Bromomethane CAS #: 74-83-9 Revised By: RRD Toxicology Unit Revision Date: August 14, 2015

Bromomethane CAS #: 74-83-9 Revised By: RRD Toxicology Unit Revision Date: August 14, 2015

<p><strong>CHEMICAL UPDATE WORKSHEET </strong></p><p><strong>Chemical Name: CAS #: </strong><br><strong>Bromomethane 74-83-9 </strong><br><strong>Revised By: Revision Date: </strong></p><p>RRD Toxicology Unit August 14, 2015 </p><p><strong>(A) Chemical-Physical Properties </strong></p><p></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li><li style="flex:1"><strong>Reference Source </strong></li><li style="flex:1"><strong>Comments </strong></li></ul><p><strong>Molecular Weight (g/mol) Physical State at ambient temp Melting Point (˚C) </strong></p><p>94.94 Liquid <br>179 <br>94.94 Gas <br>EPI MDEQ EPI <br>EXP <br>-93.70 <br>3.50 <br>EXP EXP EXP EXP EXP EXP EST NA </p><p><strong>Boiling Point (˚C) </strong></p><p></p><ul style="display: flex;"><li style="flex:1">3.5 </li><li style="flex:1">EPI </li></ul><p></p><p><strong>Solubility (ug/L) </strong></p><p>1.45E+7 <br>1672 <br>1.42E-2 <br>1.18 <br>1.52E+07 1.62E+03 7.34E-03 <br>1.19 <br>EPI </p><p><strong>Vapor Pressure (mmHg at 25˚C) HLC (atm-m³/mol at 25˚C) Log Kow (log P; octanol-water) </strong></p><p>EPI EPI EPI </p><p><strong>Koc (organic carbon; L/Kg) Ionizing Koc (L/kg) </strong></p><p></p><ul style="display: flex;"><li style="flex:1">14.5 </li><li style="flex:1">13.22 </li><li style="flex:1">EPI </li></ul><p></p><ul style="display: flex;"><li style="flex:1">NR </li><li style="flex:1">NA </li></ul><p></p><p><strong>Diffusivity in Air (Di; cm</strong><sup style="top: -0.42em;"><strong>2</strong></sup><strong>/s) </strong></p><p></p><ul style="display: flex;"><li style="flex:1">0.08 </li><li style="flex:1">1.00E-01 </li></ul><p>1.3468E-05 <br>W9 W9 <br>EST EST </p><p><strong>Diffusivity in Water (Dw; cm</strong><sup style="top: -0.42em;"><strong>2</strong></sup><strong>/s) </strong></p><p>8.0E-6 </p><p></p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li><li style="flex:1"><strong>Reference Source </strong></li><li style="flex:1"><strong>Comments </strong></li></ul><p><strong>Soil Water Partition Coefficient (Kd; inorganics) </strong></p><p>NR NA 0.1 </p><ul style="display: flex;"><li style="flex:1">NR </li><li style="flex:1">NA </li><li style="flex:1">NA </li></ul><p>EXP EXP EXP EXP EXP EST EST EST EST </p><p><strong>Flash Point (˚C) </strong></p><p></p><ul style="display: flex;"><li style="flex:1">194 </li><li style="flex:1">PC </li></ul><p></p><p><strong>Lower Explosivity Level (LEL; unit less) Critical Temperature&nbsp;(K) </strong></p><p></p><ul style="display: flex;"><li style="flex:1">0.1 </li><li style="flex:1">CRC </li></ul><p>467.00 <br>5.71E+03 <br>1.6755 <br>2.80E-05 6.86E-05 4.47E-05 1.09E-04 <br>EPA2004 EPA2004 <br>CRC </p><p><strong>Enthalpy of Vaporization (cal/mol) Density (g/mL, g/cm3) </strong></p><p><strong>EMSOFT Flux Residential 2 m (mg/day/cm</strong><sup style="top: -0.42em;"><strong>2</strong></sup><strong>) </strong></p><p>2.69E-05 6.53E-05 3.83E-05 9.24E-05 <br>EMSOFT EMSOFT EMSOFT EMSOFT </p><p><strong>EMSOFT Flux Residential 5 m (mg/day/cm</strong><sup style="top: -0.42em;"><strong>2</strong></sup><strong>) EMSOFT Flux Nonresidential 2 m (mg/day/cm</strong><sup style="top: -0.42em;"><strong>2</strong></sup><strong>) EMSOFT Flux Nonresidential 5 m (mg/day/cm</strong><sup