PMID-sentid	Pub_year	Sent_text	compound_name	comp_offset	prot_official_name	organism	prot_offset
18089729-10	2008	In in vitro experiments, ClO(2) denatured viral envelope proteins (haemagglutinin and neuraminidase) that are indispensable for infectivity of the virus, and abolished infectivity.	chlorine dioxide	25-31	neuraminidase 1	Homo sapiens	67-99
17397139-3	2007	Using bovine serum albumin and glucose-6-phosphate dehydrogenase of Saccharomyces cerevisiae as model proteins, here I demonstrate that the antimicrobial activity of ClO2 is attributable primarily to its protein-denaturing activity.	chlorine dioxide	166-170	glucose-6-phosphate dehydrogenase	Saccharomyces cerevisiae S288C	31-64
17397139-7	2007	The enzymatic activity of glucose-6-phosphate dehydrogenase decreases to 10% within 15 s of treatment with 10 microM ClO2.	chlorine dioxide	117-121	glucose-6-phosphate dehydrogenase	Saccharomyces cerevisiae S288C	26-59
14769425-3	2004	In the experiments conducted at the pilot plant the sand filtered water (MWI) and ozonated/biofiltrated water (BAF) were oxidised with ClO2.	chlorine dioxide	135-139	BAF nuclear assembly factor 1	Homo sapiens	111-114
17668816-4	2007	In the effluent and pulp samples from mills where chlorine dioxide was used as a bleaching agent, the 2,3,7,8-TCDD congener ranged from below the detection limit 0.05 to 0.12 ngL(-1)/ngg(-1).	chlorine dioxide	50-66	leucine rich repeat containing 4C	Homo sapiens	175-181
17668816-4	2007	In the effluent and pulp samples from mills where chlorine dioxide was used as a bleaching agent, the 2,3,7,8-TCDD congener ranged from below the detection limit 0.05 to 0.12 ngL(-1)/ngg(-1).	chlorine dioxide	50-66	transcriptional adaptor 3	Homo sapiens	183-189
17180964-9	2006	Although the use of alternative disinfectants (ozone, chlorine dioxide, and chloramines) minimized the formation of the four regulated THMs, trihalogenated HAAs, and total organic halogen (TOX), several priority DBPs were formed at higher levels with the alternative disinfectants as compared with chlorine.	chlorine dioxide	54-70	thymocyte selection associated high mobility group box	Homo sapiens	189-192
15497841-6	2004	Ozonation and chlorination with ClO2 removed both 4-NP and BPA below detection limits, corresponding with AOX and estrogenic activity.	chlorine dioxide	32-36	acyl-CoA oxidase 1	Homo sapiens	106-109
14562931-2	2003	The optimal pH range for generation of C1O2 by contacting Cl2 (g) directly with ClO2- solution is within pH 1.35-1.94, particularly within pH 1.35-4.00 only if minimizing the formation of Cl2.	chlorine dioxide	80-84	endogenous retrovirus group W member 5	Homo sapiens	58-61
14562931-2	2003	The optimal pH range for generation of C1O2 by contacting Cl2 (g) directly with ClO2- solution is within pH 1.35-1.94, particularly within pH 1.35-4.00 only if minimizing the formation of Cl2.	chlorine dioxide	80-84	endogenous retrovirus group W member 5	Homo sapiens	188-191
14562931-3	2003	It is unachievable to synthesize pure ClO2 from the reaction of Cl2 and ClO2- .	chlorine dioxide	38-42	endogenous retrovirus group W member 5	Homo sapiens	64-67
14562931-5	2003	ClO2 could be relatively stable if not disproportionate into ClO3-, coexisting with ClO2- (p(epsilon) 17.63 and pH > 9.68), Cl2(pH < or = 0.92) or Cl- (pH 0.92-9.68).	chlorine dioxide	0-4	endogenous retrovirus group W member 5	Homo sapiens	127-130
