HuagongsheHuagongshe Chemie-Druckbericht · Nur für Forschungszwecke
Octansäure-2,6-dibrom-4-cyanphenylester
nph1320 · rp-16272 · brominalw · 'LGC' (1610) · Bromoxynil-oct · Bromoxynil octanoa · BROMOXYNIL-OCTANOATE · Bromoxynil Octanoate EC
Identifikatoren & physikalische Daten
| CAS No. | 1689-99-2 |
|---|---|
| Summenformel | C15H17Br2NO2 |
| Durchschnittliche Molmasse | 403,11 g/mol |
| Monoisotopische Masse | 400,96260298 g/mol |
| SMILES | CCCCCCCC(=O)Oc1c(Br)cc(C#N)cc1Br |
| InChIKey | DQKWXTIYGWPGOO-UHFFFAOYSA-N |
| PubChem CID | 15533 |
| ChEMBL | CHEMBL1903970 |
| EC No. | 216-885-3 |
| DTXSID | DTXSID7023932 |
| Lokaler Name | Octansäure-2,6-dibrom-4-cyanphenylester |
Chemische & physikalische Eigenschaften
| XLogP | 5,8 |
|---|---|
| Polarare Oberfläche (TPSA) | 50,1 |
| H-Brücken-Donoren | 0 |
| H-Brücken-Akzeptoren | 3 |
| Frei drehbare Bindungen | 8 |
| Schwere Atome | 20 |
| Formalladung | 0 |
| Komplexität | 341 |
| SpringerMaterials Properties | Fusion temperature |
| Pestizide | Pesticide -> EPA IRISPesticides -> Herbicides, OtherEnvironmental transformation -> Pesticides (parent, predecessor) |
| LogP (Verteilungskoeffizient) | log Kow = 5.46.1 |
| Geruch | Characteristic odor |
| Color/Form | Cream, waxy solidClear, amber waxy solid |
| Löslichkeit | In water, 0.08 mg/L at 25 °CIn chloroform 800, xylene, dimethylformamide 700, ethyl acetate 620, cyclohexanone 550, carbon tetrachloride 500, n-propanol 120, acetone, ethanol 100 (all in g/L 20-25 °C)30μg/L at 20℃ |
| Flammpunkt | 102 °F, 39 °C (TCC) |
| Decomposition | When heated to decomposition it emits toxic fumes of /nitrogen oxide and hydrogen bromide/. |
| Schmelzpunkt | 45-46 °C45-46°C |
| Dampfdruck | 0.0000048 [mmHg]0.64 mPa (4.8X10-6 mm Hg) at 25 °C0Pa at 40℃ |
| Henry-Konstante | Henry's Law constant = 3.2X10-5 atm cu m/mol at 25 °C /Estimated/3.1×10-1 mol/(m3Pa) at 25℃, Duchowicz et al. (2020) |
| Physical Description | Bromoxynil octanoate, [solid] appears as a solid. Used as a selective contact herbicide.[Merck Index] Nearly white crystalline solid[MSDSonline] |
| Siedepunkt | 424.6±45.0 °C(Predicted) |
| Dichte | 1.6040 (rough estimate) |
| Brechungsindex | 1.6220 (estimate) |
| Lagerbedingungen | Sealed in dry,Room Temperature |
| Aggregatzustand | Solid |
| Farbe | White to off-white |
| BRN | 2756636 |
| InChI | InChI=1S/C15H17Br2NO2/c1-2-3-4-5-6-7-14(19)20-15-12(16)8-11(10-18)9-13(15)17/h8-9H,2-7H2,1H3 |
| InChIKey | DQKWXTIYGWPGOO-UHFFFAOYSA-N |
| SMILES | C(OC1=C(Br)C=C(C#N)C=C1Br)(=O)CCCCCCC |
| LogP (Verteilungskoeffizient) | 5.9 at 20℃ |
| CAS Datenbank | 1689-99-2(CAS DataBase Reference) |
| NIST chemische Informationen | octanoic acid, 2,6-dibromo-4-cyanophenyl ester(1689-99-2) |
| EPA chemische Informationen | Bromoxynil octanoate (1689-99-2) |
Sicherheit & Vorschriften
| GHS-Einstufung | DangerH302: Harmful if swallowed [Warning Acute toxicity, oral]P203, P261, P264, P270, P271, P272, P273, P280, P301+P317, P302+P352, P304+P340, P316, P318, P321, P330, P333+P317, P362+P364, P391, P403+P233, P405, and P501 (click each P-code to see the statement)H301+H331 (20.7%): Toxic if swallowed or if inhaled [Danger Acute toxicity, oralacute toxicity, inhalation]P203, P261, P264, P270, P271, P272, P273, P280, P301+P316, P301+P317, P302+P352, P304+P340, P316, P317, P318, P321, P330, P333+P317, P362+P364, P391, P403+P233, P405, and P501 (click each P-code to see the statement) |
|---|---|
| Regulatorische Informationen | Hazard Traits - Developmental ToxicityCommission Regulation No 844/2012Status: Active Update: 13-01-2022 https://echa.europa.eu/registration-dossier/-/registered-dossier/33062Bromoxynil octanoate: Does not have an individual approval but may be used under an appropriate group standardThe New Jersey Worker and Community Right to Know Act requires public and private employers to provide information about hazardous substances at their workplaces. (N.J.S.A. 34:5A-1 et. seq.) |
| Weitere Sicherheitsinformationen | IMAP assessments - Octanoic acid, 2,6-dibromo-4-cyanophenyl ester: Environment tier I assessment |
| DOT-Kennzeichnung | Poison |
| Brandgefahren | Excerpt from ERG Guide 151 [Substances - Toxic (Non-Combustible)]: |
| Gesundheitsgefahren | Excerpt from ERG Guide 151 [Substances - Toxic (Non-Combustible)]: |