style="top: -0.42em;"><strong>2</strong></sup><strong>) </strong></p><p>2</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>(B) Toxicity Values/Benchmarks </strong></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p><strong>Reference Dose </strong></p><p></p><ul style="display: flex;"><li style="flex:1">1.4E-3 </li><li style="flex:1">2.0E-2 </li><li style="flex:1">OPP, 2013 </li></ul><p></p><p><strong>(RfD) (mg/kg/day) </strong></p><p>Rat subchronic gavage study (Danse et al., </p><p><strong>Tier 1 Source: EPA-OPP: </strong></p><p><strong>Basis: </strong>OPP is the more current than IRIS, PPRTV and ATSDR. <br>Complete <br>1984); NOAEL=1.4&nbsp;<strong>OPP </strong>chronic RfD = 0.022 mg/kg-day. mg/kg/day. UF=1000. Critical effect = epithelial <br><strong>Critical Study</strong>: Mertens, J. (1997) A 24-Month Chronic Dietary Study of Methyl Bromide in Rats: Final Report: Lab Project Number: WIL-49014. Unpublished study prepared by WIL Research Labs., Inc. 4972p. (44462501) <strong>Method(s)</strong>: In a combined chronic toxicity/carcinogenicity study (MRID hyperplasia of the&nbsp;44462501), microencapsulated methyl bromide was administered to 4 groups of </p><ul style="display: flex;"><li style="flex:1">forestomach. </li><li style="flex:1">male and female Crl:CD®(SD)BR rats for a period of 12 or 24 months (interim and </li></ul><p>main study, respectively) in the diet at concentrations of 0 (diet control), 0 (placebo control), 0.5, 2.5, 50, or 250 ppm&nbsp;(equivalent to 0, 0.02, 0.11, 2.20 and 11.10 mg/kg/day in males and 0, 0.03, 0.15, 2.92 and 15.12 mg/kg/day in females. Groups of 50 males and 50 females were designated for the main study and were treated for up to 104 weeks. Groups of 20 males and 20 females were sacrificed at 52 weeks in the diet control, placebo control, 50 ppm group and the 250 ppm group. <br>Entry date: 5/26/1988 </p><p><strong>RfD details </strong></p><p><strong>Critical effect</strong>: decreased&nbsp;body weight gain and food consumption in males </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL = 2.2 mg/kg-day (50 ppm) for </p><p>males <strong>Uncertainty Factors</strong>: UF&nbsp;= 100&nbsp;(10 each for intraspecies variability and interspecies extrapolation) <strong>Source and date: </strong>EPA-OPP, 9/13/2013.&nbsp;IRIS (2015) refers to OPP for toxicity updates of methylbromide. </p><p><strong>Tier 1 and 2 Sources</strong>: <strong>EPA:OPP: </strong>Other OPP values: </p><p>Per EPA-OPP (9/13/2013), </p><p><strong>1) acute&nbsp;RfD for females ages 13-50 years = 0.014 (1.4E-2) mg/kg-day: </strong></p><p>3</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p></p><p><strong>Critical Study (ies)</strong>: Breslin,&nbsp;W.; Zablotny, C.; Bradley, G. (1990) Methyl Bromide Inhalation Teratology Study in New Zealand White Rabbits: Lab Project Number: K-000681-033. Unpublished study prepared by The Dow Chemical Co. 362 p. (41580401) <strong>Method(s)</strong>: rabbit developmental study: pregnant New Zealand White rabbits (26 animals/dose) were exposed by whole body inhalation to 0, 20, 40 or 80 ppm MeBr vapor for 6 hr./day on Days 6-16 of gestation. Mating was conducted using artificial insemination. <strong>Critical effect</strong>: developmental toxicity – agenesis (absence) of the gall bladder in the fetus and increased incidence of fused sternebrae </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL = 40 ppm (14 mg/kg-day) </p><p><strong>Uncertainty Factors</strong>: UF&nbsp;= 100&nbsp;(10 each for intraspecies variability and interspecies extrapolation); FQPA SF = 1X </p><p><strong>2) acute&nbsp;RfD for general population including infants and children = 0.9 mg/kg-day: </strong></p><p><strong>Critical Study (ies)</strong>: Driscoll, C.; Hurley, J. (1993) Methyl Bromide: Single Exposure Vapor Inhalation Neurotoxicity Study in Rats: Lab Project Number: 92N1197. Unpublished study prepared by Union Carbide, 558 p. May 27, 1993. (42793601), <strong>Method(s)</strong>: acute rat neurotoxicity study: CD rats (15 rats/sex/dose) were exposed by whole body inhalation to 0, 30, 100 or 350 ppm MeBr vapor for 6 hours (equivalent to males: 0, 27, 90 or 314 mg/kg/day and females: 0, 30, 101, or 354 mg/kg/day). <strong>Critical effect</strong>: decreased activity, increase in number of animals with drooping/half-closed eyelids and alertness, decreased rears, decreased motor activity, increased piloerection and decreased body temperature </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL = 100 ppm (90 mg/kg-day) </p><p><strong>Uncertainty Factors</strong>: UF&nbsp;= 100&nbsp;(10 each for intraspecies variability and interspecies extrapolation); FQPA SF = 1X </p><p>4</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p></p><p><strong>IRIS: </strong>Per IRIS (7/1/1991), RfD = 1.4E-3 mg/kg-day <strong>Critical Study</strong>: Danse, L.H.J.C., F.L. van Velsen and C.A. van der Heijden. 1984. Methylbromide: Carcinogenic effects in the rat forestomach. Toxicol. Appl. Pharmacol. 72: 262-271). <strong>Method(s)</strong>: Wistar rats (10/sex/dose) were exposed to 0, 0.4, 2, 10, or 50 mg/kg by gavage for 5 days/week for 13 weeks <strong>Critical effect</strong>: epithelial&nbsp;hyperplasia in the forestomach </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL = 2.0 mg/kg;&nbsp;schedule-adjusted </p><p>NOAEL = 1.4 mg/kg/day <strong>Uncertainty Factors</strong>: UF&nbsp;= 1,000&nbsp;(10 each for intraspecies variability, interspecies extrapolation and use of a subchronic study) <strong>Source and date: </strong>IRIS, Last revision date - 7/1/1991. An IRIS screening-level review in 2001 identified one or more significant new studies. </p><p><strong>PPRTV: </strong>Per PPRTV (6/5/2007), subchronic p-RfD = 5.0E-3 mg/kg-day <strong>Critical Study</strong>: Danse, L.H.J.C., F.L. van Velsen and C.A. van der Heijden. 1984. Methylbromide: Carcinogenic effects in the rat forestomach. Toxicol. Appl. Pharmacol. 72: 262-271). <strong>Method(s)</strong>: Wistar rats (10/sex/dose) were exposed to 0, 0.4, 2, 10, or 50 mg/kg by gavage for 5 days/week for 13 weeks <strong>Critical effect</strong>: forestomach&nbsp;hyperplasia in rats </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL = 2 mg/kg; NOAEL(ADJ) = 1.4 </p><p>mg/kg-day <strong>Uncertainty Factors</strong>: UF&nbsp;= 300&nbsp;(10 each for intraspecies variability and interspecies extrapolation, and 3 for database deficiencies) </p><p><strong>Source and date: </strong>PPRTV, 6/5/2007 </p><p><strong>MRL: </strong>Per ATSDR (9/1992), no chronic oral MRL at this time.&nbsp;An oral intermediate MRL = 0.003 mg/kg-day is available: From 4/2015 MRL list. <strong>Critical Study (ies)</strong>: Danse, L.H.J.C., F.L. van Velsen and C.A. van der Heijden. 