14562931-7	2003	As the acidity decreases, ClO2 disproportionates into ClO3- and Cl2.	chlorine dioxide	26-30	endogenous retrovirus group W member 5	Homo sapiens	64-67
12425638-1	2002	The disproportionation of chlorine dioxide in basic solution to give ClO2- and ClO3- is catalyzed by OBr- and OCl-.	chlorine dioxide	26-42	leptin receptor	Homo sapiens	101-104
12425638-1	2002	The disproportionation of chlorine dioxide in basic solution to give ClO2- and ClO3- is catalyzed by OBr- and OCl-.	chlorine dioxide	69-73	leptin receptor	Homo sapiens	101-104
12425638-4	2002	In the proposed mechanisms, electron transfer from OX- to ClO2(k1OBr- = 2.05 +/- 0.03 M(-1) x s(-1) for OBr(-)/ClO2 and k1OCl-= 0.91 +/- 0.04 M(-1) x s(-1) for OCl-/ClO2) occurs in the first step to give OX and ClO2-.	chlorine dioxide	58-62	leptin receptor	Homo sapiens	65-68
12425638-4	2002	In the proposed mechanisms, electron transfer from OX- to ClO2(k1OBr- = 2.05 +/- 0.03 M(-1) x s(-1) for OBr(-)/ClO2 and k1OCl-= 0.91 +/- 0.04 M(-1) x s(-1) for OCl-/ClO2) occurs in the first step to give OX and ClO2-.	chlorine dioxide	111-115	leptin receptor	Homo sapiens	65-68
12425638-4	2002	In the proposed mechanisms, electron transfer from OX- to ClO2(k1OBr- = 2.05 +/- 0.03 M(-1) x s(-1) for OBr(-)/ClO2 and k1OCl-= 0.91 +/- 0.04 M(-1) x s(-1) for OCl-/ClO2) occurs in the first step to give OX and ClO2-.	chlorine dioxide	111-115	leptin receptor	Homo sapiens	65-68
12425638-4	2002	In the proposed mechanisms, electron transfer from OX- to ClO2(k1OBr- = 2.05 +/- 0.03 M(-1) x s(-1) for OBr(-)/ClO2 and k1OCl-= 0.91 +/- 0.04 M(-1) x s(-1) for OCl-/ClO2) occurs in the first step to give OX and ClO2-.	chlorine dioxide	111-115	leptin receptor	Homo sapiens	65-68
12425638-5	2002	This reversible step (k1OBr-/k(-1)OBr = 1.3 x 10(-7) for OBr-/ClO2, / = 5.1 x 10(-10) for OCl-/ClO2) accounts for the observed suppression by ClO2-.	chlorine dioxide	62-66	leptin receptor	Homo sapiens	24-27
12425638-5	2002	This reversible step (k1OBr-/k(-1)OBr = 1.3 x 10(-7) for OBr-/ClO2, / = 5.1 x 10(-10) for OCl-/ClO2) accounts for the observed suppression by ClO2-.	chlorine dioxide	62-66	leptin receptor	Homo sapiens	34-37
12425638-5	2002	This reversible step (k1OBr-/k(-1)OBr = 1.3 x 10(-7) for OBr-/ClO2, / = 5.1 x 10(-10) for OCl-/ClO2) accounts for the observed suppression by ClO2-.	chlorine dioxide	95-99	leptin receptor	Homo sapiens	24-27
12425638-5	2002	This reversible step (k1OBr-/k(-1)OBr = 1.3 x 10(-7) for OBr-/ClO2, / = 5.1 x 10(-10) for OCl-/ClO2) accounts for the observed suppression by ClO2-.	chlorine dioxide	95-99	leptin receptor	Homo sapiens	34-37
12425638-5	2002	This reversible step (k1OBr-/k(-1)OBr = 1.3 x 10(-7) for OBr-/ClO2, / = 5.1 x 10(-10) for OCl-/ClO2) accounts for the observed suppression by ClO2-.	chlorine dioxide	95-99	leptin receptor	Homo sapiens	24-27
12425638-5	2002	This reversible step (k1OBr-/k(-1)OBr = 1.3 x 10(-7) for OBr-/ClO2, / = 5.1 x 10(-10) for OCl-/ClO2) accounts for the observed suppression by ClO2-.	chlorine dioxide	95-99	leptin receptor	Homo sapiens	34-37
12425638-7	2002	These rate constants are = 1.0 x 10(8) M(-1) x s(-1) for OBr/ClO2 and = 7 x 10(9) M(-1) x s(-1) for OCl/ClO2.	chlorine dioxide	61-65	leptin receptor	Homo sapiens	57-60
12425638-7	2002	These rate constants are = 1.0 x 10(8) M(-1) x s(-1) for OBr/ClO2 and = 7 x 10(9) M(-1) x s(-1) for OCl/ClO2.	chlorine dioxide	104-108	leptin receptor	Homo sapiens	57-60
