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**EPA REGISTRATION DIVISION COMPANY NOTICE OF FILING FOR PESTICIDE PETITIONS PUBLISHED IN THE FEDERAL REGISTER** 

**EPA Registration**  **Division contact: PV Shah, 703**  **- 308** **- 1846** 
**Jeneil Biosurfactant Company [**  **IN -**  **10852 ]**  EPA has received a pesticide petition **( [**  **IN -**  **10852 ]**  **)** from Technology Sciences Group Inc. (1150 18 th Street, Suite 1000 Washington, DC 20036) on behalf of Jeneil Biosurfactant Company, 400 N. Dekora Woods Blvd. Saukville, WI 53080 proposing, pursuant to section 408(d) of the Federal Food, Drug, and Cosmetic Act (FFDCA), 21 U.S.C. 346a(d), to amend 40 CFR part 180. **( Options (pick one)**  2. to establish an exemption from the requirement of a tolerance for Isobutryic acid, CAS #79
- 31
- 2, when used as an inert solvent applied to growing crops or harvested crops under 40 CFR 180.910 in pesticide formulations
. EPA has determined that the petition contains data or information regarding the elements set forth in section 408 (d)(2) of FDDCA; however, EPA has not fully evaluated th e sufficiency of the submitted d a ta at this time or whether the data supports granting of the petition. Additional data may be needed before EPA rules on the petition.
A. Residue Chemistry **NA remove** 1. Plant metabolism. 2. Analytical method. **NA remove** 3. Magnitude of residues. **NA remove** B. Toxicological Profile The toxic effect of concern for isobutyric acid, as with many acids, is corrosivity at the site of contact, including skin and eyes. Isobutyric acid is an endogenous2

chemical in humans, being an intermediate in the metabolism of several amino acids
. It is also a natural component of many foods; therefore, adverse effects are not likely when residues of isobutyric acid from a pesticide are ingested. To assess the toxicity of isobutyric acid, a num ber of peer
- reviewed data sources were used, including the Joint FAO/WHO Expert Committee on Food Additives’ (JECFA’s) review of methyl

substituted saturated aliphatic branched
- chain primary alcohols, aldehydes, and acids; the European Chemicals Agency (EC HA) dataset/dossier for isobutyric acid; the European Chemicals Bureau (ECB) IUCLID dataset on isobutyric acid; and the OECD’s HPV Screening Information Dataset report on isobutyric acid and on n
- Butyric Acid/n

- Butyric Anhydride Category. In addition, dat a on isobutanol were used to evaluate the subchronic toxicity of isobutyric acid, as these two are related structurally and metabolically in mammals. Isobutyric acid is a metabolic product of isobutanol
. Isobutanol is metabolized by alcohol dehydrogenase t o form isobutyric acid via conversion to isobutyraldehyde. The OECD (2003) and European Chemicals Agency (ECHA) also used this approach to assess isobutyric acid’s toxicity. 1. Acute toxicity. In an OECD test guideline (TG) 401 study, male and female WISW rats (5/sex/dose) received isobutyric acid (>99% pure) by gavage at doses of 1990, 2510, 2835, or 3160 mg/kg bw, and were observed for 14 days
. Observations included slight to severe sedation a nd ataxia, lateral and prone position, labored breathing, and staggering with the first 30 minutes. After that time, animals exhibited hypothermia, ruffled fur, trembling, bloody noses and snouts, and blood in the urine. Signs persisted in some animals unt il the end of the 14
- day observation period. There was clear body weight reduction even at the lowest dose of 1990 mg/kg bw. Mortality was seen at all 4 doses (3/10, 8/10, 9/10, 8/10). The LD 50 was determined to be 2230 mg/kg bw. Another OECD TG 401

- equivalent study derived a similar oral LD50 value. Gassner rats were gavaged with 190, 1516, 2370, 2650, 3030 or 6060 mg/kg bw and observed for 7 days. Clinical signs of toxicity included abdominal position, apathy, dyspnea, cyanosis, acute dilatation, and proventiourlus septum; body weights were not tracked. Mortality was 100% at the two high doses, and 80%, 20%, 0% and 0%, respectively, in the remaining doses. The oral LD 50 was 2510 mg/kg bw
. An older acute oral toxicity study of male Carworth
-Wistar rats use d gavage doses of 161
-436 mg/kg bw and derived an LD 50 of 266 mg/kg bw (ECHA 2013). JECFA references a secondary source of an oral rat study in which the LD 50 was determined to be 280 mg/kg. No further data were provided. In rabbits, the oral LD 50 for iso butyric acid was 8000 mg/kg bw
. Overall, acute oral LD 50 values range from 266
- 2230 mg/L in rats. ECHA rated the study determining the LD 50 of 2230 mg/kg bw as “reliable without restriction,” while the other two rat studies were determined “reliable with restrictions.” The two lower LD 50 values may or may not reference the same original study. It is unclear why these values are so disparate from the other two values. Most of the details on the test material (e.g., purity, stability, storage conditions), the effects (e.g., necropsy and any other examinations), etc., were not available for review in the two studies with lower LD 50 values. Based on the ECHA rating of the study with the higher LD 50, oral Toxicity Category III is appropriate for isobutyric ac id.3