| Gefahrenübersicht | A mild skin and eye irritantMay cause skin sensitizationEffects in a 13 week feeding study with rats include decrease in body weight (not associated with decrease in food intake), increased kidney and liver weights, hematological changes, and myocardial degeneration and necrosisFour workers in a manufacturing plant making both bromoxynil and ioxynil developed typical symptoms of uncoupler poisoning including excessive perspiration, thirst, fever, emesis, myalgia, and weight loss. ... The effects reversed rapidly after exposure ceased. [HSDB] May cause skin sensitization[eChemPortal: ESIS] May cause irritation[MSDSonline] See Bromoxynil. |
| Reaktive Gruppe | Esters, Sulfate Esters, Phosphate Esters, Thiophosphate Esters, and Borate Esters |
| Special Reports | USEPA/Office of Pesticide ProgramsReregistration Eligibility Decision Document - Bromoxynil. EPA738-R-98-013 December 1998. 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 February 1, 2005: http://www.epa.gov/pesticides/reregistration/status.htm] |
| FIFRA-Anforderungen | Based on the reviews of the generic data for the active ingredient bromoxynil, the Agency has sufficient information on the health effects of bromoxynil and on its potential for causing adverse effects in fish and wildlife and the environment. The Agency has determined that bromoxynil products, labeled and used as specified in this Reregistration Eligibility Decision, will not pose unreasonable risks to humans or the environment. Therefore, the Agency concludes that products containing bromoxynil for all uses are eligible for reregistration, provided the registrant follows all requirements as set forth in this document.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. Bromoxynil octanoate is found on List B. Case No: 2070Pesticide type: herbicideCase Status: OPP is reviewing data from the pesticide's producers regarding its human health and/or environmental effects, or OPP is determining the pesticide's eligibility for reregistration and developing the RED document.Active ingredient (AI): bromoxynil octanoateData Call-in (DCI) Date(s): 6/5/91, 10/13/95AI Status: The producers of the pesticide have made commitments to conduct the studies and pay the fees required for reregistration, and are meeting those commitments in a timely manner.Tolerances are established for residues of the herbicide bromoxynil (3,5-dibromo-4-hydroxybenzonitrile) resulting from application of its octanoic and/or heptanoic acid ester in or on the following commodities: alfalfa, seedingbarley, grainbarley, strawcanarygrass, annual, seedcorn, field, stovercorn, fodder (green)corn, graincorn, grain, fieldcorn, stoverflax, seedflax, strawgarlicgrass, canary, annual, strawmint hayoat, forageoat, grainoat, strawonion, dry bulbrye, foragerye, grainrye, strawsorghum, foragesorghum, grainsorghum, grain, stoverwheat, foragewheat, grainand wheat, straw.Tolerances are established for residues of the herbicide bromoxynil (3,5-dibromo-4-hydroxybenzonitrile) and its metabolite 3,5-dibromo-4-hydroxybenzoic acid (DBHA) resulting from application of its octanoic and/or heptanoic acid ester in or on the following commodities: cattle, fatcattle, meat byproductscotton gin byproductscotton, hullscotton, undelinted seedegggoat, fatgoat, meat byproductshot, fathog, meat byproductshorse, fathorse, meat byproductsmilkpoultry, fatpoultry, meat byproductssheep, fatsheep, meat byproductsand sheep, meat. |
| Reactivity Profile | BROMOXYNIL OCTANOATE, [SOLID] is an ester. Readily hydrolyzed to bromoxynil and octanoate at pH's exceeding 9. |
| Air and Water Reactions | No rapid reaction with air. No rapid reaction with water. |
| Hazard Classes and Categories | Acute Tox. 3 (31.4%)Reproductive toxicity - category 2Repr. 2 |
| Brandbekämpfung | Excerpt from ERG Guide 151 [Substances - Toxic (Non-Combustible)]: |
| Erste Hilfe | Excerpt from ERG Guide 151 [Substances - Toxic (Non-Combustible)]: |
| Expositionsschutz und Persönliche Schutzausrüstung | 2.0 [mg/m3], inhalable fraction, as CN[German Research Foundation (DFG)] |
| Brandbekämpfungsverfahren | If material on fire or involved in fire: Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Use "alcohol" foam, dry chemical or carbon dioxide.Carbon dioxide or dry chemical for small fires. Water-spray or alcohol type foam for large fires. |
| Lagerbedingungen | Handle carefully ... Do not use or store near heat or open flame. Store at temperature above 3 °F. If allowed to freeze, remix before using. Do not contaminate water, food or feed by storage or disposal of this chemical. |