12425638-9	2002	The activation parameters for the first step are DeltaH1(++) = 55 +/- 1 kJ x mol(-1), DeltaS1(++) = - 49 +/- 2 J x mol(-1) x K(-1) for the OBr-/ClO2 reaction and DeltaH1(++) = 61 +/- 3 kJ x mol(-1), DeltaS1(++) = - 43 +/- 2 J x mol(-1) x K(-1) for the OCl-/ClO2 reaction.	chlorine dioxide	144-148	leptin receptor	Homo sapiens	139-142
12425638-9	2002	The activation parameters for the first step are DeltaH1(++) = 55 +/- 1 kJ x mol(-1), DeltaS1(++) = - 49 +/- 2 J x mol(-1) x K(-1) for the OBr-/ClO2 reaction and DeltaH1(++) = 61 +/- 3 kJ x mol(-1), DeltaS1(++) = - 43 +/- 2 J x mol(-1) x K(-1) for the OCl-/ClO2 reaction.	chlorine dioxide	257-261	leptin receptor	Homo sapiens	139-142
11538060-1	1992	The products of the reaction of OClO with NO3 were investigated between 220 and 298 K using a flow reactor and infrared, visible, and ultraviolet analysis.	chlorine dioxide	32-36	NBL1, DAN family BMP antagonist	Homo sapiens	42-45
4008865-6	1985	The addition of exogenous glutathione (50 mg 100 ml-1) or glutathione reductase and NADPH to rat blood in the presence of Alcide returned erythrocyte osmotic fragility to control values.	chlorine dioxide	122-128	glutathione-disulfide reductase	Rattus norvegicus	58-79
35187357-6	2022	By analyzing the impact of various operating conditions on AOX emissions, it was found that chlorine dioxide reduced in the D0 stage has the greatest impact on AOX.	chlorine dioxide	92-108	acyl-CoA oxidase 1	Homo sapiens	59-62
35187357-6	2022	By analyzing the impact of various operating conditions on AOX emissions, it was found that chlorine dioxide reduced in the D0 stage has the greatest impact on AOX.	chlorine dioxide	92-108	acyl-CoA oxidase 1	Homo sapiens	160-163
3816717-7	1986	The average instantaneous TOX concentration for chlorine dioxide, chloramine, and chlorine disinfection after 30 min contact time increased by 60, 92, and 238 micrograms/L, respectively, from a nondisinfected concentration of 25 micrograms/L.	chlorine dioxide	48-64	thymocyte selection associated high mobility group box	Homo sapiens	26-29
753950-3	1978	However, chlorine dioxide is a strong oxidant that forms significant amounts of chlorite when added to potable water supplies, and chlorite is similar to nitrite in its molecular structure and may be similar in its mechanism of methemoglobin production.	chlorine dioxide	9-25	hemoglobin subunit gamma 2	Homo sapiens	228-241
6343010-0	1983	[Treatment of tap water with chlorine dioxide].	chlorine dioxide	29-45	nuclear RNA export factor 1	Homo sapiens	14-17
753950-6	1978	Since male blacks represent the largest population in the U.S. to be G-6PD deficient, Black male neonates may represent the group at highest risk to the use of chlorine dioxide as a disinfectant in the nations water supplies.	chlorine dioxide	160-176	glucose-6-phosphate dehydrogenase	Homo sapiens	69-74
32923806-2	2020	The mechanism behind the reaction of 4-hydroxy-3-methoxyacetophenone (APO), a phenolic lignin model compound, with high concentrations of chlorine dioxide was investigated.	chlorine dioxide	138-154	aminopeptidase O (putative)	Homo sapiens	70-73
32923806-4	2020	Free chlorine dioxide displayed an absorbance at 360 nm and changes in this absorbance were studied with different APO concentrations.	chlorine dioxide	5-21	aminopeptidase O (putative)	Homo sapiens	115-118
