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AZADIRACHTIN

CASRN: 11141-17-6
Chemical structure for AZADIRACHTIN
For more information, search the NLM HSDB database.

Human Health Effects:


Human Toxicity Excerpts:
/SIGNS AND SYMPTOMS/ Neem seed oil produced occasional diarrhea, nausea, and general discomfort when given orally as an anthelmintic. /Neem seed oil/
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**

/SIGNS AND SYMPTOMS/ ... 13, including 2 fatal, poisoning cases due to neem seed (margosa) oil, a traditional remedy in India and Malaysia, /were reported/. Five to ten milliliters of the oil given orally to children against minor ailments caused vomiting, drowsiness, tachypnea with acidotic respiration, and polymorphonuclear leukocytosis, and encephalopathy developed within hours of ingestion. Seizures, associated with coma, developed in some cases. Autopsy demonstrated pronounced fatty acid infiltration of the liver and proximal renal tubules, with mitochondrial damage, and cerebral edema, changes consistent with Reye's syndrome.
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**


Probable Routes of Human Exposure:
Occupational exposure to azadirachtin may occur through inhalation and dermal contact with this compound at workplaces where azadirachtin is produced or used. The greatest potential for dermal and inhalation exposure to azadirachtin is expected when the material is being applied to fields and crops for use in insect control. (SRC)
**PEER REVIEWED**


Emergency Medical Treatment:


Emergency Medical Treatment:
EMT Copyright Disclaimer:
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The following Overview, *** GENERAL OR UNKNOWN CHEMICAL ***, is relevant for this HSDB record chemical.

