35691-65-7N#CCCC(Br)(C#N)CBrDHVLDKHFGIVEIP-UHFFFAOYSA-NCrystals with a pungent odor. Insoluble in water. Used as a preservative in latex paint, adhesives, etc.
35691-65-7DTXSID3024944CHEMBL3188084CHEBI:62823Cosmetic ingredients (Methyldibromo Glutaronitrile) -> CIR (Cosmetic Ingredient Review)
Preservative
Slightly sweet odor
Mildly pungent odor
0.970 g/mL at 20 °C
Relative density (water = 1): 1.1
Yellowish-white granular solid
Crystals from ethanol
Very soluble in chloroform, ethyl acetate. Soluble in methanol, ethanol, ether.
Very soluble in acetone, benzene, dimethylformamide
In water, 0.212 g/100 mL /SRC: 2.12X10+3 mg/L/
Solubility in water: none
52 °C
This chemical does not meet GHS hazard criteria for 1.1% (15 of 1350) of reports.
Danger
H302 (98.5%): Harmful if swallowed [Warning Acute toxicity, oral]
P261, P264, P264+P265, P270, P272, P273, P280, P301+P317, P302+P352, P305+P354+P338, P317, P321, P330, P332+P317, P333+P317, P362+P364, P391, and P501 (click each P-code to see the statement)
Aggregated GHS information provided per 1350 reports by companies from 26 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.
Danger
Chemical: Pentanedinitrile, 2-bromo-2-(bromomethyl)-
Pentanedinitrile, 2-bromo-2-(bromomethyl)-: Does not have an individual approval but may be used under an appropriate group standard
Excerpt from ERG Guide 154 [Substances - Toxic and/or Corrosive (Non-Combustible)]:
Combustible. Gives off irritating or toxic fumes (or gases) in a fire.
One of the two chemical components of Euxyl K400, the mixture contains 20% 1,2-dibromo-2,4-dicyanobutane and 80% phenoxyethanol. The former chemical is thought to be the skin sensitizer in the biocide, Euxyl K400. [Kanerva, p. 1795] A skin and eye irritant; May cause skin sensitization; [ICSC] Danger of skin sensitization; [MAK]
1,2-Dibromo-2,4-dicyanobutane is an indirect food additive for use only as a component of adhesives. Limit: for use as a preservative only.
... After iv administration of (14)C-BCB to male Fischer 344 rats, (14)C-equivalents were observed to bind gradually to blood constituents. By 48 hr, approximately 12% of the total dose was covalently bound. At no time was parent compound detected in the blood. However, the debrominated BCB metabolite 2-methyleneglutaronitrile (MGN) was observed. In vitro experiments revealed that BCB was extremely labile and was readily debrominated in fresh whole blood, erythrocyte preparations, and buffered glutathione (GSH) solutions. In each case, the formation of MGN was inhibited by the alkylation of free sulfhydryls with N-ethylmaleimide (NEM). For every 1 mole of BCB converted to MGN, 2 moles of GSH were oxidized to glutathione disulfide (GSSG) (BCB + 2 GSH --> MGN + GSSG + 2 HBr). The oxidation of free sulfhydryls during the conversion of BCB to MGN caused erythrocyte hemolysis (EC50 approximately 1 mM) in isolated preparations. Hemolysis was increased by coincubation of BCB with NEM (EC50 approximately 0.3 mM) and was decreased by coincubation with GSH (EC50 > 3 mM). However, MGN did not cause hemolysis of erythrocytes, even at concentrations 10-fold higher than the EC50 of BCB. In vitro experiments also demonstrated that incubation with either BCB or MGN resulted in significant macromolecular binding to the erythrocyte fraction of the blood (approximately 80%). Incubation with NEM resulted in a significant decrease in binding for both BCB (11.3% bound) and MGN (29.5% bound).