32923806-7	2020	The reaction path between APO and chlorine dioxide at high concentrations was speculated, and it was observed that the activity of C1, C2, C3, C5, and C6 on the APO benzene ring was enhanced when high concentrations of chlorine dioxide were present.	chlorine dioxide	34-50	aminopeptidase O (putative)	Homo sapiens	26-29
32923806-7	2020	The reaction path between APO and chlorine dioxide at high concentrations was speculated, and it was observed that the activity of C1, C2, C3, C5, and C6 on the APO benzene ring was enhanced when high concentrations of chlorine dioxide were present.	chlorine dioxide	34-50	heterogeneous nuclear ribonucleoprotein C	Homo sapiens	131-153
32923806-7	2020	The reaction path between APO and chlorine dioxide at high concentrations was speculated, and it was observed that the activity of C1, C2, C3, C5, and C6 on the APO benzene ring was enhanced when high concentrations of chlorine dioxide were present.	chlorine dioxide	34-50	aminopeptidase O (putative)	Homo sapiens	161-164
32923806-7	2020	The reaction path between APO and chlorine dioxide at high concentrations was speculated, and it was observed that the activity of C1, C2, C3, C5, and C6 on the APO benzene ring was enhanced when high concentrations of chlorine dioxide were present.	chlorine dioxide	219-235	aminopeptidase O (putative)	Homo sapiens	26-29
32923806-7	2020	The reaction path between APO and chlorine dioxide at high concentrations was speculated, and it was observed that the activity of C1, C2, C3, C5, and C6 on the APO benzene ring was enhanced when high concentrations of chlorine dioxide were present.	chlorine dioxide	219-235	heterogeneous nuclear ribonucleoprotein C	Homo sapiens	131-153
32923806-7	2020	The reaction path between APO and chlorine dioxide at high concentrations was speculated, and it was observed that the activity of C1, C2, C3, C5, and C6 on the APO benzene ring was enhanced when high concentrations of chlorine dioxide were present.	chlorine dioxide	219-235	aminopeptidase O (putative)	Homo sapiens	161-164
31824729-1	2019	Adsorbable organic halogen (AOX) is generally formed by the reaction of residual lignin in pulps with chlorine dioxide during bleaching.	chlorine dioxide	102-118	acyl-CoA oxidase 1	Homo sapiens	28-31
32059828-2	2020	Tristel Trio Wipes system (TTWS) is a manual reprocessing method based on chlorine dioxide that has lately emerged in ENT department.	chlorine dioxide	74-90	trio Rho guanine nucleotide exchange factor	Homo sapiens	8-12
31824729-6	2019	The kinetics of AOX formation by the reaction of VA or VE with chlorine dioxide was studied.	chlorine dioxide	63-79	acyl-CoA oxidase 1	Homo sapiens	16-19
31824729-7	2019	The effects of pH, chlorine dioxide, lignin model compound concentration and reaction temperature on AOX formation are discussed.	chlorine dioxide	19-35	acyl-CoA oxidase 1	Homo sapiens	101-104
31824729-9	2019	Thus, we found that the non-phenolic lignin can react with chlorine dioxide to form AOX more easily than phenolic lignin.	chlorine dioxide	59-75	acyl-CoA oxidase 1	Homo sapiens	84-87
30942239-1	2019	The chlorine dioxide radical (ClO2 ) was found to act as an efficient oxidizing agent for the aerobic C-H oxygenation of the side-chain methyl groups in polypropylene under photoirradiation and ambient conditions (298 K and 1 atm).	chlorine dioxide	4-28	ATM serine/threonine kinase	Homo sapiens	226-229