An acute dermal study was conducted in New Zealand white male rabbits (4/group) in a study equivalent to an OECD Guideline study
. Administration of the test compound at concentrations of 351
- 636 mg/kg and occlusive wrapping for 24 hours was followed by a 14
- day observation period. The dermal LD 50 was 475 mg/kg bw, corresponding to acute dermal toxicity category II. No mortality was noted in an OECD guideline study, when 6 male and 6 female rats inhaled air saturated with isobutyric acid (about 9.59 mg/L) for eight hours . This corresponds to an acute inhalation toxicity category of IV.

2. Genotoxicty. Results for multiple Ames assays on isobutyric acid were negative for mutagenicity under all conditions tested. The Salmonella typhimurium strains that have been tested are TA98, TA100, TA1535, TA1537, and TA1538, and concentrations tested are as high as 5000 μg/plate in the absence and presence of metabolic activation
. Negative results were also obtained in the rec assay with Bacillus subtilis H17 and M45 at concentrations of 19 g/plate. Isobutyric acid at concentrations up to 1000 g/mL did not induce unscheduled DNA synthesis in rat hepatocytes
. A mouse lymphoma assay produced weakly positive results in L5178Y TK+/

- cells at a concentratio n of 500 g/mL without metabolic activation, and negative results at 600 g/mL in the presence of activation
. JECFA concluded that isobutyric acid, along with other aliphatic acyclic branched
- chain primary alcohols, aldehydes, and carboxylic acids are not mu tagenic or clastogenic in vitro or in vivo. JECFA did not attribute the one weakly positive effect in the mouse lymphoma assay to direct DNA damage. 3. Reproductive and developmental toxicity. In two prenatal developmental toxicity inhalation studies, ma ted female Wistar rats and Himalayan rabbits were exposed to isobutanol (99.8%) at vapor concentrations of 0, 151, 758 or 3030 ppm (0, 500, 2,500 or 10,000 mg/m 3 ) for six hours/day. The rats were dosed on post

-coitum days 6
- 15. No mortality or significant differences in clinical signs, body weight development, or gross pathology between controls and treated groups were observed. No effects on development were noted. The maternal and developmental rat NOAELs were 3030 ppm. Rabbits (15/dose) were dosed on p ostinsemination days 7
- 19. High
- dose rabbit dams had a slightly lower body weight gain, particularly during the first phase of exposure. The maternal NOAEL for rabbits was 758 ppm. Fetuses exhibited no signs of developmental changes in response to isob utanol. Therefore, the rabbit developmental NOAEL was 3030 ppm, the highest dose. In a 2
-generation reproductive inhalation study isobutanol (99.9%) was administered to 30 Crl:CD(SD)IGS BR rats/sex/dose by whole body exposure at 0, 500, 1000 and 2500 ppm ( 0, 1476, 2952, and 7380 mg/m3) for 6 hours per day 7 days per week. Exposure began at the commencement of the study for the F0 generation, and on postnatal day 28 for the F1 generation. It ended after weaning of the pups (F0 generation postnatal day 28, F1 generation postnatal day 21). For dams, exposure was discontinued after day 20 of gestation through lactation day 5. No exposure
- related effects were observed on F0 and F1 parental survival or on4