YX089CPS05
METHYLDIBROMO GLUTARONITRILE
Established Pharmacologic Class [EPC] - Standardized Chemical Allergen
Physiologic Effects [PE] - Increased Histamine Release
Physiologic Effects [PE] - Cell-mediated Immunity
Chemical Structure [CS] - Allergens
The metabolism of (14)C-dibromodicyanobutane was studied in male CD rats following a single oral administration of 50 mg/kg (14)C-dibromodicyanobutane (labeled in the butane core of the molecule). Total recovery of radioactivity during the 7 day collection period in the urine, feces, and respired (14)C-CO2 was 84-91%, 6-10%, and 0.5% of the administered dose, respectively. Tissue assay showed that 7 days after administration organs contained relatively greater concentrations of compound including the lung (2.7 ppm), liver (2.5 ppm), kidneys (2.3 ppm), and spleen (2.3 ppm). Maximum blood concentration (71 ug/mL) of dibromodicyanobutane equivalent is attained at 5 hours postadministration. On the basis of percent dose per whole organ, each of these 11 ... /SRP: tissues contained/ <0.1%, except for liver at 0.3%. Although numerous deficiencies were noted, this study provides supplemental information. Since the compound is rapidly absorbed and excreted, most of the radioactivity in the urine was found during the first 24 hours post-administration.
Keine Reaktionsaufzeichnungen unter den aktuellen Filterkriterien.
Wird geladen…
51-52 °C
0.00025 [mmHg]
6.7E-3 Pascal /SRC: 5.025X10-5 mm Hg/ at 25 °C
FCS -> FDA Cumulative Estimated Daily Intake (CEDI)
FCS -> FDA Inventory of Food Contact Substances Listed in 21 CFR
Crystals with a pungent odor. Insoluble in water. Used as a preservative in latex paint, adhesives, etc.
Crystals with a pungent odor; [CAMEO]
WHITE CRYSTALS WITH PUNGENT ODOUR.
The chemical was found to be stable when subjected to Al, Sn, Ni, Fe, thermal and photosensitivity tests. One year storage at room temperature did not produce any significant change regarding purity, color, specific gravity, and refractive index.
(a) Slimicides may be safely used in the manufacture of paper and paperboard that contact food, in accordance with the following prescribed conditions: (1) Slimicides are used as antimicrobial agents to control slime in the manufacture of paper and paperboard. (2) Subject to any prescribed limitations, slimicides are prepared from one or more of the slime-control substances named in paragraph (c) of this section to which may be added optional adjuvant substances as provided for under paragraph (d) of this section. (3) Slimicides are added to the process water used in the production of paper or paperboard, and the quantity added shall not exceed the amount necessary to accomplish the intended technical effect. (b) To insure safe usage, the label or labeling of slimicides shall bear adequate directions for use. c) Slime-control substances permitted for use in the preparation of slimicides include substances subject to prior sanction or approval for such use and the following: 1,2-Dibromo-2,4-dicyanobutane; Limitation: At a maximum level of 0.005% of dry weight fiber.
USEPA/Office of Pesticide Programs; Reregistration Eligibility Decision Document - Dibromodicyanobutane. June 1996. The RED summarizes the risk assessment conclusions and outlines any risk reduction measures necessary for the pesticide to continue to be registered in the U.S.[Available from, as of July 15, 2011: http://www.epa.gov/pesticides/reregistration/status.htm]
Based on the reviews of the generic data for the active ingredient dibromodicyanobutane, the Agency has sufficient information on the health effects of dibromodicyanobutane and on its potential for causing adverse effects in fish, wildlife and the environment. The Agency has determined that dibromodicyanobutane products, labeled and used as specified in this Reregistration Eligibility Decision, will not pose unreasonable risks or adverse effects to humans or the environment. Therefore, the Agency concludes that products containing dibromodicyanobutane for all uses are eligible for reregistration.