1984. Methylbromide: Carcinogenic effects in the rat forestomach. Toxicol. Appl. </p><p>5</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p></p><p>Pharmacol. 72: 262-271). <strong>Method(s)</strong>: Bromomethane was administered to Wistar rats (10/sex/dose) by gavage 5 days/week for 13 weeks at 0, 0.4, 2, 10, or 50 mg/kg. </p><p><strong>Critical effect</strong>: hyperplasia&nbsp;and ulcers <strong>End point or Point of Departure (POD): </strong>adjusted NOAEL = 0.4 mg/kg-day </p><p><strong>Uncertainty Factors</strong>: UF&nbsp;= 100&nbsp;(10 each for intraspecies variability and interspecies extrapolation) </p><p><strong>Tier 3 Source: </strong></p><p><strong>MDEQ: </strong>Per DEQ-CCD/RRD (5/26/1988), RfD = 1.4E-3 mg/kg-day.&nbsp;See Part 201 RfD details. </p><p><strong>Oral Cancer Slope Factor (CSF) </strong></p><p></p><ul style="display: flex;"><li style="flex:1">-- </li><li style="flex:1">NA </li><li style="flex:1">MDEQ, 2015 </li></ul><p></p><p><strong>(mg/kg-day)</strong><sup style="top: -0.42em;"><strong>-1</strong></sup><strong>) </strong></p><p><strong>Tier 1 and 2 Sources</strong>: </p><p><strong>IRIS: </strong>Per IRIS (1989), bromomethane is classified as D (not classifiable as to human carcinogenicity) based on inadequate human and animal data: a single mortality study from which direct exposure associations could not be deduced and studies in several animal species with too few animals, too brief exposure or observation time for adequate power. <br>Complete </p><p><strong>EPA-OPP: </strong>Per OPP (2013), methyl bromide is classified as “Not Likely to be </p><p>Carcinogenic to Humans" based on a weight of evidence evaluation of the toxicity database including no indications of carcinogenesis observed in the chronic rodent bioassays. </p><p><strong>CSF details </strong></p><p>NA <br><strong>PPRTV: </strong>Per PPRTV (6/05/07), there is inadequate information to assess the carcinogenic potential of bromomethane in humans. <strong>MRL: </strong>NA; MRLs are for non-cancer effects only. </p><p><strong>Tier 3 Source: </strong></p><p><strong>MDEQ: </strong>Per DEQ-CCD, no value at this time. </p><p><strong>Reference Concentration (RfC) or Initial </strong></p><p></p><ul style="display: flex;"><li style="flex:1">5.0E+0 </li><li style="flex:1">1.0E+1 </li><li style="flex:1">PPRTV, 2007 </li></ul><p></p><p>6</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p><strong>Threshold Screening Level (ITSL) (µg/m³) </strong></p><p><strong>Tier 2 Source: PPRTV: </strong></p><p><strong>Basis: </strong>PPRTV (6/5/2007) is the more current than IRIS.&nbsp;MDEQ applied an additional UF of 10 to account for sub chronic to chronic to derive the chronic RfC = 1.0E-2 mg/m<sup style="top: -0.42em;">3</sup>. <br>Complete <br><strong>ATSDR </strong>subchronic p-RfC = 1.0E-1 mg/m<sup style="top: -0.42em;">3</sup>. <strong>Critical Study</strong>: NTP&nbsp;(National Toxicology Program). 1992. Toxicology and carcinogenesis studies of methyl bromide (CAS No. 74-83-9) in B6C3F1 mice (inhalation studies). NTP TR 385, NIH Publication No. 92-2840. <strong>Method(s)</strong>: A 13-week subchronic inhalation range-finding study was conducted in F344 rats (18/sex/group) exposed to target concentrations of 0, 30, 60 or 120 ppm (0, 116, 233 or 466 mg/m3) of bromomethane 6 hours/day, 5 days/week. <br>Based on EPA's RfC of 5 ug/m3, from Reuzel et al 1987 &amp; 1991 - rat&nbsp;Additional groups of eight rats of