Chlorine dioxide hydrate, frozen is an orange colored solid, appearing as a block of ice, with a faint odor of chlorine. It may only be shipped in the frozen state and then only by private or contract motor carrier. The melting point of the hydrate is around 30°F. If it should thaw and further warm up, chlorine dioxide gas is given off. The gas is toxic by inhalation. The gas and liquid are violently decomposed by organic materials. The gas will decompose explosively at temperatures below the boiling point of water. It is used to bleach wood pulp, fats and oils; in processing flour, and for water purification. Chlorine dioxide is a yellow to reddish gas or a red-brown liquid below 52 deg. F. with an unpleasant odor similar to chlorine.
颜色/状态:
Yellowish-brown gas
气味:
... Unpleasant odor similar to chlorine and nitric acid.
Both chlorine dioxide and chlorite are primarily metabolized to chloride ion. At 72 hours following single oral (gavage) administration of radiolabeled chlorine dioxide in rats, chloride ion accounted for approximately 87% of the radioactivity that had been collected in the urine and 80% of the radioactivity in a plasma sample. Chlorite was the other major metabolite, accounting for approximately 11 and 21% of the radioactivity in the urine and plasma samples, respectively. Chlorate was a minor component of the radioactivity in the urine. Similarly, chloride ion accounted for approximately 85% of the radioactivity in the 72-hour urine collection of rats that had been orally administered radiolabeled chlorite; the remainder in the form of chlorite.
IDENTIFICATION AND USE: Chlorine dioxide is a yellowish-brown gas with unpleasant odor similar to chlorine and nitric acid. Its uses include bleaching cellulose, paper-pulp, flour, leather, fats and oils, textiles, and beeswax. It is also used for purification of water, taste and odor control of water, cleaning and detanning leather, in the manufacture of chloride salts, and as an oxidizing agent, bactericide, antiseptic and deodorizer. Chlorine dioxide was found to be highly effective against various microorganisms tested at very low concentrations in a minimum contact time of 30 to 60 seconds. HUMAN STUDIES: Potential symptoms of overexposure are irritation of eyes, nose, and throat, as well as coughing, wheezing, bronchitis, and pulmonary edema. Workers industrially exposed to low concentrations of the gas in air have been noted occasionally to suffer from irritation of the eyes and to see haloes about lights, but these effects have been minor compared to respiratory irritation. Bronchoscopy and biopsy revealed slight chronic bronchitis in 7 of 12 workers. Only two workers who had been exposed just prior to examination showed physical signs of respiratory effects. Workers acutely exposed to chlorine dioxide developed both reactive airways dysfunction syndrome (RADS), a form of occupational asthma, and an upper airways reactive disorder that was called reactive upper airways disfunction syndrome (RUDS). A positive association was found between exposure of the mother to chlorine dioxide-treated water during pregnancy and prematurity of the newborn. Children born of mothers who drank disinfected water treated with either chlorine dioxide or hypochlorite were noted to have an increased incidence of small cranial circumference, small body length, and neonatal jaundice. Chlorine dioxide was found to be weakly genotoxic in human leukocytes. ANIMAL STUDIES: Chlorine dioxide is very toxic by inhalation in rats. Clinical signs of toxicity included respiratory distress. Macroscopically, pulmonary edema and emphysema were seen in all groups of chlorine dioxide-exposed animals, with the incidence increasing in a dose-related manner. Chlorine dioxide is toxic when administered in solution by the oral route to rats. Two males and two females receiving 80 mg chlorine dioxide/kg body weight died, and a further two males at 40 mg/kg body weight also died within 48 hr of administration. There were no deaths at 20 mg/kg body weight. A developmental study in rats did not demonstrate any impairment of reproductive function, and there were no signs of developmental effects among rats receiving up to 10 mg aqueous chlorine dioxide/kg body weight per day. A negative result was obtained for micronucleus formation, and there were no increases in the number of structural or numerical chromosome aberrations in mice treated with chlorine dioxide. However, chlorine dioxide increased water genotoxicity in assays with E. coli and with S. cerevisiae. In Chinese hamster ovary cells at 2.5-15 ug/mL, there was a marked dose-related, statistically significant increase in the number of metaphases with chromosome aberrations. In the presence of metabolic activation, cell toxicity and an absence of mitotic cells were observed at 75 ug/mL. An increase in the number of metaphases with chromosome aberrations was noted at 50 ug/mL. ECOTOXICITY STUDIES: Developmental abnormalities in the sea urchin were evident at exposure to the chlorine dioxide concentration 250 mg/L. Compared with the control, pre-hatch malformations were 6% higher; retarded development, 2%; post-hatch malformations, 20%; skeletal malformations, 21%; and gut malformations, 11%. Survival of larval kelp bass was not significantly affected by chlorine dioxide. In Fathead minnows (Pimephales promelas) chlorine dioxide exposure produced dose-dependent gill pathology including epithelial lifting, hypertrophy, hyperplasia, lamellar fusion, and necrosis. Complete recovery, even in fish with severe hypertrophy and lamellar fusion, was achieved within 4 days. Chlorine dioxide concentrations ranging from 0.1 to 0.5 mg/L induced micronuclei in Vicia faba at acid pH, while 1-2 mg/L chlorine dioxide gave positive responses at neutral pH. Chlorine dioxide produced positive responses in the Tradescantia micronucleus test.
