)O(4)-perchlorate) with excellent assay precision (coefficient

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