| Reinigungsverfahren | Environmental considerations: Land spill: Dig a pit, pond, lagoon, holding area to contain liquid or solid material. /SRP: If time permits, pits, ponds, lagoons, soak holes, or holding areas should be sealed with an impermeable flexible membrane liner./ Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water.Environmental considerations: Water spill: Use natural barriers or oil spill control booms to limit spill travel. Use natural deep water pockets, excavated lagoons, or sand bag barriers to trap material at bottom. Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates. |
| Freisetung ohne Brand | Excerpt from ERG Guide 151 [Substances - Toxic (Non-Combustible)]: |
| Entsorgungsverfahren | SRP: The most favorable course of action is to use an alternative chemical product with less inherent propensity for occupational exposure 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 qualitypotential migration in soil or watereffects on animal, aquatic, and plant lifeand conformance with environmental and public health regulations. |
| Preventive Measures | SRP: Contaminated protective clothing should be segregated in such a manner so that there is no direct personal contact by personnel who handle, dispose, or clean the clothing. Quality assurance to ascertain the completeness of the cleaning procedures should be implemented before the decontaminated protective clothing is returned for reuse by the workers. Contaminated clothing should not be taken home at end of shift, but should remain at employee's place of work for cleaning.SRP: The scientific literature for the use of contact lenses in industry is conflicting. The benefit or detrimental effects of wearing contact lenses depend not only upon the substance, but also on factors including the form of the substance, characteristics and duration of the exposure, the uses of other eye protection equipment, and the hygiene of the lenses. However, there may be individual substances whose irritating or corrosive properties are such that the wearing of contact lenses would be harmful to the eye. In those specific cases, contact lenses should not be worn. In any event, the usual eye protection equipment should be worn even when contact lenses are in place.If material not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers.Personnel protection: Avoid breathing dusts, and fumes from burning material. Keep upwind. Avoid bodily contact with the material. ... Do not handle broken packages unless wearing appropriate personal protective equipment. Wash away any material which may have contacted the body with copious amounts of water or soap and water. If contact with the material anticipated, wear appropriate chemical protective clothing. |
| Isolation and Evacuation | Excerpt from ERG Guide 151 [Substances - Toxic (Non-Combustible)]: |
| Allowable Tolerances | Tolerances are established for residues of the herbicide bromoxynil (3,5-dibromo-4-hydroxybenzonitrile) resulting from application of its octanoic and/or heptanoic acid ester in or on the following commodities: alfalfa, seeding 0.1 ppmbarley, grain 0.1 ppmbarley, straw 0.1 ppmcanarygrass, annual, seed 0.1 ppmcorn, field, stover 0.1 ppmcorn, fodder (green) 0.1 ppmcorn, grain 0.1 ppmcorn, grain, field 0.1 ppmcorn, stover 0.1 ppmflax, seed 0.1 ppmflax, straw 0.1 ppmgarlic 0.1 ppmgrass, canary, annual, straw 0.1 ppmmint hay 0.1 ppmoat, forage 0.1 ppmoat, grain 0.1 ppmoat, straw 0.1 ppmonion, dry bulb 0.1 ppmrye, forage 0.1 ppmrye, grain 0.1 ppmrye, straw 0.1 ppmsorghum, forage 0.1 ppmsorghum, grain 0.1 ppmsorghum, grain, stover 0.1 ppmwheat, forage 0.1 ppmwheat, grain 0.1 ppmand wheat, straw 0.1 ppm.Tolerances are established for residues of the herbicide bromoxynil (3,5-dibromo-4-hydroxybenzonitrile) and its metabolite 3,5-dibromo-4-hydroxybenzoic acid (DBHA) resulting from application of its octanoic and/or heptanoic acid ester in or on the following commodities: cattle, fat 1 ppmcattle, meat byproducts 3.5 ppmcattle, meat 0.5 ppmcotton gin byproducts 7.0 ppmcotton, hulls 5.0 ppmcotton, undelinted seed 1.5 ppmegg 0.05 ppmgoat, fat 1 ppmgoat, meat byproducts 3.5 ppmgoat, meat 0.5 ppmhot, fat 1 ppmhog, meat byproducts 3.5 ppmhog, meat 0.5 ppmhorse, fat 1 ppmhorse, meat byproducts 3.5 ppmhorse, meat 0.5 ppmmilk 0.1 ppmpoultry, fat 0.05 ppmpoultry, meat byproducts 0.3 ppmpoultry, meat 0.05 ppmsheep, fat 1 ppmsheep, meat byproducts 3.5 ppmand sheep, meat 0.5 ppm. |
| Permissible Exposure Limit (PEL) | 5.0 [mg/m3], as CN |