As the federal pesticide law FIFRA directs, EPA is conducting a comprehensive review of older pesticides to consider their health and environmental effects and make decisions about their future use. Under this pesticide reregistration program, EPA examines health and safety data for pesticide active ingredients initially registered before November 1, 1984, and determines whether they are eligible for reregistration. In addition, all pesticides must meet the new safety standard of the Food Quality Protection Act of 1996. Pesticides for which EPA had not issued Registration Standards prior to the effective date of FIFRA '88 were divided into three lists based upon their potential for human exposure and other factors, with List B containing pesticides of greater concern and List D pesticides of less concern. 1-Bromo-1-(bromomethyl)-1,3-propanedicarbonitrile is found on List B. Case No: 2780; Pesticide type: fungicide, herbicide, antimicrobial; Case Status: RED Approved 6/96; OPP has made a decision that some/all uses of the pesticide are eligible for reregistration, as reflected in a Reregistration Eligibility Decision (RED) document .; Active ingredient (AI): 1-Bromo-1-(bromomethyl)-1,3-propanedicarbonitrile; Data Call-in (DCI) Date(s): 6/14/91; AI Status: OPP has completed a Reregistration Eligibility Decision (RED) for the case/AI.
1-BROMO-1-(BROMOMETHYL)-1,3-PROPANEDICARBONITRILE may polymerize in the presence of metals and some metal compounds. Incompatible with acids; mixing nitriles with strong oxidizing acids can lead to extremely violent reactions. Nitriles are generally incompatible with other oxidizing agents such as peroxides and epoxides. The combination of bases and nitriles can produce hydrogen cyanide. Nitriles are hydrolyzed in both aqueous acid and base to give carboxylic acids (or salts of carboxylic acids). These reactions generate heat. Peroxides convert nitriles to amides. Nitriles can react vigorously with reducing agents.
Excerpt from ERG Guide 154 [Substances - Toxic and/or Corrosive (Non-Combustible)]:
Use water spray, powder, foam, carbon dioxide.
Fresh air, rest.
Remove contaminated clothes. Rinse and then wash skin with water and soap.
First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.
Rinse mouth. Give one or two glasses of water to drink. Refer for medical attention .
SRP: The most favorable course of action is to use an alternative chemical product with less inherent propensity for occupational harm/injury/toxicity or environmental contamination. Recycle any unused portion of the material for its approved use or return it to the manufacturer or supplier. Ultimate disposal of the chemical must consider: the material's impact on air quality; potential migration in soil or water; effects on animal and plant life; and conformance with environmental and public health regulations.
Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Sweep spilled substance into covered containers. If appropriate, moisten first to prevent dusting. Carefully collect remainder. Then store and dispose of according to local regulations.
/The objective of this study was/ to determine whether there exists evidence for synergy between contact allergens during the induction phase of skin sensitization using the mouse local lymph node assay (LLNA) as a model system. Proliferative responses in draining lymph nodes were assessed with increasing concentrations of 1,4-phenylenediamine (PPD), methyldibromo glutaronitrile (MDBGN), and a combination of PPD and MDBGN. Data from each of two independent experiments show that lymph node cell proliferation associated with combined exposure to PPD and MDBGN was, in general, only modestly increased relative to that predicted from a simple summation of their individual responses. Although the increase in response is very modest, it does imply a relationship between this combination of sensitizers that may not be simply additive in terms of their ability to stimulate proliferative responses in draining lymph nodes...
The present study was undertaken to evaluate the combined effect of the preservative methyldibromo glutaronitrile (MDBGN) and sodium lauryl sulfate (SLS) on the elicitation response of allergic contact dermatitis. 20 volunteers with contact allergy to MDBGN were patch tested with 5 concentrations (10, 50, 100, 500 and 1000 p.p.m.) of MDBGN alone and in combination with 0.25% SLS on the upper arms for 24 hr. Skin reactions were evaluated by clinical scoring, and data were evaluated by logistic dose-response models. Additionally, evaluation of skin reactions was performed by measurement of transepidermal water loss (TEWL) and skin colour. Measurements were obtained at baseline and at D3 and D7. As evaluated by clinical assessment, allergic reactions to MDBGN were elicited at lower concentrations when applied in combination with SLS than when applied alone. The response was augmented by a factor of 6.4. An increased response to combined exposure to SLS and MDBGN as compared with MDBGN alone was confirmed by TEWL and colour measurements. Effects of exposure time and concentration of the detergent are discussed. In conclusion, an augmented response was found after concurrent application of MDBGN and SLS. The response was augmented by a factor of 6.4, with confidence limits of 2.8-14.6 (P < 0.0001). This result is important in relation to the determination of threshold values and the risk assessment of contact allergens in consumer and industrial products, where allergens are often present in combination with surfactants.