31054055-6	2019	The THMs and AOX concentration of the samples disinfected chlorine dioxide ranged from N.D.-47.6 mug/L and N.D.-102 mug/L, respectively.	chlorine dioxide	58-74	acyl-CoA oxidase 1	Homo sapiens	13-16
30942239-1	2019	The chlorine dioxide radical (ClO2 ) was found to act as an efficient oxidizing agent for the aerobic C-H oxygenation of the side-chain methyl groups in polypropylene under photoirradiation and ambient conditions (298 K and 1 atm).	chlorine dioxide	30-34	ATM serine/threonine kinase	Homo sapiens	226-229
30891303-1	2019	Adsorbable organic halogens (AOX) are formed in pulp bleaching as a result of the reaction of residual lignin with chlorine dioxide.	chlorine dioxide	115-131	acyl-CoA oxidase 1	Homo sapiens	29-32
30543973-3	2019	Among chemical disinfection methods, chlorine dioxide (ClO2) has been largely used to control Legionella spp.	chlorine dioxide	37-53	histocompatibility minor 13	Homo sapiens	105-108
30543973-3	2019	Among chemical disinfection methods, chlorine dioxide (ClO2) has been largely used to control Legionella spp.	chlorine dioxide	55-59	histocompatibility minor 13	Homo sapiens	105-108
30543973-8	2019	Data from the water samples collected from 163 selected sampling points (hot water tanks, the return loop and distal outlets) was analysed using a life table analysis in order to investigate the duration of the effectiveness of the ClO2 method in eradicating Legionella spp.	chlorine dioxide	232-236	histocompatibility minor 13	Homo sapiens	270-273
30891303-3	2019	All the factors can affect the study about the mechanism of AOX formation in the reaction of lignin with chlorine dioxide.	chlorine dioxide	105-121	acyl-CoA oxidase 1	Homo sapiens	60-63
30891303-5	2019	The effect of lignin structure on AOX formation was determined by reacting phenolic and non-phenolic lignin model compound with a chlorine dioxide solution.	chlorine dioxide	130-146	acyl-CoA oxidase 1	Homo sapiens	34-37
30891303-9	2019	In a solution containing a combination of VA and VE in chlorine dioxide, VE was the dominant producer of AOX.	chlorine dioxide	55-71	acyl-CoA oxidase 1	Homo sapiens	105-108
28774629-2	2017	A major portion of total organic halogen (TOX), a collective parameter for all halogenated DBPs, formed in ClO2-treated drinking water is still unknown.	chlorine dioxide	107-111	thymocyte selection associated high mobility group box	Homo sapiens	42-45
29349741-7	2018	The TCS removal rate increased from 85.33 to 99.75% when the ClO2 concentration increased from 0.25 to 1.5 mg L-1.	chlorine dioxide	61-65	L1 cell adhesion molecule	Homo sapiens	110-113
27864634-0	2017	Reactions of aquacobalamin and cob(II)alamin with chlorite and chlorine dioxide.	chlorine dioxide	63-79	metabolism of cobalamin associated B	Homo sapiens	17-20
27966089-0	2017	Correlation of Conformational Changes and Protein Degradation with Loss of Lysozyme Activity Due to Chlorine Dioxide Treatment.	chlorine dioxide	100-116	lysozyme	Homo sapiens	75-83
27966089-2	2017	The purpose of this research is to elucidate the manner in which ClO2 destroys proteins by studying the effects of ClO2 on lysozyme.	chlorine dioxide	65-69	lysozyme	Homo sapiens	123-131