| Ökotoxizitätswerte | LD50 Anas platyrhynchos (Mallard duck) oral 200 mg/kg/10 daysLC50 Anas platyrhynchos (Mallard duck) dietary 2150 ppm/8 daysLD50 Apis mellifera (Honey bee) topical 2 ug/bee/48 hrLD50 Colinus virginianus (Northern bobwhite) oral 170 mg/kg/21 daysFor more Ecotoxicity Values (Complete) data for BROMOXYNIL OCTANOATE (17 total), please visit the HSDB record page. |
| Umweltverhalten | TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 21,000(SRC), determined from a log Kow of 5.4(2) and a regression-derived equation(3), indicates that bromoxynil octanoate is expected to be immobile in soil(SRC). In an aged soil leaching study, bromoxynil octanoate residues were found to not be mobile in four soils and aquatic sediment(4). A Kd of 7 mL/g (Koc = 1,003) was reported in soils with 1.2% organic matter(4). Volatilization of bromoxynil octanoate from moist soil surfaces is expected(SRC) given an estimated Henry's Law constant of 3.2X10-5 atm-cu m/mole(SRC), derived from its vapor pressure, 4.8X10-6 mm Hg(5), and water solubility, 0.08 mg/L(5). However, adsorption to soil is expected to attenuate volatilization(SRC). Bromoxynil octanoate is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure of 4.8X10-6 mm Hg(5) Chemical hydrolysis, photolytic degradation, and microbially-mediated degradation are important environmental processes for bromoxynil octanoate(4). 14C labeled bromoxynil octanoate was reported to degrade in sandy loam soil with a half-life of 2 daysthe major degradation product was CO2, which accounted for 64.28% of the applied radioactivity after 90 days(4). In soil photolysis experiments, bromoxylnil octanoate was found to degrade with a half-life of 2.6 days when irradiated with a xenon arc lampa degradation half-life of 3.6 days was observed in a dark control(4). Degradation in the dark control suggests that degradation processes in addition to photolysis (e.g., hydrolysis or microbial degradation) were also occurring (4). A half-life of <12 hrs was reported when treated sandy loam soil was flooded with pond water and then aerobically incubatedtest compound concn was 87% of applied at time zero, declining to undetectable levels in 48 hrs(4). Field dissipation half-lives ranging from 0.5 to 28 days have been reported(5). In degradation experiments using 5 soil types (sandy loam, acid sand, organic silt, sandy loam, and clay) in a soil perfusion apparatus and C14 (cyano) bromoxynil octanoate half-lives ranged from 7 to 22 days(6). In experiments using C14 (ring) bromoxynil octanoate half-live ranged from 10-12 days in clay and sandy loam soils(6). The degradation of bromoxynil octanoate in two soils, a heavy clay and a sandy loam, at 85% of field capacity moisture and at 20 °C, was studied(7). In both soils bromoxynil octanoate was rapidly degraded to bromoxynil, which was then also rapidly degradedafter 7 days >90% of the original application had disappeared(7). Three pesticides, including bromoxynil octanoate, were applied to two field plots in Saskatchewanafter 10 weeks none of the pesticides could be detected in the top 10 cm of soil(7).AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 21,000(SRC), determined from a log Kow of 5.4(2) and a regression-derived equation(3), indicates that bromoxynil octanoate is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(3) based upon an estimated Henry's Law constant of 3.2X10-5 atm-cu m/mole(SRC), derived from its vapor pressure, 4.8X10-6 mm Hg(3), and water solubility, 0.08 mg/L(3). Using this Henry's Law constant and an estimation method(4), volatilization half-lives for a model river and model lake are 2.5 and 25 days, respectively(SRC). However, volatilization from water surfaces is expected to be attenuated by adsorption to suspended solids and sediment in the water column(SRC). The volatilization half-life from a model pond is about 130 years when adsorption is considered(5). In addition the rapid hydrolysis and photolysis of bromoxynil octanoate may attenuate its volatilization from water surfaces(SRC). Hydrolysis half-lives of 34.1, 11.5, and 1.7 days at pH 5, 7, and 9 have been reported for bromoxynil octanoate(6). A photolytic half-life of 4.6 days at pH 5 was reported for bromoxynil octanoate(6). A BCF of 230 (whole fish) was reported in bluegill sunfish when continuously exposed to 14C radiolabeled bromoxynil octanoate at 1.3-4.6 ug/L(6). According to a classification scheme(7), this BCF suggests the potential for bioconcentration in aquatic organisms is high, provided the compound is not metabolized by the organism(SRC). Bromoxynil octanoate