Life Support:
o   This overview assumes that basic life support measures
       have been instituted.
Clinical Effects:
0.2.1 SUMMARY OF EXPOSURE
   0.2.1.1 ACUTE EXPOSURE
     A)  A SPECIFIC REVIEW on the clinical effects and treatment
         of individuals exposed to this agent HAS NOT YET BEEN
         PREPARED. The following pertains to the GENERAL
         EVALUATION and TREATMENT of individuals exposed to
         potentially toxic chemicals.
     B)  GENERAL EVALUATION -
      1)  Exposed individuals should have a careful, thorough
          medical history and physical examination performed,
          looking for any abnormalities. Exposure to chemicals
          with a strong odor often results in such nonspecific
          symptoms as headache, dizziness, weakness, and nausea.
     C)  IRRITATION -
      1)  Many chemicals cause irritation of the eyes, skin, and
          respiratory tract. In severe cases respiratory tract
          irritation can progress to ARDS/acute lung injury,
          which may be delayed in onset for up to 24 to 72 hours
          in some cases.
      2)  Irritation or burns of the esophagus or
          gastrointestinal tract are also possible if caustic or
          irritant chemicals are ingested.
     D)  HYPERSENSITIVITY -
      1)  A number of chemical agents produce an allergic
          hypersensitivity dermatitis or asthma with
          bronchospasm and wheezing with chronic exposure.
Laboratory:
A)  A number of chemicals produce abnormalities of the
       hematopoietic system, liver, and kidneys. Monitoring
       complete blood count, urinalysis, and liver and kidney
       function tests is suggested for patients with significant
       exposure.
   B)  If respiratory tract irritation or respiratory depression
       is evident, monitor arterial blood gases, chest x-ray,
       and pulmonary function tests.
Treatment Overview:
0.4.2 ORAL EXPOSURE
    A)  GASTRIC LAVAGE
     1)  Significant esophageal or gastrointestinal tract
         irritation or burns may occur following ingestion. The
         possible benefit of early removal of some ingested
         material by cautious gastric lavage must be weighed
         against potential complications of bleeding or
         perforation.
     2)  GASTRIC LAVAGE: Consider after ingestion of a
         potentially life-threatening amount of poison if it can
         be performed soon after ingestion (generally within 1
         hour). Protect airway by placement in the head down
         left lateral decubitus position or by endotracheal
         intubation. Control any seizures first.
      a)  CONTRAINDICATIONS: Loss of airway protective reflexes
          or decreased level of consciousness in unintubated
          patients; following ingestion of corrosives;
          hydrocarbons (high aspiration potential); patients at
          risk of hemorrhage or gastrointestinal perforation;
          and trivial or non-toxic ingestion.
    B)  ACTIVATED CHARCOAL
     1)  Activated charcoal binds most toxic agents and can
         decrease their systemic absorption if administered soon
         after ingestion. In general, metals and acids are
         poorly bound and patients ingesting these materials
         will not likely benefit from activated charcoal
         administration.
      a)  Activated charcoal should not be given to patients
          ingesting strong acidic or basic caustic chemicals.
          Activated charcoal is also of unproven value in
          patients ingesting irritant chemicals, where it may
          obscure endoscopic findings when the procedure is
          justified.
     2)  ACTIVATED CHARCOAL: Administer charcoal as a slurry
         (240 mL water/30 g charcoal). Usual dose: 25 to 100 g
         in adults/adolescents, 25 to 50 g in children (1 to 12
         years), and 1 g/kg in infants less than 1 year old.
    C)  DILUTION -
     1)  Immediate dilution with milk or water may be of benefit
         in caustic or irritant chemical ingestions.
     2)  DILUTION: If no respiratory compromise is present,
         administer milk or water as soon as possible after
         ingestion. Dilution may only be helpful if performed in
         the first seconds to minutes after ingestion. The ideal
         amount is unknown; no more than 8 ounces (240 mL) in
         adults and 4 ounces (120 mL) in children is recommended
         to minimize the risk of vomiting.
    D)  IRRITATION -
     1)  Observe patients with ingestion carefully for the
         possible development of esophageal or gastrointestinal
         tract irritation or burns. If signs or symptoms of
         esophageal irritation or burns are present, consider
         endoscopy to determine the extent of injury.
    E)  OBSERVATION CRITERIA -
     1)  Carefully observe patients with ingestion exposure for
         the development of any systemic signs or symptoms and
         administer symptomatic treatment as necessary.
     2)  Patients symptomatic following exposure should be
         observed in a controlled setting until all signs and
         symptoms have fully resolved.
  0.4.3 INHALATION EXPOSURE
    A)  DECONTAMINATION -
     1)  INHALATION: Move patient to fresh air. Monitor for
         respiratory distress. If cough or difficulty breathing
         develops, evaluate for respiratory tract irritation,
         bronchitis, or pneumonitis. Administer oxygen and
         assist ventilation as required. Treat bronchospasm with
         an inhaled beta2-adrenergic agonist. Consider systemic
         corticosteroids in patients with significant
         bronchospasm.
    B)  IRRITATION -
     1)  Respiratory tract irritation, if severe, can progress
         to pulmonary edema which may be delayed in onset up to
         24 to 72 hours after exposure in some cases.
    C)  ACUTE LUNG INJURY -
     1)  ACUTE LUNG INJURY: Maintain ventilation and oxygenation
         and evaluate with frequent arterial blood gases and/or
         pulse oximetry monitoring. Early use of PEEP and
         mechanical ventilation may be needed.
    D)  BRONCHOSPASM -
     1)  If bronchospasm and wheezing occur, consider treatment
         with inhaled sympathomimetic agents.
    E)  OBSERVATION CRITERIA -
     1)  Carefully observe patients with inhalation exposure for
         the development of any systemic signs or symptoms and
         administer symptomatic treatment as necessary.
     2)  Patients symptomatic following exposure should be
         observed in a controlled setting until all signs and
         symptoms have fully resolved.
  0.4.4 EYE EXPOSURE
    A)  DECONTAMINATION: Remove contact lenses and irrigate
        exposed eyes with copious amounts of room temperature
        0.9% saline or water for at least 15 minutes. If
        irritation, pain, swelling, lacrimation, or photophobia
        persist after 15 minutes of irrigation, the patient
        should be seen in a healthcare facility.
  0.4.5 DERMAL EXPOSURE
    A)  OVERVIEW
     1)  DERMAL DECONTAMINATION -
      a)  DECONTAMINATION: Remove contaminated clothing and
          jewelry and place them in plastic bags. Wash exposed
          areas with soap and water for 10 to 15 minutes with
          gentle sponging to avoid skin breakdown. A physician
          may need to examine the area if irritation or pain
          persists (Burgess et al, 1999).
     2)  PESTICIDES -
      a)  DECONTAMINATION: Remove contaminated clothing and
          jewelry and place them in plastic bags. Wash exposed
          areas with soap and water for 10 to 15 minutes with
          gentle sponging to avoid skin breakdown. A physician
          may need to examine the area if irritation or pain
          persists (Burgess et al, 1999).
     3)  IRRITATION -
      a)  Treat dermal irritation or burns with standard topical
          therapy. Patients developing dermal hypersensitivity
          reactions may require treatment with systemic or
          topical corticosteroids or antihistamines.
     4)  DERMAL ABSORPTION -
      a)  Some chemicals can produce systemic poisoning by
          absorption through intact skin. Carefully observe
          patients with dermal exposure for the development of
          any systemic signs or symptoms and administer
          symptomatic treatment as necessary.
Range of Toxicity:
A)  No specific range of toxicity can be established for the
       broad field of chemicals in general.

