Page 1 of 4 UNITED STATES ENVIRONMEN TAL PROTECTION AGENCY WASHINGTON, D.C. 20460

OFFICE OF

CHEMICAL SAFETY AND

POLLUTION PREVENTION

MEMORANDUM

Date: March 29, 2012

Subject: Glufosinate Ammonium. Report of th e Residues of Concern Knowledgebase Subcommittee (ROCKS).

PC Code: 128850 DP Barcode: D397644
Decision No.: 424395 Registration No.: NA
Petition No.: NA Regulatory Action: Section 3 Registration Risk Assessment Type: Single Chemical Aggregate Case No.: NA

TXR No.: NA CAS No.: 77182-82-2

MRID No.: NA 40 CFR: 180.437

From: Ideliz Negrón-Encarnaci ón, ROCKS Alternate Secretary Health Effects Division (7509P)

Through: Christine L. Olinger, ROCKS Co-Chair Edward J. Scollon, ROCKS Co-Chair Health Effects Division (7509P)

To: Glufosinate Ammonium Risk Assessment Team

Risk Assessment Branch V Health Effects Division (7509P)

The ROCKS met on January 11, 2012 to discuss the residues of concern for the herbicide glufosinate ammonium in drinking water. The residue of concern recommendation was subjected to electronic revi ew to consider a subsequent ToxSAC report (02/21/2012).

Team Members Attended: John Doherty, Chuck Peck, William Donovan, Mike Metzger, and Marietta Echeverria

ROCKS Members Attended: Christine Olinger, Edward Scollon, Ray Kent , Richard Loranger, Elizabeth Holman, William Irwin, Leung Cheng, George Kramer, Reuben Ba ris, Dennis McNeilly and Ideliz Negrón

Material Reviewed: Briefing Materials: Glufosinat e Ammonium ROCKS SubmissionPage 2 of 4 Background

The residues of concern of th e herbicide glufosinate ammonium in plants, rotational crops, livestock and drinking water were previously evaluated (Txt# 0050727, T. Bloem, 05/09/2002).

The risk assessment team solicited the ROCKS a re-evaluation of the residues of concern in drinking water. Supplemental toxicity informa tion for water degradates was provided for the ROCKS consideration. Based on input provided by the ToxSAC (02/21/2012), the recommendation from the ROCKS meeting held on January 11, 2012 was amended. The

amended decision memo was circulated electroni cally to the ROCKS comm ittee on February 28,

2012 for comments.

Committee Recommendation

Summary of Degradates to be included in the Risk Assessment

Matrix Residues included in Risk Assessment Residues included in Tolerance Expression

Drinking Water Glufosinate Ammonium 1,2 Not Applicable

1 Glufosinate ammonium is butanoic acid, 2-amino-4-(hydroxymethylphosphinyl)-monoammonium salt. Although glufosinate ammonium will be dissociated in water, for risk assessment purposes it is described as the salt in order to aggregate the residues in drinking water with those in food where the concentration is expressed in terms of the salt.

2 Since MPP is likely less toxic than the parent compound and should not be aggregated with the parent, if MPP EDWCs are not significantly greater than those for glufosin ate, the risk assessment for the parent will be protective of any toxicity associated with exposure to MPP in dr inking water and a quantitative risk assessment for MPP will not be required.

Summary of Briefing Materials Considered

Glufosinate ammonium [ammonium-DL-homoala nin-4-yl-(methyl)-phos phinate] is a nonselective foliar herbicide that acts by inhibi ting glutamine synthetase . In addition to the complete toxicity database for the parent compound, subchronic toxicity and developmental

studies are available for the environmental de gradates MPP, MPA and NAG (structures are shown in Appendix 1). MPA is at least 100 fold less potent than glufos inate ammonium based upon the lack of effects in a 90-day study in ra ts. Rabbit developmental studies are also available for GA, NAG, and MPP to aid in re lative potency comparisons. NAG and MPP were 5- to 10-fold less potent than th e parent; however, the maternal e ffects noted were different than those observed than the pare nt glufosinate ammonium.