added to sandy loam soil flooded with pond water degraded with a half-life of <12 hours under aerobic conditions at 25 °C in the dark (6). Bromoxynil octanoate was reported to degrade with a half-life of 3.7 days in a sandy loam sediment under anaerobic conditions(6). The environmental fate of bromoxynil octanoate was investigated in small ponds in the wetland area of the Delta Waterfowl and Wetlands Research Station in Canada(8). Bromoxynil octanoate, along with bromoxynil butyrate were sprayed on the pondssampling showed that bromoxynil octanoate persisted in the surface microlayer (0-1 mm) with half-lives of 0.8-2.5 hours(8). In subsurface waters (10-20 cm depth) the major forms of the pesticides were bromoxynil (phenol) and its monobromo analog(8).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), bromoxynil octanoate, which has a vapor pressure of 4.6X10-6 mm Hg at 25 °C(2), will exist in both the vapor and particulate phases in the particulate phase. Vapor-phase bromoxynil octanoate 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 2.2 days(SRC), calculated from its rate constant of 7.4X10-12 cu cm/molecule-sec at 25 °C(SRC) that was derived using a structure estimation method(3). Particulate-phase bromoxynil octanoate may be removed from the air by wet and dry deposition(SRC). While bromoxynil octanoate undergoes aqueous photolysis with half-lives of 4-5 hours(4), no data were found regarding direct photolysis in air(SRC). |
| Unerwünschte Wirkungen | Occupational hepatotoxin - Secondary hepatotoxins: the potential for toxic effect in the occupational setting is based on cases of poisoning by human ingestion or animal experimentation. |
| Ökotoxizitätsauszüge | /AQUATIC SPECIES/ Fathead minnows showed decreased larval growth, survival and embryo hatching success when tested in fish early life stage tests. NOEL=18 ppbLOEL=39 ppbMATC=26 ppb. /97.2% Bromoxynil octanoate/ /from table//AQUATIC SPECIES/ The acute toxicities of technical grade bromoxynil octanoate and two commercial formulations, Buctril and Bronate, to <24 hr old neonate Daphnia magna (Straus) were determined in soft, hard, and oligosaline water. In addition, effects of life stage, feeding, aging the herbicide, and exposure duration on bromoxynil octanoate toxicity to daphnids were investigated. Regardless of formulation, life stage, and water quality, bromoxynil octanoate was found to be extremely to highly toxic to daphnids in standard tests48 hr EC50 values ranged from 41 to 161 ug/l. Bromoxynil octanoate was the most toxic to neonates in soft water and the least toxic in hard water. The acute toxicities of the three bromoxynil herbicides to a given age group of daphnids were similar within the same water type. Overall, neonates and 7 day old adults were more sensitive than 14 or 15 day old adults to each herbicide. Feeding daphnids during the toxicity test significantly decreased bromoxynil octanoate toxicity compared to not feeding them. Aging bromoxynil octanoate (as Buctril) in hard water decreased its toxicity, and the rate of deactivation was rapid, with an estimated half-life of biological activity of 13 hr. Daphnids immobilized by exposures to toxic bromoxynil octanoate concn for : 6 hr recovered their mobility, whereas exposures of 18 and 24 hr to bromoxynil octanoate produced toxic effects in daphnids similar to those exposed for 48 hr. These results indicated that standard continuous exposure tests may not adequately predict the acute toxicity of bromoxynil octanoate to freshwater animals in the field./AQUATIC SPECIES/ Two chronic toxicity tests were conducted in which Daphnia magna were either continuously or intermittently exposed to bromoxynil octanoate (as Buctril) for 28 days. In the intermittent exposure test, daphnids were exposed to daily pulses of bromoxynil octanoate with 24 hr mean concentration equal to those in the continuous exposure test, and the peak concentration were three times the 24 hr mean values. After 28 days of continuous exposure to bromoxynil octanoate, survival of daphnids was reduced at 80 ug/L, whereas mean number of young per adult, intrinsic rate of natural increase, and mean weight of adults were all reduced at 40 ug/L. Intermittent exposures to daily pulses of bromoxynil octanoate for 28 days caused reduced survival of daphnids at 24 hr mean concentration : 40 ug/L and reduced mean number of young per adult, intrinsic rate of natural increase, and mean weight of adults at 24 hr mean concentration 20 ug/L. The