United States Office of Pestlcidei end Toxic Subrtanen Environmental Protection Office of Potlddc Programs (TS-766C) Agency Washington, DC 20460 v°/EPA Pesticide Fact Sheet Name of Chemical: NITOAPYRIN Reason for Issuance: Date Issued: June 28,1985 Fact Sheet Number: 54 1. Description of chemical Generic Name: 2-Ghloro-6-(trlchloranethyl)pyrldlne Cannon name: Nltrapyrin Trade name: N-Serve EPA Shaughnessy code: 069203 Chemical Abstracts Service (CAS) number: 1929-82-4 Year of Initial registration: 1974 Pesticide type: Bacterlostat Chemical family: Pyrldlnes U.S. and foreign producers: Dow Chemical Company 2. Use patterns and formulations Application sites: Nltrapyrln Is registered for use as a nitrogen stabilizer In com, cotton, rice, sorghum, strawberries, and wheat Types of formulations: Etaulslflable concentrate and soluble concentrate Types and methods of application: Broadcast or band with soil Injection or Incorporation during or Immediately after application Application rates: 0.25 Ib al/A to 1.0 Ib al/A Usual carrier: Water and/or fertilizer 3. Science findings Summary science statement: The existing data base Is Insufficient to fully assess the toxicology, residue chemistry, environmental fate or ecological effects of nltrapyrln. Previous toxlclty testing had been conducted using the major metabolite 6-chloroplcollnlc acid and In most areas, previous testing was found, upon revaluation, to be supplementary or invalid according to current testing guidelines. Chemical characteristics: Nitrapyrln is a white crystalline solid with a mildly sweet odor. The melting point Is 62-63°C. The vapor pressure of nltrapyrln Is 2.8 x 10-3 ran Hg at 23 C and its solubility Is 0.004 grams (g)/100 g in water. Toxicologies! characteristics: Acute Toxicology: Nltrapyrin has moderate oral toxiclty (Toxicity Category HI) and is a moderate dermal Irritant (Toxicity Category III). ------- Chronic !Ibxicology: Chronic feedirg/aicogenicity, teratogenicity and reproduction testing uair€ riltrapyrin AI have been identified as data gaps. Previous chronic testing .s conducted using 6—chloropicolinic acid (6-CPA), a major metabolite which was initially identified as the residue of concern. A chronic feeding/oncogenicity study in the rat using 6—CPA, aitbough considered supplementary data, indicated (upon reevaluation) si ificant canpound related microscopic char€es (biliary hyperplasia) occurred in f nA 1e rat livers at all doses tested. Nitrapyrin did not demonstrate an increase in unscheduled rat hepatocyte DNA synthesis and i s not genotoxic in ixnitageniclty tests. Gene mutation (Ames) and chra2loscfnal aberration tests are data gaps. Physiological a ix! biochemical behavioral characteristics: Mechaniem of Action: Nitrapyrin is an aninoniacal nitrogen stabilizer which inhibits the nitriflcation of amoniacal and urea nitrogen fertilizer in the soil by selectively a id temporarily, inhibiting Nitrosanonas . These bacteria convert amoniuzn nitrogen to nitrite nitrogen, which in turn is converted to nitrate nitrogen by other bacteria, e.g., Nitrobacter. Environnenta]. characterlsitics: Degradation: Preliminary data indicate that hydrolysis of nitrapyrin is rapid, the rate increasing with increasing temperature. It is not affected by pH aid degrades more rapidly in the light than in the dark. Persistence: In soil, nitrapyrin has a half life of < 3 to 35 days, depending on soil type. Bloac cumulation: Nitrapyrin accunni1 tes in the edible aid visceral tissues of bluegill sunfish with maxlmtun bioconcent ration factors of 33 x and 60 x, respec- tively. The residues depurate rapidly. Ecological Characteristics: Avian 8tudies: Acute oral (Mallard duck)>2708 xr /kg (slightly toxic). Avian dietary (Japanese quail) >820 ppm (slightly toxic) Aquatic species studies: t phnia magia 8—hour acute Is 5.8 n /l (moderately toxic). Bluegill sunfish 96—hour acute is 7.876 mg/i (moderately toxic). Rainbow trout 96—bour acute is 9.191 i Jl (moderately toxic). -2- ------- Potential prob1 na for endangered species: Based on an estimated envirorinental concentration ( C) of 0.1 p n in water (due to z,inoff), the expected hazard to aquatic organ- isms is expected to be minimal. However, use in rice, although estimated to be negligible, me y result in an C in floodwater of 0. 