Glufosinate ammonium is readily miscible in wa ter. Glufosinate will not volatilize significantly due to a low vapor pressure, and is moderately mobile. Glufosinate is considered stable to photolysis in water but degrades in soil due to photolysis with a half-life of 17 days. The metabolism studies showed that glufosinate degrad es in aerobic soil and aqueous environments, with soil half-lives ranging from 8.5 to 23 days, and aquatic half-lives ranging from 11 to 87 days. Glufosinate in the anaerob ic soil environment degraded w ith a measured half-life of 37 days in one study, but the chemical was persistent in the anaerobi c aquatic environment, with a measured half-life of 415 days in another study.Page 3 of 4 MPP was a major degradate in the soil photolys is study, reaching a maximum of 60.4% (Day 30). MPP was also a major degradate in all metabolism studies with the exception of the anaerobic aquatic study. In aerob ic systems, maximum MPP values ranged from 26 to 55% in soil and 17 to 80% in aquatic e nvironments. In anaer obic soil, MPP reached a maximum of 42% at the end of the study (Day 60).

MPA was a major or minor degradate in all of metabolism studies with the exception to the anerobic aquatic metabolism. In aerobic system s, maximum MPA values ranged from 3 to 28% in soil and 7 to 20% in aquatic environments. When MPA was a major degradate, it tended to form at the end of the study, supporting the supposition that it forms as a result of MPP degradation. In anaerobi c soil and soil photolysis, MP A was a minor degradate.

NAG was major degradate of photolysis in soil, reaching maximum of 17.7% (Day 4). It was a minor degradate in one of two aer obic aquatic studies and not detect ed in the other. In addition,

it was not detected in the anaer obic aquatic study, a nd aerobic and anaerob ic soil studies.

Rationale

MPA: A 90-day rat feeding study showed no effects at the highest dose tested which is about 100-fold higher than the NOAEL of the parent; therefore, MPA is c onsidered less toxic than the parent. Even though it is a major degradate in so me studies, considering its much lower toxicity than the parent, ROCKS recommends its exclusion as a residue of concern in drinking water.

NAG: Based on the rabbit developmental studies NAG can be considered slightly less toxic than the parent. It was only observed as a major de gradate during photolysis in soil; therefore, its exposure is significantly lower to that of the parent in drinking water. The ROCKS recommends

its exclusion as a residue of concern in drinking water.

MPP: The ROCKS noted that MPP may have differe nt toxicity than the pa rent and is likely to have a lower toxicity but not so low that it could be definitely excl uded from consideration. After the ROCKS meeting, the team consulted with Health Eff ects Division ToxSAC regarding the toxicity of MPP (J. Kidwell, 02/21/2012). The consensus of the ToxSAC was that glufosinate ammonium, the parent, and MPP, the de gradate, show different toxicities, such that they should not be aggregated. Moreover, the Environmental Fate and Effects Division have

indicated that the acute concentrat ions of MPP are not likely to be significantly greater than that of glufosinate in drinking water. However, gi ven the minimal fate data available for MPP that indicates MPP does not degrade in aerobic aquatic e nvironments, it is unclear if this will be true for chronic concentrations of MPP and glufosinate. Since MPP is likely less toxic than the parent compound and should not be aggregated with the parent, if MPP EDWCs are not significantly greater than those for glufosinate, the risk asse ssment for the parent wi ll be protective of any toxicity associated with exposure to MPP in drinking water. Therefore, a quantitative risk assessment for MPP in drinking water will not be required.Page 4 of 4 Appendix 1. Glufosinate Ammonium and it major degradates in water.

Common Name Chemical Name Structure

Glufosinate ammonium (parent) (HOE 039866) IUPAC name: ammonium-DL-homoalanin4-yl-(methyl)-phosphinate

CAS name: butanoic acid, (±)-2-amino-4- (hydroxymethylphosphinyl)-,

monoammonium salt P NH 2

O

OH O

CH 3 -O NH 4 +

MPP ( HOE 061517) CAS Name: 3-methylphosphinico-propionic

acid

P HO

CH 3

O OH

O

MPA ( HOE 064619) CAS Name: 2-methylphosphinico-acetic acid

P HO

CH 3

O O

OH

NAG ( HOE 085355/HOE 099730) CAS Name: 2-acetamido-4- methylphosphinico-butanoic acid

P HO

CH 3

O O

OH NH CH 3

O