LD50; Species: Anas platyrhynchos (Mallard duck) 14 days old, oral 1038 mg/kg/14 days
LC50; Species: Anas platyrhynchos (Mallard duck) 14 days old, dietary >10000 ppm for 8 days
LC50; Species: Colinus virginianus (Northern bobwhite) 14 days old, dietary 4042 ppm for 8 days
LC50; Species: Americamysis bahia (Opossum shrimp); Conditions: flow through; Concentration: 2.7 ppm for 96 hr (95% confidence interval: 2.5-3.2 ppm) /formulated product/
For more Ecotoxicity Values (Complete) data for 1,2-DIBROMO-2,4-DICYANOBUTANE (14 total), please visit the HSDB record page.
TERRESTRIAL FATE: Based on a classification scheme(1), Koc values ranging from 528 to 33.4(2) indicate that 1,2-dibromo-2,4-dicyanobutane is expected to have moderate to very high mobility in soil(SRC). Volatilization of 1,2-dibromo-2,4-dicyanobutane from moist soil surfaces is not expected to be an important fate process(SRC) given an estimated Henry's Law constant of 8.3X10-9 atm-cu m/mole(SRC), derived from its vapor pressure, 5.025X10-5 mm Hg(2), and water solubility, 2.12X10+3 mg/L(2). 1,2-Dibromo-2,4-dicyanobutane is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(2). Biodegradation data were not available(SRC, 2011).
AQUATIC FATE: Based on a classification scheme(1), Koc values ranging from 528 to 33.4(2) indicate that 1,2-dibromo-2,4-dicyanobutane is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is not expected(3) based upon an estimated Henry's Law constant of 8.3X10-9 atm-cu m/mole(SRC), derived from its vapor pressure, 5.025X10-5 mm Hg(2), and water solubility, 2.12X10+3 mg/L(2). According to a classification scheme(4), an estimated BCF of five(SRC), from an estimated log Kow of 1.63(5) and a regression-derived equation(6), suggests the potential for bioconcentration in aquatic organisms is low(SRC). Biodegradation data were not available(SRC, 2011).
AQUATIC FATE: Radio-labeled 1,2-dibromo-2,4-dicyanobutane at an initial concentration of 10 ug/g exhibited a half-life of 0.874 days in flooded sandy loam soil; degradates included 2-methyleneglutaronitrile and (E) and (Z) isomers of 1-bromo-2,4-dicyano-1-butene. Degradation appears to be controlled by alkaline hydrolysis and microbially-mediated processes(1).
ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), 1,2-dibromo-2,4-dicyanobutane, which has a vapor pressure of 5.025X10-5 mm Hg at 25 °C(2), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase 1,2-dibromo-2,4-dicyanobutane is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC); the half-life for this reaction in air is estimated to be 18 days(SRC), calculated from its rate constant of 5.9X10-13 cu cm/molecule-sec at 25 °C(SRC) that was derived using a structure estimation method(3). 1,2-Dibromo-2,4-dicyanobutane does no contain chromophores that absorb at wavelengths >290 nm(4), and therefore is not expected to be susceptible to direct photolysis by sunlight(SRC).
Based on the available data, the CIR Expert Panel concludes Methyldibromo Glutaronitrile to be safe as used in rinse off products, and safe up to 0.025% in leave on products.
Safe for use in cosmetics, with qualifications
Redness.
Redness. Pain.
Abdominal pain.