CLASSIFICATION: D; not classifiable as to human carcinogenicity. BASIS FOR CLASSIFICATION: No satisfactory human or animal studies assessing the chronic carcinogenic potential of chlorine dioxide have been located. HUMAN CARCINOGENICITY DATA: None. ANIMAL CARCINOGENICITY DATA: None.
来源:Hazardous Substances Data Bank (HSDB)
毒理性
暴露途径
这种物质可以通过吸入被身体吸收。
The substance can be absorbed into the body by inhalation.
来源:ILO-WHO International Chemical Safety Cards (ICSCs)
The distribution and chemical fate of (36)Cl-ClO2 gas subsequent to fumigation of tomatoes or cantaloupe was investigated as were major factors that affect the formation of chloroxyanion byproducts. Approximately 22% of the generated (36)Cl-ClO2 was present on fumigated tomatoes after a 2 hr exposure to approximately 5 mg of (36)Cl-ClO2. A water rinse removed 14% of the radiochlorine while tomato homogenate contained approximately 63% of the tomato radioactivity; 24% of the radiochlorine was present in the tomato stem scar area. Radioactivity in tomato homogenate consisted of (36)Cl-chloride (>/= 80%), (36)Cl-chlorate (5 to 19%), and perchlorate (0.5 to 1.4%). In cantaloupe, 55% of the generated (36)Cl-ClO2 was present on melons fumigated with 100 mg of (36)Cl-ClO2 for a 2 hr period. Edible cantaloupe flesh contained no detectable radioactive residue (LOQ = 0.3 to 0.4 ug/g); >99.9% of radioactivity associated with cantaloupe was on the inedible rind, with <0.1% associated with the seed bed. Rind radioactivity was present as (36)Cl-chloride (approximately 86%), chlorate (approximately 13%), and perchlorate (approximately 0.6%). Absent from tomatoes and cantaloupe were (36)Cl-chlorite residues. Follow-up studies have shown that chlorate and perchlorate formation can be completely eliminated by protecting fumigation chambers from light sources.
After oral administration of Alcide (sodium chlorite and lactic acid) in rats, the peak plasma level was obtained in 8 hr. At 144 hr, radioactivity was highest in plasma followed by lung, kidney, skin, bone marrow, stomach, ovary, duodenum, ileum, spleen, fat, brain, liver, and carcass. Subcellular distribution revealed that 85% of the activity in the liver homogenate resided in the cytosol. 70% of total activity in plasma was located in the trichloroacetic acid supernatant, with 30% bound to the precipitated protein fraction. Urinary excretion accounted for most of the (36)chlorine eliminated.
One study shows that "chlorine" (chemical form not characterized) derived from aqueous chlorine dioxide is absorbed by the oral route, with a wide distribution and rapid and extensive elimination. In this study, groups of four rats received a single oral gavage dose of approximately 1.5 or 4.5 mg 36ClO2/kg body weight. Blood samples were collected for up to 48 hr post-administration, and at 72 hr, animals were killed, with samples taken from kidneys, lungs, small intestine, liver, spleen, thymus, bone marrow, and testes. 36Cl was found in all tissues except testes, skin, and the remaining carcass, although levels in these tissues each accounted for less than 1% of the administered dose.