27966089-2	2017	The purpose of this research is to elucidate the manner in which ClO2 destroys proteins by studying the effects of ClO2 on lysozyme.	chlorine dioxide	115-119	lysozyme	Homo sapiens	123-131
27966089-4	2017	Lysozyme activity was drastically reduced to 45.3% of original enzyme activity when exposed to 4.3 mM ClO2 in the sample after 3 h. Almost all activities were lost in 3 h after exposure to higher ClO2 concentrations of up to 16.8 and 21.9 mM.	chlorine dioxide	102-106	lysozyme	Homo sapiens	0-8
27966089-4	2017	Lysozyme activity was drastically reduced to 45.3% of original enzyme activity when exposed to 4.3 mM ClO2 in the sample after 3 h. Almost all activities were lost in 3 h after exposure to higher ClO2 concentrations of up to 16.8 and 21.9 mM.	chlorine dioxide	196-200	lysozyme	Homo sapiens	0-8
27966089-6	2017	Raman shifts and the alteration of spectral features observed in the ClO2-treated lysozyme samples are associated with loss of the alpha-helix secondary structure, tertiary structure, and disulfide bond.	chlorine dioxide	69-73	lysozyme	Homo sapiens	82-90
27966089-7	2017	Progressive degradation of the denatured lysozyme by increasing levels of chlorine dioxide was also observed in gel electrophoresis.	chlorine dioxide	74-90	lysozyme	Homo sapiens	41-49
27864634-1	2017	Reactions of aquacobalamin (H2O-Cbl(III)) and its one-electron reduced form (cob(II)alamin, Cbl(II)) with chlorite (ClO2-) and chlorine dioxide (ClO 2  ) were studied by conventional and stopped-flow UV-Vis spectroscopies and matrix-assisted laser desorption/ionization-mass spectrometry (MALDI-MS).	chlorine dioxide	127-143	metabolism of cobalamin associated B	Homo sapiens	17-20
27865123-5	2017	Log10 reduction on corroded iron pipe wall coupons ranged from 1.0 to 2.9 at respective chlorine dioxide concentrations of 5 and 25 mg L-1, although spores were undetectable on the iron surface during disinfection at 25 mg L-1.	chlorine dioxide	88-104	immunoglobulin kappa variable 1-16	Homo sapiens	135-138
28064143-9	2017	PM and ClO2 pre-oxidation could both reduce the DBP formation from MC-LR.	chlorine dioxide	7-11	D-box binding PAR bZIP transcription factor	Homo sapiens	48-51
27865123-7	2017	Chlorine dioxide was the best performing disinfectant with >3.0 log10 removal from cement-mortar at 5 and 25 mg L-1.	chlorine dioxide	0-16	immunoglobulin kappa variable 1-16	Homo sapiens	115-118
24280616-6	2014	The formation of CHI3 was higher at 25 C than 5 C and 35 C. CHI3 formation showed an increase followed by a decrease trend with increasing ClO2 doses and iodide concentrations and the highest yields occurred at iodide to ClO2 molar ratios of 1-2. pH 8 resulted in the highest CHI3 formation.	chlorine dioxide	139-143	chitinase 1	Homo sapiens	17-21
27709908-0	2016	Genetic, Structural, and Phenotypic Properties of MS2 Coliphage with Resistance to ClO2 Disinfection.	chlorine dioxide	83-87	MS2	Homo sapiens	50-53
27709908-2	2016	Here, we investigated the resistance of MS2 coliphage to inactivation by chlorine dioxide (ClO2).	chlorine dioxide	73-89	MS2	Homo sapiens	40-43
27709908-2	2016	Here, we investigated the resistance of MS2 coliphage to inactivation by chlorine dioxide (ClO2).	chlorine dioxide	91-95	MS2	Homo sapiens	40-43
27709908-3	2016	ClO2 inactivates MS2 by degrading its structural proteins, thereby disrupting the ability of MS2 to attach to and infect its host.	chlorine dioxide	0-4	MS2	Homo sapiens	17-20