The following link will take the user to the National Toxicology Program (NTP) Test Agent Search Results page, which tabulates all of the "Standard Toxicology & Carcinogenesis Studies", "Developmental Studies", and "Genetic Toxicity Studies" performed with this chemical. Clicking on the "Testing Status" link will take the user to the status (i.e., in review, in progress, in preparation, on test, completed, etc.) and results of all the studies that the NTP has done on this chemical.[Available from: http://ntp-apps.niehs.nih.gov/ntp_tox/index.cfm?fuseaction=ntpsearch.searchresults&searchterm=35691-65-7]
At concentrations of 0.1 to 1.0 ug/mL, 1,2-dibromo-2,4-dicyanobutane exhibited Koc values of 528 in sand, 87.8 in sandy loam soil, 72.9 in clay loam, and 33.4 in silt loam soil, corresponding to Freundlich coefficients of 0.264, 0.351, 0.474, and 0.701, respectively(1). According to a classification scheme(2), this Koc range suggests that 1,2-dibromo-2,4-dicyanobutane is expected to have moderate to very high mobility in soil.
/HUMAN EXPOSURE STUDIES/ A 2% dilution of the commercial solution containing 20% Methyldibromo Glutaronitrile in phenoxyethanol was applied in a single 24 hr occlusive patch to the inner forearm of 30 panelists. Observations made at the time of patch removal and at 48 hr and 72 hr after initial exposure revealed no reactions.
/HUMAN EXPOSURE STUDIES/ ... From January 1993 until July 1994, all consecutive patients attending for routine patch testing were also tested with 1,2-dibromo-2,4-dicyanobutane (0.1% petrolatum): one of 281 (0.3%), nine of 281 (3.2%) and six of 247 (2.4%) were found to be positive in the first and second halves of 1993 and the first half of 1994, respectively. In at least 12 of 16 patients this allergy was responsible for their presenting complaint (perianal and facial dermatitis).
/HUMAN EXPOSURE STUDIES/ ... Seven presensitized individuals (37%) developed allergic contact dermatitis from the soap containing MDBGN. The mean dose of MDBGN per application was 2.2 ug/ sq cm and the reactions appeared between days 6 and 34. ... The difference in reactivity between test subjects and controls was significant (one-sided Fisher's exact test, P = 0.04). Patch test threshold values ranged from < 0.001% to 0.2% MDBGN in ethanol/water.
/HUMAN EXPOSURE STUDIES/ ... A study group of 1,307 patients (Group 1) suspected of having allergic contact dermatitis was given patch tests using a standard series. Patch tests with Euxyl-K-400, its components methyldibromoglutaronitrile and phenoxyethanol (122996), and imidazolidinyl were performed on 1,109 patients (Group 2). Allergic reactions to Euxyl-K-400 were seen in 24 subjects (2.4%), all of whom also exhibited positive reactions to methyldibromoglutaronitrile. ... Of the chemicals in the supplementary series, allergic reactions were produced in 2.4% of the subjects by Euxyl-K-400 and methyldibromoglutaronitrile.
For more Human Toxicity Excerpts (Complete) data for 1,2-DIBROMO-2,4-DICYANOBUTANE (31 total), please visit the HSDB record page.
1,2-Dibromo-2,4-dicyanobutane's production may result in its release to the environment through various waste streams; its use as a microbiocide/microbiostat against slime-forming bacteria and fungi(1) for latex paints, adhesives, latex emulsions, dispersed pigments, joint cements, and metal working fluids(2) will result in its direct release to the environment(SRC).
1,2-Dibromo-2,4-dicyanobutane is an indirect food additive for use only as a component of adhesives. Limit: for use as a preservative only.
(a) Slimicides may be safely used in the manufacture of paper and paperboard that contact food, in accordance with the following prescribed conditions: (1) Slimicides are used as antimicrobial agents to control slime in the manufacture of paper and paperboard. (2) Subject to any prescribed limitations, slimicides are prepared from one or more of the slime-control substances named in paragraph (c) of this section to which may be added optional adjuvant substances as provided for under paragraph (d) of this section. (3) Slimicides are added to the process water used in the production of paper or paperboard, and the quantity added shall not exceed the amount necessary to accomplish the intended technical effect. (b) To insure safe usage, the label or labeling of slimicides shall bear adequate directions for use. c) Slime-control substances permitted for use in the preparation of slimicides include substances subject to prior sanction or approval for such use and the following: 1,2-Dibromo-2,4-dicyanobutane; Limitation: At a maximum level of 0.005% of dry weight fiber.