[Rumack BH POISINDEX(R) Information System Micromedex, Inc., Englewood, CO, 2017; CCIS Volume 172, edition expires May, 2017. Hall AH & Rumack BH (Eds): TOMES(R) Information System Micromedex, Inc., Englewood, CO, 2017; CCIS Volume 172, edition expires May, 2017.] **PEER REVIEWED**


Antidote and Emergency Treatment:
Skin decontamination: If skin contamination occurs, the skin should be thoroughly washed with soap and water.
[U.S. Environmental Protection Agency/Office of Prevention, Pesticides, and Toxic Substances. Reigart, J.R., Roberts, J.R. Recognition and Management of Pesticide Poisonings. 5th ed. 1999. EPA Document No. EPA 735-R-98-003, and available in electronic format at: http://www.epa.gov/pesticides/safety/healthcare p. 63] **PEER REVIEWED**

Gastrointestinal decontamination: Due to the severe gastrointestinal irritation, gastric emptying and catharsis are not indicated. Consideration should be given to administration of activated charcoal...
[U.S. Environmental Protection Agency/Office of Prevention, Pesticides, and Toxic Substances. Reigart, J.R., Roberts, J.R. Recognition and Management of Pesticide Poisonings. 5th ed. 1999. EPA Document No. EPA 735-R-98-003, and available in electronic format at: http://www.epa.gov/pesticides/safety/healthcare p. 63] **PEER REVIEWED**

Basic treatment: Establish a patent airway. Suction if necessary. Watch for signs of respiratory insufficiency and assist ventilations if needed. Administer oxygen by nonrebreather mask at 10 to 15 L/min. Monitor for pulmonary edema and treat if necessary ... . Monitor for shock and treat if necessary ... . Anticipate seizures and treat if necessary ... . For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with normal saline during transport ... . Do not use emetics. For ingestion, rinse mouth and administer 5 ml/kg up to 200 ml of water for dilution if the patient can swallow, has a strong gag reflex, and does not drool ... . Cover skin burns with dry sterile dressings after decontamination ... . /Poison A and B/
[Bronstein, A.C., P.L. Currance; Emergency Care for Hazardous Materials Exposure. 2nd ed. St. Louis, MO. Mosby Lifeline. 1994., p. 139] **PEER REVIEWED**

Advanced treatment: Consider orotracheal or nasotracheal intubation for airway control in the patient who is unconscious, has severe pulmonary edema, or is in respiratory arrest. Positive pressure ventilation techniques with a bag valve mask device may be beneficial. Monitor cardiac rhythm and treat arrhythmias as necessary ... . Start an IV with D5W /SRP: "To keep open", minimal flow rate/. Use lactated Ringer's if signs of hypovolemia are present. Watch for signs of fluid overload. Consider drug therapy for pulmonary edema ... . For hypotension with signs of hypovolemia, administer fluid cautiously. Watch for signs of fluid overload ... . Treat seizures with diazepam (Valium) ... . Use proparacaine hydrochloride to assist eye irrigation ... . /Poison A and B/
[Bronstein, A.C., P.L. Currance; Emergency Care for Hazardous Materials Exposure. 2nd ed. St. Louis, MO. Mosby Lifeline. 1994., p. 139] **PEER REVIEWED**


Animal Toxicity Studies:


Non-Human Toxicity Excerpts:
/LABORATORY ANIMALS: Acute Exposure/ Methanolic extracts of neem leaf and bark /in mice caused/.... discomfort, gastrointestinal spasms, loss of appetite, hypothermia, and, ultimately, convulsion leading to death within 24 hr. /Neem extract/
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**

/LABORATORY ANIMALS: Subchronic or Prechronic Exposure/ The subacute toxicity of Vepacide, an enriched neem oil-based preparation containing 12% azadirachtin..., upon oral administration of 80, 160, and 320 mg/kg daily insecticide doses for 90 days was studied in male rats. On the 90th day, the high and medium doses caused significant decreases in (1) cytochrome P-450 concentrations in the liver, lungs, and kidneys but not the brain; (2) cytochrome b5 in the brain; and (3) cytochrome P-450 reductase level in the liver and brain. The highest dose also caused 10% mortality; the medium dose elicited toxic signs, including behavioral abnormalities, lacrymation, reduced feeding, and loss in body weight. No toxicity was seen for the low dose. The toxic symptoms disappeared by the 28th day after cessation of treatment.
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**

/LABORATORY ANIMALS: Developmental or Reproductive Toxicity/ Oral administration of neem seed extract to female rats from days 8 to 10 of the pregnancy caused complete resorption of embryos by day 15 of pregnancy and the animals regained fertility in cycles subsequent to treatment. Single intrauterine administration of 100 uL neem oil caused lasting infertility by apparent induction of leukocytic infiltration in the uterine epithelium during the preimplantation period (between days 3 and 5 postcoitum). Fertility was regained 5 months after treatment without apparent teratogenic effects.
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**

/LABORATORY ANIMALS: Developmental or Reproductive Toxicity/ ... Daily oral doses of neem leaf extract to male mice and rats did not affect normal development but caused reversible infertility. Spermatogenesis was not affected and the observed infertility was attributed to the decreased motility of the spermatozoa. The extract, however, was toxic to guinea pigs and rabbits. By contrast, neem seed kernel extracts lacked activity in a similar test with rats. /Neem extract/
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**

/LABORATORY ANIMALS: Developmental or Reproductive Toxicity/ Daily intramuscular injection of 250 and 500 mg/kg doses of neem oil for 8 days to male rats caused significant decreases in sperm counts, epididymal weight, and glycogen levels... . Marked structural changes in the testes and impaired spermatogenesis were also observed. /Neem extract/
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**

/GENOTOXICITY/ ... CdCl(2) and Aza induced genotoxicity in O. mossambicus, the former in greater quantity than that produced by Aza. However, Cd-induced toxicity in O. mossambicus appeared to be ameliorated to some extent by Aza.
[Chandra P, Khuda-Bukhsh AR; Ecotoxicol Environ Saf 58 (2): 194-201 (2004)] **PEER REVIEWED** PubMed Abstract

/ALTERNATIVE IN VITRO TESTS/ ... Neem-based pesticides showed relatively high toxicity to both hybridoma and oyster cells at concentrations of 1 microg AZA/mL and higher. The IC50 values for hybridoma cells were 2.15 microg AZA/mL for Neemix and 1.67 pg AZA/mL for Bioneem. Oyster cells had IC50 values of 2.18 microg AZA/mL for Neemix and 9.46 pg AZA/mL for Bioneem.
[Goktepi E, Plhak LC; J Environ Sci Health B 38 (2): 169-80 (2003)] **PEER REVIEWED** PubMed Abstract

/LABORATORY ANIMALS: Developmental or Reproductive Toxicity/ ... rats fed with 500, 1000 and 1500 mg/kg/day azadirachtin on gestation days 6-15 did not produce any significant adverse effects in reproductive parameters. Significant embryo/fetotoxic effects were not observed. There were no major malformations.
[Srivastava MK, Raizada RB; Food Chem Toxicol 39 (10): 1023-7 (2001)] **PEER REVIEWED** PubMed Abstract

/LABORATORY ANIMALS: Subchronic or Prechronic Exposure/ ... Azadirachtin technical 12% orally administered to male and female rats at doses of 500, 1000 and 1500 mg/kg/day for 90 days did not produce any signs of toxicity, mortality, changes in tissue weight, pathology and serum and blood parameters.
[Raizada RB et al; Food Chem Toxicol 39 (5): 477-83 (2001)] **PEER REVIEWED** PubMed Abstract