each sex were exposed for eurobehavioral 29 month inhalation LOAEL of 3 ppm. studies. <strong>Critical effect</strong>: degeneration&nbsp;of the olfactory epithelium of the nasal cavity </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL =&nbsp;233 mg/m<sup style="top: -0.42em;">3</sup>; NOAEL<sub style="top: 0.13em;">HEC </sub>= 4.0 </p><p>mg/m<sup style="top: -0.42em;">3 </sup></p><p><strong>RfC/ITSL details </strong></p><p>Olfactory epithelium lesions&nbsp;<strong>Uncertainty Factors</strong>: UF&nbsp;= 30 (10 each for intraspecies variability and 3 for were observed. CCD/AQD date: 12/10/1991 interspecies extrapolation) </p><p><strong>Source and date:&nbsp;</strong>PPRTV, 6/5/2007 <strong>Tier 1 and 2 Sources: </strong></p><p><strong>IRIS: </strong>IRIS (10/1/1992)&nbsp;RfC = 5.0E-3 mg/m<sup style="top: -0.42em;">3</sup>: </p><p><strong>Critical Study(ies)</strong>: </p><p>1) Reuzel, P.G.J., C.F. Kuper, H.C. Dreef-van der Meulen and V.M.H. Hollanders. 1987. Chronic (29-month) inhalation toxicity and carcinogenicity study of methyl bromide in rats. Report No. V86.469/221044. Netherlands Organization for Applied Scientific Research, Division for Nutrition and Food Research, TNO. EPA/OTS Document No. 86-8700001202. 2) Reuzel, P.G.J., H.C. Dreef-van der Meulen, V.M.H. Hollanders, C.F. Kuper, V.J. </p><p>7</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p></p><p>Feron and C.A. van der Heijden. 1991. Chronic inhalation toxicity and carcinogenicity study of methyl bromide in Wistar rats. Fd. Chem. Toxic. 29(1): 31- 39. <strong>Method(s)</strong>: 50 male and 60 female Wistar rats were exposed to 0, 3, 30, or 90 ppm (0, 11.7, 117, or 350 mg/cu.m, respectively) bromomethane for 6 hours/day, 5 days/week (duration- adjusted concentrations are 0, 2.08, 20.9, or 62.5 mg/m3, respectively) for up to 29 months. Three satellite groups of 10/sex/group were sacrificed at 14, 53, and 105 weeks of exposure. <strong>Critical effect</strong>: Degenerative&nbsp;and proliferative lesions of the olfactory epithelium of the nasal cavity </p><p><strong>End point or Point of Departure (POD): </strong>LOAEL =&nbsp;3 ppm (11.7 mg/m<sup style="top: -0.42em;">3</sup>); LOAEL<sub style="top: 0.13em;">HEC </sub></p><p>0.48 mg/m<sup style="top: -0.42em;">3</sup>) <br>=<br><strong>Uncertainty Factors</strong>: UF&nbsp;= 100 (10 each for intraspecies variability, a factor of 3 for the use of a LOAEL for a mild effects&nbsp;and 3 for interspecies extrapolation) <strong>Source and date:&nbsp;</strong>IRIS, Last revision date - 10/1/1992.&nbsp;An IRIS screening-level review conducted in 2001 identified one or more significant new studies. </p><p><strong>MRL: </strong>Per ATSDR (9/1992), chronic inhalation MRL = 0.005 ppm (2.0 E-2 mg/m<sup style="top: -0.4217em;">3</sup>) based on neurotoxic effects. From 4/2015 MRL list. <strong>Critical Study</strong>: Anger, W.K., L. Moody, J. Burg et al. 1986. Neurobehavioral evaluation of soil and structural fumigators using methyl bromide and sulfuryl fluoride. Neurotoxicology. 