F0 and F1 reproductive performance, body weights, food cons umption and food efficiency in males or females. There were no significant spermatogenic or macroscopic findings, changes in primordial follicle or corpora lutea counts, changes in mean organ weights or histopathologic lesions in the F0 or F1 rats at any dose. Pup endpoints were not significant for either F1 or F2 generations, including survival, general physical condition, and mean body weights. There were no macroscopic findings, changes in mean organ weights, or maturation of F1 pups. The NOAEL of isobu tanol for parental systemic, reproductive and neonatal toxicity is 2500 ppm (7380 mg/m3, the maximum applied dose) in males and females of the F0, F1 and F2 generations (ECHA 2014b). The study was rated “reliable without restriction” by the European Chemic als Agency (ECHA). 4. Subchronic toxicity. There were no studies identified on the subchronic, chronic, developmental, or reproductive toxicity of isobutyric acid. A structural assessment of toxicity was carried out using the method of Cramer. Repeat
- dose studies of isobutanol were used to bridge the subchronic data gap for isobutyric acid. Isobutanol is related structurally and metabolically to isobutyric acid. In animals, isobutanol is metabolized by alcohol dehydrogenase to isobutyric acid via conversion to isobutyraldehyde. The Joint FAO/WHO Expert Committee on Food Additives (JECFA) reviewed isobutyric acid as a member of the methyl
- substituted saturated aliphatic branched
- chain primary alcohols, aldehydes, and acids group, and determined that isobutyric acid and the other 21 compounds in this group belong i n Cramer Structural Class I. The Cramer scheme is a peer
- reviewed approach to classifying chemicals with respect to non
- cancer risk from oral exposure. It primarily uses information on the toxicity of a chemical’s substructures and the predi cted pathway of mammalian metabolism. Other factors in the classification include whether the compound occurs naturally in the body and in food. Isobutyric acid is categorized as a Class I substance, which is the lowest concern, based on the absence of su bstructures associated with toxicity, an efficient metabolic pathway, and the fact that it is an endogenous chemical in humans and in food. In a 9 0
- day oral rodent toxicity study on isobutanol, which served as the scientific basis for US EPA’s oral Reference Dose (RfD) for that compound (U.S. EPA 1991) , the test compound was administered to 30 Crj: CD(SD) rats/sex/dose by gavage at dose levels of 0, 100, 316, or 1000 mg/kg bw/day. Treatment related effects were seen only at 1000 mg/kg bw/day and included hypoactivity, which was significant during week one and decreased markedly after week 4, and lower body weight gain (18% below that of control rats) in males during week one. Food consumption averages were below those of the controls for both males and fem ales during weeks 1 and 2. Clinical signs and effects on body weight and food consumption were all transient and were considered as adaptive and therefore as not adverse. In addition, serum potassium levels were 11
- 15% lower in both sexes compared to controls on day 29, but group mean serum potassium concentrations were similar for treated and control groups at the final clinical pathologic evaluation. No other significant difference between dosed groups and controls were found for ophthalmoscopic examinati on, hematology, urinalysis, organ weights,5

gross pathology and histopathology. The NOEL was determined to be 316 mg/kg bw/day and the NOAEL was 1000 mg/kg/day. U.S. EPA derived an oral RfD of 0.3 mg/kg/day for isobutanol by applying uncertainty factors totaling 1000 to this NOEL
. Wistar rats (10/sex/group) were exposed to isobutanol in drinking water at concentrations of 0, 1000, 4000, or 16,000 ppm, equivalent to approximately 0, 80, 340, or 1450 mg/kg bw/day isobutanol actually ingested. The 90
- day study was carried out under OECD Test Guideline 408 and included full hematology, urinalysis, and ophthalmological endpoints as well as post
sacrifice histological exam. Body weight, food and water consumption, and clinical signs of toxicity were monitored throughout the study. There were no significant dose
- dependent signs of toxicity in any of these parameters. Study authors concluded that the NOAEL for isobutanol was the highest dose, 1450 mg/kg/day. In a 90
- day inhalation study, 99% pure isobutanol was adm inistered by dynamic whole
- body exposure to 10
- 20 Sprague
- Dawley rats/sex/dose at 0, 250, 1000, or 2500 ppm for 6 hours per day, 5 days/week. During exposure time only, there was a slight decreased response to external stimuli that disappeared immediately after exposure. ECHA considered it an effect of the narcotic properties of isobutanol rather than an adverse effect. In high dose females, total erythrocyte count, hemoglobin, and hematocrit were slightly elevated compared to controls (p ≤ 0.05). ECHA co nsidered this to be not biologically significant. No differences were found in body weight, food consumption, ophthalmoscopic examination, clinical observation, clinical chemistry, neurobehavioral observations, organ weights, gross pathology, and histopath ology. The NOAEL for repeat
- dose effects including neurotoxicity was 2500 ppm.