27709908-3	2016	ClO2 inactivates MS2 by degrading its structural proteins, thereby disrupting the ability of MS2 to attach to and infect its host.	chlorine dioxide	0-4	MS2	Homo sapiens	93-96
27336956-0	2016	[Evaluation of chlorine dioxide concentrations needed to effectively control contamination by Legionella spp in hospital hot water distribution systems].	chlorine dioxide	15-31	histocompatibility minor 13	Homo sapiens	105-108
27336956-1	2016	This aim of the study was to identify effective levels of ClO2 for control of Legionella spp.	chlorine dioxide	58-62	histocompatibility minor 13	Homo sapiens	89-92
26263004-4	2015	The hexenuronic acid (HexA) could obviously be reduced after xylanase pretreatment, and the adsorbable organic halides (AOX) were reduced after chlorine dioxide bleaching.	chlorine dioxide	144-160	acyl-CoA oxidase 1	Homo sapiens	120-123
26263004-8	2015	Xylanase pretreatment could remove HexA and expose more lignin, which decreased the chlorine dioxide demand and thus reduced formation of AOX.	chlorine dioxide	84-100	acyl-CoA oxidase 1	Homo sapiens	138-141
25632897-0	2015	Disinfection of herbal spa pool using combined chlorine dioxide and sodium hypochlorite treatment.	chlorine dioxide	47-63	surfactant protein A2	Homo sapiens	23-26
24280616-6	2014	The formation of CHI3 was higher at 25 C than 5 C and 35 C. CHI3 formation showed an increase followed by a decrease trend with increasing ClO2 doses and iodide concentrations and the highest yields occurred at iodide to ClO2 molar ratios of 1-2. pH 8 resulted in the highest CHI3 formation.	chlorine dioxide	139-143	chitinase 1	Homo sapiens	60-64
24280616-6	2014	The formation of CHI3 was higher at 25 C than 5 C and 35 C. CHI3 formation showed an increase followed by a decrease trend with increasing ClO2 doses and iodide concentrations and the highest yields occurred at iodide to ClO2 molar ratios of 1-2. pH 8 resulted in the highest CHI3 formation.	chlorine dioxide	139-143	chitinase 1	Homo sapiens	60-64
23561492-2	2013	Among the investigated I-DBPs, CHI3 was the major species during ClO2 oxidation in artificial synthesized waters.	chlorine dioxide	65-69	chitinase 1	Homo sapiens	31-35
24280616-6	2014	The formation of CHI3 was higher at 25 C than 5 C and 35 C. CHI3 formation showed an increase followed by a decrease trend with increasing ClO2 doses and iodide concentrations and the highest yields occurred at iodide to ClO2 molar ratios of 1-2. pH 8 resulted in the highest CHI3 formation.	chlorine dioxide	221-225	chitinase 1	Homo sapiens	17-21
24280616-6	2014	The formation of CHI3 was higher at 25 C than 5 C and 35 C. CHI3 formation showed an increase followed by a decrease trend with increasing ClO2 doses and iodide concentrations and the highest yields occurred at iodide to ClO2 molar ratios of 1-2. pH 8 resulted in the highest CHI3 formation.	chlorine dioxide	221-225	chitinase 1	Homo sapiens	60-64
24280616-6	2014	The formation of CHI3 was higher at 25 C than 5 C and 35 C. CHI3 formation showed an increase followed by a decrease trend with increasing ClO2 doses and iodide concentrations and the highest yields occurred at iodide to ClO2 molar ratios of 1-2. pH 8 resulted in the highest CHI3 formation.	chlorine dioxide	221-225	chitinase 1	Homo sapiens	60-64