estimated geometric mean-maximum acceptable toxicant concentration of bromoxynil octanoate based on 24 hr mean nominal values were 28 ug/L for continuous exposures and 14 ug/L for intermittent exposures. These results demonstrated that continuous exposure studies may not be adequate in assessing herbicide toxicity to aquatic biota when concentrations fluctuate temporally./FIELD STUDIES/ The toxicity of a single spray application of a 1:1 mixture of bromoxynil octanoate and bromoxynil butyrate were studied in fifteen 0.01 ha ponds located in the Delta marsh area of Manitoba. Two ponds were treated at 2.5 ug/L and two treated at 50 ug/L (nominal concentration). Complete mortality of brook sticklebacks (Culaea inconstans), held in cages in subsurface waters, occurred within 24 hr at the two highest treatment levels (nominal concentration of 100 and 500 ug/L). Mortality of caged Hyalella azteca at the highest dose levels ranged from 85 to 95% at 50 hr. |
| EPA IRIS Information | Bromoxynil octanoate2 x 10 ^-2 mg/kg-day |
| Soil Adsorption/Mobility | The Koc of bromoxynil octanoate is estimated as 21,000(SRC), using a log Kow of 5.4(1)and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that bromoxynil ocatonate is expected to be immobile mobility in soil. In an aged soil leaching study, bromoxynil octanoate residues were found to not be mobile in four soils and aquatic sediment(4). A Kd of 7 mL/g (Koc = 1,003) was reported in soils with 1.2% organic matter(4). |
| Human Toxicity Excerpts | /SIGNS AND SYMPTOMS/ Four workers in a manufacturing plant making both bromoxynil and ionoxynil developed typical symptoms of uncoupler poisoning including excessive perspiration, thirst, fever, emesis, myalgia, and weight loss. ... The effects reversed rapidly after exposure ceased. |
| Artificial Pollution Sources | Bromoxynil octanoate's production may result in its release to the environment through various waste streamsits use as a herbicide(1) will result in its direct release to the environment(SRC). |
| Environmental Biodegradation | 14C-Labeled bromoxynil octanoate was reported to degrade in sandy loam soil with a half-life of 2 daysthe major degradation product was CO2, which accounted for 64.28% of the applied radioactivity after 90 days(1). In soil photolysis experiments, bromoxylnil octanoate was found to degrade with a half-life of 2.6 days when irradiated with a xenon arc lampa degradation half-life of 3.6 days was observed in a dark control(1). Degradation in the dark control suggests that degradation processes in addition to photolysis (e.g., hydrolysis or microbial degradation) were occurring(1). A half-life of <12 hrs was reported when treated sandy loam soil was flooded with pond water and then aerobically incubatedtest compound concn was 87% of applied at time zero, declining to undetectable levels in 48 hrs(1). Field dissipation half-lives ranging from 0.5 to 28 days have been reported(2). In degradation experiments using 5 soil types (sandy loam, acid sand, organic silt, sandy loam, and clay) in a soil perfusion apparatus and C14 (cyano) bromoxynil octanoate half-lives ranged from 7 to 22 days(3). In experiments using C14 (ring) bromoxynil octanoate half-live ranged from 10-12 days in clay and sandy loam soils(3). The degradation of bromoxynil octanoate in two soils, a heavy clay and a sandy loam, at 85% of field capacity moisture and at 20 °C, was studied(4). In both soils bromoxynil octanoate was rapidly degraded to bromoxynil, which was then also rapidly degradedafter 7 days >90% of the original application had disappeared(4). Three pesticides, including bromoxynil octanoate, were applied to two field plots in Saskatchewanafter 10 weeks none of the pesticides could be detected in the top 10 cm of soil(4). Bromoxynil octanoate was reported to degrade with a half-life of 3.7 days in a sandy loam sediment under anaerobic conditions(1). The environmental fate of bromoxynil octanoate was investigated in small ponds in the wetland area of the Delta Waterfowl and Wetlands Research Station in Canada(5). Bromoxynil octanoate, along with bromoxynil butyrate were sprayed on the pondssampling showed that bromoxynil octanoate persisted in the surface microlayer (0-1 mm) with half-lives of 0.8-2.5 hours(5). In subsurface waters (10-20 cm depth) the major forms of the pesticides were bromoxynil (phenol) and its monobromo analog(5). |