4 ppn. This level may impact on endangered or threatened species, such as the Fat Pocketbook Pearly Mussel, which 18 bott d ller, and as such would be exposed to nitrapyrin in the both the water and sediments • The aquatic invertebrate toxicity test data are not appropriate in assessing hazard to bivalves. Therefore, marine n llusc shell deposition testing is required. For nal consultation with the Office of Endangered Species, USFWS, will be considered after these data are received arid evaluated. Tolerance assessment8: U.S. tolerances for residues of nitrapyrin [ 2—chloro—6—(trichloranethyl) pyridine] and Its inetabolite, 6-chloroplcolinic acid in or on raw agricultural ca nodities are as follows [ Z 0 CFR h80.350]: Caiinodlties Tolerance (pm) Cattle, fat 0.05 Cattle, mbyp 0.05 Cattle, meat 0.05 Corn, fodder 1.0 Corn, forage 1.0 Corn, grain 0.1 Corn, fresh 0.1 Cottonseed 1.0 Goats, fat 0.05 Goats, inbyp 0.05 Goats, meat 0.05 Hogs, fat 0.05 Hogs, yp 0.05 Hogs, meat 0.05 Horses, fat 0.05 Horses, mbyp 0.05 Horses, meat 0.05 Poultry, fat 0.05 Poultry, mbyp 0.05 Poultry, meat 0.05 Rice, grai.n 0.2 Rice, straw 2.0 Sheep, fat 0.05 Sheep, inbyp 0.05 Sheep, meat 0.05 Sorghtin, fodder 0.5 Sorglium, forage 0.1 Sorghum, grain 0.1 strawberries 0.2 Wheat, forage 0.5 Wheat, grain 0.1 Wheat, straw 0.5 —3— ------- No mexican tolerances or Codex t’ Ls have been established for residues of nltrapyrin. A Canadian tolerance of 0.1 ppm exists for, presumably, residues of nitrapyrin per se in or on corn. esidue studies are not adequate to support existing tolerances. The plant arid animal metaboli&n of nitrapyrln are not adequately understood and analytical methodolog.y may need to be revised ,then required data are evaluated. Storage stability data and additional, more geographically representative residue data are required for most calEodities. Tolerances have been proposed for residues of nitrapyrin arid Its metabolite, 6—CPA, in or on the crop group cereal grains; lettuce; potatoes; soybeans and soybean forage and hay. The Agency has decided, however, that no new tolerances or ex np- tioris will be established until all major toxicology and residue ch iiatry data requir nenta have been satisfied. 44• S rTn .ry of Regulatory Position and Rationale Risk/benefit review: None of the risk criteria set forth in Title 140 Code of Federal Regulations S162.11 for caitnencing a special review have been met or exceeded by nitrapyrin. Growxl Water Potential: Nitrapyrin se has not been previ isly identified as a potential ground water contaminant arid in moni- toring studies conducted to date nitrapyrin residues have not been found in ground water. However, one study using the 6-CPA metabolite indicated a moderate potential for 6-CPA to leach in loam soil. Therefore, envirorinental chamistry studies are being required in the minimum times necessary to conduct the tests arid will be evaluated on an expedited basis when received. 5. Sm iar’y of major data gaps and when these are due to be filled 6 Months: Product identity and canposition Physical and Che!nIcal characteristics Avian subacute dietary and freshwater fish toxicity Acute freshwater Invertebrate toxicity 9 Months: H.ydrolys Is, photodegradat ion Acute dermal and inhalation toxicity Primary eye Irritation and dennal sensitization Gene mutation (Ames) 12 ?bnths: Preliminary analysis of’ product samples Leaching and adsorpticn/desorPtion Structural chranosr l aberration Acute toxicity to estuarine and marine organisms -14- ------- 15 Months: Teratolog i (2 species) 18 Months: Animal metabolism and residues 214 Months: Plant metabo].isrn Storage stability Analytical methods and stability of residues under storage Crop residue studies for corn, sorgjiurn, strawberries, wheat and cottonseed General metabolism 27 Months: Aerobic aquatic metaboli i Field dissiçation (soil) and di.ssipation aquatic (sediment) 39 Months: Rotational, crops (confined) Irrigated crops Reproduction (2—generation) 50 Months: Chronic feeding (2 species) Oncogenicity (2 species) Rotational crops (field) 6. Contact person at EPA Richard P. Mountfort Product Manager (23) &ivirorinental Protection Agency (TS—767C) 1401 M Street, S’vI Washington, DC 201460 (703) 557—1830 DISCLAIM : The information presented in this Ch iica.l Information Fact Sheet is for informational purposes only and m&y not be used to fulfill data requirenents for pesticide registration and reregistratial. -5- ------- |