21905903-4	2013	The concentrations of chlorine dioxide (ClO2) generated in ASC-Gel under conditions (a) to (e) were 12.1, 14.1, 17.2, 21.2, and 39.3 ppm, respectively.	chlorine dioxide	22-38	PYD and CARD domain containing	Homo sapiens	59-62
24334848-6	2013	Comparing no- and post-flush samples, a higher frequency of no-flush positive samples was noted using chlorine dioxide, suggesting an increased risk for patients when they open the tap.	chlorine dioxide	102-118	nuclear RNA export factor 1	Homo sapiens	181-184
23561492-4	2013	Formation of CHI3, IAA and TIAA followed an increasing and then decreasing pattern with increased ClO2 or DOC concentration.	chlorine dioxide	98-102	chitinase 1	Homo sapiens	13-17
23561492-8	2013	When 100 mug/L I(-)and ClO2 (7.5-44.4 muM) were spiked to the raw water samples from Yangshupu and Minhang drinking water treatment plant, certain amounts of CHI3 and IAA were found under pH 7 and the concentrations were strongly correlated with ClO2 dosage and water qualities, however, no TIAA was detected.	chlorine dioxide	23-27	chitinase 1	Homo sapiens	158-162
23561492-8	2013	When 100 mug/L I(-)and ClO2 (7.5-44.4 muM) were spiked to the raw water samples from Yangshupu and Minhang drinking water treatment plant, certain amounts of CHI3 and IAA were found under pH 7 and the concentrations were strongly correlated with ClO2 dosage and water qualities, however, no TIAA was detected.	chlorine dioxide	246-250	chitinase 1	Homo sapiens	158-162
21555141-4	2011	In this study, nine representative nitrogenous organic compounds with different DON characteristics and structures were selected to react with free chlorine, chlorine dioxide and monochloramine, respectively, for their DBP formation characteristics (nitrosamines, trihalomethanes (THMs) and haloacetic acids (HAAs)).	chlorine dioxide	158-174	D-box binding PAR bZIP transcription factor	Homo sapiens	219-222
23668125-5	2013	The CT values of 99.9% inactivation by free chlorine, monochloramine and chlorine dioxide were detected as (76.25 +/- 47.55)mg.min.L-1, (1396 +/-382)mg.min.L-1, (13.5 +/- 4.9) mg.min L-1.	chlorine dioxide	73-89	immunoglobulin kappa variable 1-16	Homo sapiens	131-134
23668125-5	2013	The CT values of 99.9% inactivation by free chlorine, monochloramine and chlorine dioxide were detected as (76.25 +/- 47.55)mg.min.L-1, (1396 +/-382)mg.min.L-1, (13.5 +/- 4.9) mg.min L-1.	chlorine dioxide	73-89	immunoglobulin kappa variable 1-16	Homo sapiens	156-159
23668125-5	2013	The CT values of 99.9% inactivation by free chlorine, monochloramine and chlorine dioxide were detected as (76.25 +/- 47.55)mg.min.L-1, (1396 +/-382)mg.min.L-1, (13.5 +/- 4.9) mg.min L-1.	chlorine dioxide	73-89	immunoglobulin kappa variable 1-16	Homo sapiens	156-159
22889665-4	2012	In contrast, preoxidation with ClO(2) sometimes reduced I-THM formation, primarily due to a reduction in CHI(3) formation.	chlorine dioxide	31-37	chitinase 1	Homo sapiens	105-111
21507519-0	2011	Chlorine dioxide for Legionella spp.	chlorine dioxide	0-16	histocompatibility minor 13	Homo sapiens	32-35
21033446-2	2010	METHODS: 0.8 mg/L chlorine dioxide solution was injected into 5 kinds of pipes respectively, PPR, PVC-U, Steel with Zinc coating, copper and PE pipes.	chlorine dioxide	18-34	PPR1	Homo sapiens	93-96
19763895-11	2010	Oxalate decarboxylase was thus a better choice than oxalate oxidase for treatment of filtrates from chlorine dioxide bleaching.	chlorine dioxide	100-116	LOC548260	Hordeum vulgare	52-67