来源:Hazardous Substances Data Bank (HSDB)
吸收、分配和排泄
大约40%的36Cl单次剂量通过尿液、呼出气体和粪便排出,其中尿液占了大多数(约30%)。
About 40% of /a single dose of/ 36Cl was recovered in urine, expired air, and feces, although the urine accounted for most (about 30%).
Photoreduction of Pt(IV) Halo-Hydroxo Complexes: Possible Hypohalous Acid Elimination
作者:Lasantha A. Wickramasinghe、Paul R. Sharp
DOI:10.1021/ic402358s
日期:2014.2.3
detected in photolyzed benzene solutions. Photolysis of 3 or 6 in the presence of 2,3-dimethyl-2-butene (TME) yields the chlorohydrin (2-chloro-2,3-dimethyl-3-butanol), 3-chloro-2,3-dimethyl-1-butene, and acetone, all expected products from HOCl trapping, but additional oxidation products are also observed. Photolysis of mixed chloro-bromo complex 7 with TME yields the bromohydrin (2-bromo-2,3-dimethyl-3-butanol)
An infrared study of the UV photolysis of chlorine nitrate trapped in various matrices at 11 K
作者:Armelle De Saxce、Louise Schriver
DOI:10.1016/0009-2614(92)85016-4
日期:1992.11
Photolysis of matrix isolated chlorine nitrate in argon matrix assisted by reactive matrices (solid nitrogen and oxygen) at 11 K have been carried out by visible and ultraviolet light in the 800—250 nm range. The product identification and relative measurements of the species time evolution were made by Fourier transform infrared spectrometry. Below 300 nm, two main dissociation channels are evidenced
借助在800-250 nm范围内的可见光和紫外光,在11 K下由反应性基质(固体氮和氧)辅助下的氩气基质中的基质分离的硝酸氯光解。用傅立叶变换红外光谱法对产物的时间演化进行产物鉴定和相对测量。在300 nm以下,有两个主要的解离通道被证明分别导致ClNO + O 2和ClONO +O。重组笼过程在基质中发生,并且获得的结果与气相研究部分不同,但提供了有关冷凝相系统(例如极地平流层云表面)中可能发生的光反应的信息。
Outer-sphere electron-transfer reactions involving the chlorite/chlorine dioxide couple. Activation barriers for bent triatomic species
作者:David M. Stanbury、Lynn A. Lednicky
DOI:10.1021/ja00322a018
日期:1984.5
Cinetique des reactions redox mettant en jeu le couple ClO 2 |ClO 2 − en solution aqueuse. ClO 2 est reduit par [Co(terpy) 2 ] 2+ pour produire ClO 2 − . ClO 2 − est oxyde par IrCl 6 2− pour produire ClO 2 et IrCl 6 3−
Cinetique des reaction 氧化还原金属 en jeu le Couple ClO 2 |ClO 2 − en solution aqueuse。ClO 2 est reduit par [Co(terpy) 2 ] 2+ pour produire ClO 2 − 。ClO 2 − est oxyde par IrCl 6 2− 倒入产品 ClO 2 et IrCl 6 3−
Radiation mechanisms. Part 9. A comparative electron spin resonance study of radiation effects in thallous and thallic salts
作者:Martyn C. R. Symons、Donald N. Zimmerman
DOI:10.1039/dt9760000180
日期:——
Exposure of thallous salts to high-energy radiation usually yields TlII centres together with paramagnetic centres derived from the anions which show strong charge-transfer interaction with neighbouring thallous ions. Previous work on thallous acetate and nitrate is extended to the perchlorate, and to the corresponding TlIII salts. The latter all gave TlII but centres derived from the anions generally
Methods and apparatus for generation of dual biocides are provided. The electrolytic generation of chlorine as a biocide is employed for further generation of additional biocides within a single system or generator, including bromine, iodine, chlorine dioxide, fluorine, or chloramines from their respective salts and/or precursors. A single on-site generating system produces a combination of biocides for applications of use providing cost, safety and efficacy improvements. Methods of using the disinfecting biocides provide a synergistic effect through simultaneous or sequential applications.