| Environmental Bioconcentration | A BCF of 230 (whole fish) was reported in bluegill sunfish when continuously exposed to 14C radiolabeled bromoxynil octanoate at 1.3-4.6 ug/L(1). According to a classification scheme(2), this BCF suggests the potential for bioconcentration in aquatic organisms is high, provided the compound is not metabolized by the organism(SRC). |
| Volatilization from Water/Soil | The Henry's Law constant for bromoxynil octanoate is estimated as 3.2X10-5 atm-cu m/mole(SRC) derived from its vapor pressure, 4.8X10-6 mm Hg(1), and water solubility, 0.08 mg/L(1). This Henry's Law constant indicates that bromoxynil octanoate is expected to volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(3) is estimated as 2.5 days(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 25 days(SRC). However, volatilization from water surfaces is expected to be attenuated by adsorption to suspended solids and sediment in the water column(SRC). The estimated volatilization half-life from a model pond is 130 years if adsorption is considered(3). Bromoxynil octanoate is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(3). |
| Non-Human Toxicity Excerpts | /LABORATORY ANIMALS: Subchronic or Prechronic Exposure/ Bromoxynil octanoate technical grade powder (no purity stated)doses of 0, 20, 50, 125, 312, 781 or 1953 ppm fed in the diet to groups of 10/sex Sprague-Dawley rats per group with 30/sex in controls, for 13 weeks. Increased kidney and liver weights at 781 and 1953 ppm in males and females and changed blood profile at 1953 ppm. The absolute weight of the thyroid and pituitary were decreased in the malesthe respective LOELs were 125 ppm and 312 ppm. Paradoxically, increased absolute thyroid weight was seen in the 20 ppm and 50 ppm female groups and increased absolute pituitary weight was seen in the 50 ppm female group. Since an increasing dose response was not seen, both of these increases may be spurious. However, the magnitude of the difference from the control values was impressive and may be indicative of a significant biological effect./LABORATORY ANIMALS: Subchronic or Prechronic Exposure/ Bromoxynil Octanoate (95.2% purity) was administered in the diet at 0, 150, 600, 1100 and 2100 ppm to 20-30 Crl:CD BR VAF/Plus rats/sex/group /for a period of 13-weeks/. The only deaths in the study occurred in the groups given the 2100 ppm diet. Twenty six females and nine males in the 2100 ppm groups (30/sex) were found dead, mainly on study days 3-5. The survivors in the 2100 ppm groups were sacrificed on study day 9. Each of the survivors had lost 6-34 grams in bodyweight during the first study week. Other findings for the survivors(both sexes) included: greatly decreased platelet countincreased RBC count, hemoglobin concentration and hematocritincreased blood urea nitrogen, SGOT and SGPTdecreased serum globulinlymphocytic necrosis and degeneration in the spleen, thymus, and mesenteric lymph nodehematopoietic depletion in the bone marrowand stomach hemorrhages and congestion. Bodyweight effects also were seen in the lower dose groups: the 600 ppm and 1100 ppm females had mean BWs during study weeks 2-14 that were 90-94% and 78-81% of the control values, respectivelythe 1100 ppm males had mean BWs during study weeks 2-14 that were 84-87% of the control values. These BW effects were not accompanied by a decrease in food consumption, except for the first study week. The 1100 ppm female group exhibited the following hematological effects: decreased platelet count and increased RBC count, hemoglobin concentration and hematocrit in the testing done at study week 5and an increased lymphocyte count in the testing done at study week 14. The following clinical chemistry effects were seen at study week 5, but not study week 14: an increase in serum albumin in the 150 ppm and 600 ppm female groups and in the 600 ppm male groupdecreased total bilirubin in the 600 ppm and 1100 ppm female groupsdecreased serum potassium in the 1100 ppm female groupdecreased serum chloride in the 600 ppm and 1100 ppm female groups. The following clinical chemistry effects were seen at study weeks 5 and 14: a decrease in total serum protein in the 1100 ppm groups (both sexes)a decrease in the globulin concentration in the 1100 ppm groups (both sexes). At study week 14, the 1100 ppm groups (both sexes) also exhibited an increase in serum alkaline phosphatase. No effects on blood urea nitrogen, SGOT or SGPT were noted in the testing done at study weeks 5 and 14. Increased absolute liver weight and decreased absolute right adrenal weight were seen in the 