Based on the reviews of the generic data for the active ingredient dibromodicyanobutane, the Agency has sufficient information on the health effects of dibromodicyanobutane and on its potential for causing adverse effects in fish, wildlife and the environment. The Agency has determined that dibromodicyanobutane products, labeled and used as specified in this Reregistration Eligibility Decision, will not pose unreasonable risks or adverse effects to humans or the environment. Therefore, the Agency concludes that products containing dibromodicyanobutane for all uses are eligible for reregistration.
As the federal pesticide law FIFRA directs, EPA is conducting a comprehensive review of older pesticides to consider their health and environmental effects and make decisions about their future use. Under this pesticide reregistration program, EPA examines health and safety data for pesticide active ingredients initially registered before November 1, 1984, and determines whether they are eligible for reregistration. In addition, all pesticides must meet the new safety standard of the Food Quality Protection Act of 1996. Pesticides for which EPA had not issued Registration Standards prior to the effective date of FIFRA '88 were divided into three lists based upon their potential for human exposure and other factors, with List B containing pesticides of greater concern and List D pesticides of less concern. 1-Bromo-1-(bromomethyl)-1,3-propanedicarbonitrile is found on List B. Case No: 2780; Pesticide type: fungicide, herbicide, antimicrobial; Case Status: RED Approved 6/96; OPP has made a decision that some/all uses of the pesticide are eligible for reregistration, as reflected in a Reregistration Eligibility Decision (RED) document .; Active ingredient (AI): 1-Bromo-1-(bromomethyl)-1,3-propanedicarbonitrile; Data Call-in (DCI) Date(s): 6/14/91; AI Status: OPP has completed a Reregistration Eligibility Decision (RED) for the case/AI.
Studies were conducted to characterize the absorption, disposition, metabolism, and excretion of 1,2-dibromo-2,4-dicyanobutane (BCB; methyldibromoglutaronitrile) following iv, oral, and topical administration to male Fischer 344 rats. Following iv administration of (14)C-BCB (8 mg/kg, 120 muCi/kg), no parent compound was detected in the blood; its debrominated metabolite, 2-methyleneglutaronitrile (2-MGN; Cmax 7.3 mug/mL), was observed up to 1 hr. Within 72 hr, greater than 60% of the dose was excreted in the urine and 4.1% in the feces, and 6.6% was exhaled as (14)CO2. ... Following oral administration of (14)C-BCB (80 mg/kg, 100 muCi/kg), approximately 85% of the dose was absorbed, whereas 72% of the dosed radioactivity was recovered in the urine and 9.7% in the feces, 7.5% was exhaled as (14)CO2, 3.5% bound to tissues, and 2.6% bound to blood.
The absorption of Methyldibromo Glutaronitrile over a 6 hr post-application period was evaluated. (14)C-Methyldibromo Glutaronitrile (99% pure, specific activity of 15.05 mCi/mmol), in 250 uL of either water or sunscreen formulation, was applied to samples of excised skin from Sprague-Dawley rats and humans such that the concentration loaded was established to be 0.08 mg/sq m of skin surface (radioactivity level of at least 5- 10 uCi/skin preparation). While the specific composition of the sunscreen formulation is not reported, 63% of it was water. Effluents were collected every 15 min for 6 hr. At the end of the assay the skin discs were combusted to determine radioactivity content contained therein. At 6 hr contact time, Methyldibromo Glutaronitrile in the sunscreen formulation was absorbed by human skin to about 0.9%; an additional 2% was detected via combustion of the discs. ... The test material in the sunscreen vehicle was absorbed to a slightly greater extent by female rat skin, where an average of 1.5% of the applied radioactivity was collected in the effluent after 6 hr, with an additional 3% being found in the discs. Methyldibromo Glutaronitrile in aqueous solution was more readily absorbed by both human and female rat skin, with approximately 33% being absorbed by human skin after 6 hr and 25% absorbed by female rat skin. Combustion of the skin discs detected an additional 13% radioactivity in the human samples and 10% in the rat (male and female). ... Of note is that when the chambers were stoppered to prevent vehicle evaporation, the radioactivity recovered in the effluent from human skin exposed to an aqueous solution dropped from the average of 33% to 16%.