/ALTERNATIVE IN VITRO TESTS/ ... In the TP53 mutant cell lines, azadirachtin reduced the proportion of dividing cells and induced formation of micronuclei. Except for G-44 which showed a decrease in binucleation index, proliferation in the TP53 wild-type cell lines was unaffected by azadirachtin. ... Cell survival was suppressed by 25-69% in all cell lines.
[Akudugu J et al; Life Sci 68 (10): 1153-60 (2001)] **PEER REVIEWED** PubMed Abstract

/ALTERNATIVE IN VITRO TESTS/ ... At concentrations of azadirachtin between 10 and 100 microM significant changes in the electrophysiological properties of cultured DRG neurones were seen.
[Scott Rh et al; Comp Biochem Physiol C Pharmacol Toxicol Endocrinol 123 (1): 85-93 (1999)] **PEER REVIEWED** PubMed Abstract


Ecotoxicity Excerpts:
/AQUATIC SPECIES/ ...Exposure to concentrations of 0.40 and 0.50 mg/L /azadirachtin/ resulted in a significant decrease in percent fertilization success of B. quercicus eggs, and a marked reduction in swimming speed of stage 24 tadpoles. At a concentration of 0.50 mg/L, food consumption by stage 24 tadpoles was significantly reduced.
[Punzo F; Florida Scientist 60 (3): 158-65 (1997)] **PEER REVIEWED**

/AQUATIC SPECIES/ ... . Chlorophyll and protein contents of the algae, and the concentrations of the insecticides in water and algae were monitored at intervals of time up to 20 days. Chlorophyll and protein contents in algae were inhibited at treatment levels of 3.0 and 4.5 ug AZ-A/mL, whereas at 1.5 ug/mL, the chemical stimulated the chlorophyll production. The partition of AZ-A between water and algae was reversible, and the bioconcentration factor (BCF) was low. In contrast, TF dosed at 0.25 to 0.75 ug/mL stimulated algal growth.
[Sundaram K MS; J Environ Sci Health Part B (Pesticides Food Contaminants and Agricultural Wastes) 32 (2): 295-312 (1997)] **PEER REVIEWED**

/FIELD STUDIES/ Outdoor stream channels were treated with a commercial neem formulation, Neemix 4.5, and a neem extract (no formulation ingredients) to determine the effects on aquatic insect communities. An exposure period of 5 hr was chosen to simulate the transient nature of pesticide residues in streams and rivers after aerial applications. Multivariate analytic procedures based on Bray-Curtis similarity matrices were used to compare community structure among the replicate channels 9 days after treatment. No significant differences in community structure were found among controls and channels treated with Neemix at an azadirachtin concentration of 0.28 mg/L, but a multivariate measure of community stress indicated an increase in variability among treated channels. Significant differences in community structure were found among controls and channels treated with Neemix at 0.84 and 2.54 mg/L. The formulation ingredients of Neemix were at least partially responsible for the significant effects on community structure at 0.84 mg/L azadirachtin. No significant differences were found among controls and channels treated with the extract at 0.9 mg/L, whereas the community structure of aquatic insects in channels treated at 3.0 mg/L differed significantly from controls.
[Kreutzweiser DP et al; Environ Toxicol Chem 19 (4): 855-861 (2000)] **PEER REVIEWED**


Non-Human Toxicity Values:
LD50 Rat oral >5000 mg/kg
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**

LD50 Rabbit oral >2000 mg/kg
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**

LD50 Rabbit dermal >2000 mg/kg
[Tomlin CDS, ed. Azadirachtin (11141-17-6). In: The e-Pesticide Manual, 13th Edition Version 3.1 (2004-05). Surrey UK, British Crop Protection Council.] **PEER REVIEWED**

LD50 Mouse oral 13 mg/kg /Neem extract/
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**


Ecotoxicity Values:
LC50 Bufo quercus (Oak toad, tadpoles- stage 12) 4.41 mg/L/96 hr (95% confidence interval: 3.9-4.6 mg/L) /Conditions of bioassay not specified in source examined/ /formulated product/
[Punzo F; Florida Scientist 60 (3): 158-65 (1997)] **PEER REVIEWED**