600 and 1100 ppm female groupsOrgan weight was not determined for the heart, pituitary or thyroid. Myocardial degeneration and necrosis were observed in both sexes. The incidence rate in the males was: 0 ppm, 5/30150 ppm, 7/20600 ppm, 8/20 (p = 0.066)and 1100 ppm, 11/20(p = 0.006). The incidence rate in the females was: 0 ppm, 3/30150 ppm, 3/20600 ppm, 3/20and 1100 ppm, 10/20 (p = 0.002). Myocardial lesions also were noted in two 2100 ppm females that were found dead on study days 3 and 4. Retinal degeneration was seen in two 1100 ppm males (10% incidence rate)given the rarity of this lesion in rats of this age, this may be an incipient effect. NOAEL = 150 ppm (myocardial degeneration and necrosis in males, liver hypertrophy in females)./LABORATORY ANIMALS: Subchronic or Prechronic Exposure/ In a 13-wk subchronic feeding study, technical grade bromoxynil octanoate was administered in the diet to groups of 20-30 male and 20-30 female Sprague Dawley rats at dose levels of 0 (control), 150, 600 or 1100 ppm (equivalent to 0, 11, 45 or 91 mg/kg/day in males and 0, 13, 55 or 111 mg/kg/day in females). An additional group of 30 male and 30 female rats was started at a dose level of 2100 ppm, but was sacrificed during the first week of the study due to high mortality and signs of severe toxicity. No treatment related signs of toxicity were observed in males at 150 or 600 ppm. At 1100 ppm, the following effects were observed in males: decreased body weight gain, decreased serum total protein, decreased globulins, possibly increased thymic lymphocyte necrosis, and increased degeneration/necrosis of cardiac myofibers. No treatment-related effects were observed in females at 150 ppm. At 600 ppm, decreased body weight gain and increased liver weights were observed in females. At 1100 ppm, the following additional effects were also noted in females: decreased serum total protein, decreased globulins, possibly increased thymic lymphocyte necrosis, and increased degeneration/necrosis of cardiac myofibers. For male rats, the NOEL is 600 ppm (45 mg/kg/day) and the LOEL is 1100 ppm (91 mg/kg/day), based on decreased body weight gain, decreased serum total protein, decreased globulins and increased degeneration/necrosis of cardiac myofibers. For female rats, the NOEL is 150 ppm (13 mg/kg/day) and the LOEL is 600 ppm (55 mg/kg/day), based on decreased body weight gain and increased liver weights./LABORATORY ANIMALS: Subchronic or Prechronic Exposure/ In a 13-wk subchronic oral study, technical grade bromoxynil octanoate was administered orally in gelatin capsules to groups of 2 male and 2 female beagle dogs at dose levels of 0 (control), 0.43, 1.43 or 7.14 mg/kg/day. The only treatment-related effect observed in males and females in this study was decreased body weight gain. For males, mean absolute body weight gains from 0-13 weeks were +3.60, +2.80, +2.20 and +1.15 kg for the control, low, mid and high dose level groups respectively. These gains corresponded to 78%, 61% and 32% of the male control group (100%) for the low, mid and high dose level groups respectively. For females, the comparable mean absolute body weight gains were +2.90, +2.05, +1.75 and +0.55 kg. These gains corresponded to 71%, 60% and 19% of the female control group (100%). Although the % of body weight gain compared to controls was 78% for low dose level males and 71% for low dose level females, the corresponding differences in absolute body weight gains were actually <1 kg and since the low dose level animals appeared healthy throughout the entire study and showed no other sign of toxicity, it was concluded that the NOEL for both males and females in this study is 0.43 mg/kg/day and the LOEL is 1.43 mg/kg/day, based on decreased body weight gain.For more Non-Human Toxicity Excerpts (Complete) data for BROMOXYNIL OCTANOATE (18 total), please visit the HSDB record page. |
| Wassergefährdungsklasse (WGK) | 3 |
| TSCA-Inventar-Status | TSCA listed |
| UN-Transportnummer | 2588 |
| RTECS-Nr. | DI3325000 |
| R-Sätze (R) | 22-23-43-50/53-63 |
| Toxizität | LC50 (48-hour) for rainbow trout 150 μg/L (Hartley and Kidd, 1987), goldfish 460 μg/L and catfish 63 μg/L (Worthing and Hance, 1991)acute oral LD50 for rats 365 mg/kg (Hartley and Kidd, 1987). |
| Gefahrensymbole | TN,N,T |
| Sicherheitshinweise (S) | 36/37-45-60-61-63 |
| Gefahrenklasse | 6.1(b) |
| Verpackungsgruppe | III |
| Gefahrstoffdaten | 1689-99-2(Hazardous Substances Data) |
Anwendungen & Verwendung
Verwenden
Herbicide.