Groups of 10 rats (five of each sex; strain and weight not specified) were dosed with (14)C-Methyldibromo Glutaronitrile according to the following procedures, respectively: in single oral doses of 5 and 200 mg/kg, daily oral doses of 5 mg/kg for 15 days, or a single intravenous dose at 5 mg/kg. Excretion via the urine accounted for recovery of >64.6% of radioactivity in all cases. At 168 hr post-exposure, and in all dose groups, the whole blood contained the highest levels of radioactivity. When three male rats were tested following a single oral administration of 5 mg/kg, the peak mean blood level of radioactivity (4.34 ug equiv/g) was measured at 8 hr. This level declined to 2.34 ug equiv/g at 48 hr and 0.75 ug equiv/g at 168 hr. At the time of maximum tissue concentration (8 hr), the gastrointestinal tract and kidneys contained the highest levels of radioactivity. The concentration in other tissues/locations were generally lower than in plasma, with the exception of whole blood. At 48 hr, the highest mean levels of radioactivity were associated with whole blood.
For more Absorption, Distribution and Excretion (Complete) data for 1,2-DIBROMO-2,4-DICYANOBUTANE (6 total), please visit the HSDB record page.
CIR ingredient: Methyldibromo Glutaronitrile
Euxyl K-400 is a biocide used in cosmetics, cleaning solutions, glues, paints, and metalworking fluids. Sensitization reported in masseurs, a beautician, an offset printer, machinists, and a hospital cleaner; [Kanerva, p. 1795]
Metal Machining [Category: Heat or Machine]
For 1-bromo-1-(bromomethyl)-1,3-propanedicarbonitrile (USEPA/OPP Pesticide Code: 111001) ACTIVE products with label matches. /SRP: Registered for use in the U.S. but approved pesticide uses may change periodically and so federal, state and local authorities must be consulted for currently approved uses./
Preservative for latex paints, adhesives, latex emulsions, dispersed pigments, joint cements, metal working fluids.
Methyldibromo Glutaronitrile is used in cosmetic formulations as a preservative.
Data in industry submissions indicate that Methyldibromo Glutaronitrile is used in cosmetic products as a 98.5% pure substance. Impurities found are as follows: water 1.5% (maximum); bromide 0.1% (maximum); total organic impurities 100 ppm (maximum); and iron 5 ppm (maximum).
Methyldibromoglutaronitrile is prepared by reacting bromine with 2-methyleneglutaronitrile at temperatures below 30 °C.
Preparation: S.J. Lederer, DE 2164723 corresponding to US 3833731 (1972, 1974 to Merck & Co.)
Beschreibung1,2-Dibromo-2,4-dicyanobutane is the main sensitizer of Euxyl K400, a widely used preservative agent in cosmetics, toiletries or metalwork fluids. Methyldibromo glutaronitrile (MDBGN), also known as dibromocyanobutane, is to be found in the preservative system Euxyl K 400 (also called Tektamer 38), which is a mix of MDBGN and phenoxyethanol in a ratio of 1:4. Euxyl K 400 is a broad‐spectrum preservative with activity against fungi and bacteria. MDBGN is nearly always the allergen when sensitization to Euxyl K 400 occurs.
Verwenden1,2-Dibromo-2,4-dicyanobutane is a preservative for metalworking fluids, cosmetics, adhesives, latex emulsions and paints, dispersed pigments and detergents; active ingredient in Euxyl K 400 and Tektamer 38.
DefinitionChEBI: An organobromine compound that consists of pentanedinitrile bearing bromo and bromomethyl substituents at position 2.