7(3): 137-156. <strong>Method(s)</strong>: epidemiological study of workers who had an increased prevalence of muscle ache, fatigue, and ataxia following 8-yearchronic exposure to average levels of 2.3 ppm. <strong>Critical effect</strong>: increased&nbsp;prevalence of muscle ache, fatigue, and ataxia </p><p><strong>End point or Point of Departure (POD): </strong>LOAEL =&nbsp;2.3 ppm </p><p><strong>Uncertainty Factors</strong>: UF&nbsp;= 100 (10 each for intraspecies variability and use of a LOAEL) </p><p>Per ATSDR (9/1992) an intermediate-duration inhalation MRL = 0.05 ppm is also derived. From 4/2015 MRL list: </p><p>8</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p></p><p><strong>Critical Study</strong>: Honma T, A. Sudo, M. Miyagawa et al. 1982. Significant changes in monoamines in rat brain induced by exposure to methyl bromide. Neurobehav. Toxicol. Teratol. 4: 521-524. </p><p><strong>Method(s)</strong>: 3-week study in rats </p><p><strong>Critical effect</strong>: decreased&nbsp;brain neurotransmitters </p><p><strong>End point or Point of Departure (POD): </strong>NOAEL =&nbsp;5 ppm </p><p><strong>Uncertainty Factors</strong>: UF&nbsp;= 100 (10 each for intraspecies variability and use of a LOAEL) </p><p><strong>Tier 3 Source: </strong></p><p><strong>MDEQ: </strong>Per DEQ-CCD/AQD (12/10/1991), ITSL = 5.0 ug/m3.&nbsp;See Part 201 RfC details. </p><p><strong>Inhalation Unit Risk Factor </strong></p><p></p><ul style="display: flex;"><li style="flex:1">-- </li><li style="flex:1">NA </li><li style="flex:1">MDEQ, 2015 </li></ul><p></p><p><strong>(IURF) ((µg/m</strong><sup style="top: -0.42em;"><strong>3</strong></sup><strong>)</strong><sup style="top: -0.42em;"><strong>-1</strong></sup><strong>) </strong></p><p>Per IRIS (1989), bromomethane is classified as D (not classifiable as to human carcinogenicity) based on inadequate human and animal data: a single mortality study from which direct exposure associations could not be deduced and studies in several animal species with too few animals, too brief exposure or observation time for adequate power. <br>Complete </p><p>Per OPP (2013), methyl bromide is classified as “Not Likely to be Carcinogenic to </p><p>Humans" based on a weight of evidence evaluation of the toxicity database including no indications of carcinogenesis observed in the chronic rodent bioassays. </p><p><strong>IURF details </strong></p><p>NA </p><p><strong>Tier 1 and 2 Sources</strong>: <strong>IRIS: </strong>No value available. <strong>EPA-OPP: </strong>No value available. </p><p><strong>PPRTV: </strong>Per PPRTV (6/05/07), there is inadequate information to assess the carcinogenic potential of bromomethane in humans. <strong>MRL: </strong>NA; MRLs are for non-cancer effects only. </p><p><strong>Tier 3 Source: </strong></p><p>9</p><ul style="display: flex;"><li style="flex:1">CHEMICAL UPDATE WORKSHEET </li><li style="flex:1">Bromomethane (74-83-9) </li></ul><p></p><p><strong>Source/Reference/ Comments/Notes </strong></p><ul style="display: flex;"><li style="flex:1"><strong>Part 201 Value </strong></li><li style="flex:1"><strong>Updated Value </strong></li></ul><p></p><ul style="display: flex;"><li style="flex:1"><strong>Date </strong></li><li style="flex:1"><strong>/Issues </strong></li></ul><p></p><p><strong>MDEQ: </strong>Per DEQ-CCD/AQD, no value at this time. </p><p><strong>Mutagenic Mode of Action (MMOA)? (Y/N) </strong></p><p>-- -- </p><ul style="display: flex;"><li style="flex:1">NO </li><li style="flex:1">USEPA, 2015 </li></ul><p>NA </p><p><strong>MMOA Details </strong></p><p>Not listed as a carcinogen with mutagenic MOA in the USEPA OSWER List. <br>No, the RfD or RfC/ITSL is not based on a reproductive- </p>

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