. 5. Chronic toxicity. No chronic studies were identified for isob utyric acid or its metabolites **.** 6. Animal metabolism. Branched
- chain acyclic aliphatic acids in general are rapidly absorbed following an oral dose
. The metabolism of isobutyric acid has been well studied in rodent models. The β
- carbon undergoes oxidation to yield propionic acid, which is eventually fully metabolized via the fatty acid pathway or Kreb’s cycle. Increased methylmalonic acid and succinic acid have also been detected in urine following an oral dose of isobutyric acid. In male Charles River CD rats, 75.4, 83.3, and 66.7% of gavage doses of 4, 40, or 400 mg/kg bw radio
- labeled isobutyric acid, respect ively, were exhaled as CO 2 after 4
- hours. After 48
- hours, 85
-90% of the doses had been exhaled. Less than 5% of the dose was recovered in the urine and feces . There was no isobutyric acid in milk or peripheral blood of dairy cattle that had eaten 170 mg/kg/day for 10 days
. I sobutyric acid was detected in the serum and plasma of fasted human subjects (n=6) at mean concentrations of 30.7 μg/dL and 143 μg/dL, respectively. It has also been detected in human feces.
.6
7. Metabolite toxicology
. NA Remove 8. Endocrine disruption
. Toxicity data related to endocrine disruption were not identified in the isobutyric acid database. As the scientific knowledge develops, screening of additional compounds may be added to the Endocrine Disruptor Screening Program (EDSP ). When additional screening and/or testing is conducted, isobutyric acid may be the focus of screening and/or testing to better characterize effects related to endocrine disruption. C. Aggregate Exposure 1. Dietary exposure. The estimated dietary exposure to isobutyric acid was determined using methods to estimate chronic dietary exposure for a generic inert ingredient. This assessment considers drinking water and crop
- specific residues from pre
- harvest applications of agricultural insecticides, herbicide s and fungicides, assuming the highest established tolerance level residue for each commodity. The assessment assumes that the inert ingredient is used on all crops . The inert ingredient is assumed to be present in all commodities treated with 57 of the most significant active ingredients at the maximum tolerance level as identified by the U.S. EPA for the default assessment. Chronic dietary exposure estimates were derived for the general US population and sub
-groups of the population using the Dietary E xposure Evaluation Model, DEEMTM. Assuming all crops are treated with formulated products containing 10% isobutyric acid by weight, t he estimated chronic exposure for the total US population is 0. 038 mg/kg/day, 10.1 % of the chronic Population Adjusted Dose (cPAD). Children age 1 to 2 years old have the highest estimated exposure at 0. 141 mg/kg/day, or 37.6% of the cPAD **.** i. Food. Dietary exposures of concern are not anticipated for isobutyric acid due to its lack of persistence in the environment and low g eneral toxicity. A significant source of dietary isobutyric acid comes from natural food sources and its use as a food additive. The annual individual consumption of isobutyric acid from food flavoring substances was estimated to be 140 μg/person/day in the U.S. , equivalent to 2.0 μg/kg bw/day
. ii. Drinking water. I sobutyric acid exposure via drinking water from use as an inert ingredient is not expected to be significant. Isobutyric acid is readily biodegradable . Exposure via drinking water was estimated in the DEEM dietary exposure assessment assuming a concentration of 100 ppb **.** 2. Non
-dietary exposure
. Residential exposures of concern are not anticipated for i sobutyric acid due to its ready ability to biodegrad e in the environment, low projected use
- level in pesticides, and low general toxicity **.** D. Cumulative Effects Section 408(b)(2)(D) (9v) of the FFDCA requires that, when considering whether to establish, modify, or revoke a tolerance, the Agency consider “ available information” concerning7

the cumulative effects of a particular pesticide’s residues and “other substances that have a common mechanism of toxicity.” To our knowledge there are no available data or other reliable information that suggests any tox ic effects produced by i sobutyric acid would be cumulative with those of any other chemical compounds. EPA has not made a common mechanism of toxicity finding as to i sobutyric acid and other compounds. Isobutyric acid does not produce toxic metabolites in common with other substances of potential concern. For the purpose of the tolerance exemption proposed, it is assumed that is obutyric acid does not share a common mechanism of toxicity with other substances
. E. Safety Determination 1. U.S. population. Taking into consideration all available information on i sobutyric acid , there is a reasonable certainty that no harm to any population subgroup will result from dietary and other nonoccupational exposures to i sobutyric acid when used as an inert ingredient in an inert mixture intended for use in pesticide formulations. Adjusting for relative molecular weight, EPA’s oral RfD of 0.3 mg/kg/day for isobutanol was used to derive an RfD for iso butyric acid of 0.376 mg/kg/day, which added uncertainty factors tota ling 1000 for interspecies extrapolation, intraspecies variability, and for extrapolating subchronic exposure to chronic exposure. The chronic Population Adjusted Dose (cPAD) was determined to be the same as the RfD because no effects of isobutanol on deve lopment or reproduction were observed, suggesting that isobutyric acid too would not increase susceptibility of sensitive populations. For the total US population, the estimated chronic dietary exposure from food and drinking water for isobutyric acid , ca lculated as 1 0% of all agricultural formulations, is 10.1 % of the cPAD, well below any level of potential concern. 2. Infants and children
. An evaluation of susceptibility and uncertainty issues associated with isobutyric acid has been performed and t here is a reasonable certainty that no harm to infants and children will result from the use of isobutyric acid as an inert ingredient in pesticide products. The structurally similar and metabolically related compound isobutyl alcohol was not a developmental toxin to rats or rabbits following inhalation. For this reason, a safety factor analysis has not been implemented to assess risk and the additional tenfold safety factor for the protection of infants and children is also unnecessary. The estimated chronic dietary exposure from food and drinking water was highest ( 37.6 % of cPAD) for children aged 1 to 2 years old. This estimated exposure to isobutyric acid is well below any level of potential concern. F. International Tolerances NA Remove8