LC50 Bufo quercus (Oak toad, tadpoles- stage 16) 4.39 mg/L/96 hr (95% confidence interval: 3.7-4.5 mg/L) /Conditions of bioassay not specified in source examined/ /formulated product/
[Punzo F; Florida Scientist 60 (3): 158-65 (1997)] **PEER REVIEWED**

LC50 Bufo quercus (Oak toad, tadpoles- stage 20) 6.12 mg/L/96 hr (95% confidence interval: 5.8-6.2 mg/L) /Conditions of bioassay not specified in source examined/ /formulated product/
[Punzo F; Florida Scientist 60 (3): 158-65 (1997)] **PEER REVIEWED**

LC50 Bufo quercus (Oak toad, tadpoles- stage 24) 11.34 mg/L/96 hr (95% confidence interval: 10.3-11.7 mg/L) /Conditions of bioassay not specified in source examined/ /formulated product/
[Punzo F; Florida Scientist 60 (3): 158-65 (1997)] **PEER REVIEWED**

LC50 Bufo quercus (Oak toad, tadpoles- stage 30) 19.62 mg/L/96 hr (95% confidence interval: 17.9-20.4 mg/L) /Conditions of bioassay not specified in source examined/ /formulated product/
[Punzo F; Florida Scientist 60 (3): 158-65 (1997)] **PEER REVIEWED**

LC50 Isonychia bicolor/rufa (Mayfly) 1.12 mg/L/1 hr (95% confidence interval: 0.98-1.27 mg/L); flow through
[Kreutzweiser DP; Ecotoxicol Environ Saf 36 (2): 109-117 (1997) Available from, as of September 30, 2005: http://cfpub.epa.gov/ecotox/quick_query.htm **PEER REVIEWED**

LC50 Daphnia pulex 0.028 uL/mL/48 hr /Conditions of bioassay not specified in source examined/ /Neemix/
[Goktepe I et al; Environ Toxicol Chem 21 (1): 31-36 (2002)] **PEER REVIEWED** PubMed Abstract

LC50 Daphnia pulex 0.033 uL/mL/48 hr /Conditions of bioassay not specified in source examined/ /Bioneem/
[Goktepe I et al; Environ Toxicol Chem 21 (1): 31-36 (2002)] **PEER REVIEWED** PubMed Abstract

LC50 Daphnia pulex 0.382 ug/mL/48 hr /Conditions of bioassay not specified in source examined/ /95% AZA/
[Goktepe I et al; Environ Toxicol Chem 21 (1): 31-36 (2002)] **PEER REVIEWED** PubMed Abstract


Metabolism/Pharmacokinetics:


Metabolism/Metabolites:
Injection of a tritiated azadirachtin derivative, (22,23-(3)H)dihydroazadirachtin into locusts indicated fast clearing of radiolabeled material from the blood. Ninety percent of the applied radioactivity was excreted during the first 7 hr with the feces, whereas the remaining (22,23-(3)H)dihydroazadirachtin accumulated in the Malpighian tubules where it could be detected even 24 days after treatment. After the first 24 hr, feces contained at least three polar, unidentified metabolites but no (22,23-(3)H)dihydroazadirachtin.
[Krieger, R. (ed.). Handbook of Pesticide Toxicology. Volume 1, 2nd ed. 2001. Academic Press, San Diego, California., p. 132] **PEER REVIEWED**


Pharmacology:


Environmental Fate & Exposure:


Environmental Fate/Exposure Summary:
Azadirachtin's production may result in its release to the environment through various waste streams; it's use as an insecticide will result in its direct release to the environment. Azadirachtin is the main component in neem seed extract. If released to air, a vapor pressure of 2.7X10-11 mm Hg indicates azadirachtin will exist solely in the particulate phase in the atmosphere. Particulate-phase azadirachtin will be removed from the atmosphere by wet and dry deposition. Azadirachtin has a reported half-life of 3.9 days when exposed to UV light. If released to soil, azadirachtin is expected to have high mobility based upon a Koc of 93. Volatilization from moist soil surfaces is not expected to be an important fate process based upon an estimated Henry's Law constant of 9.9X10-14 atm-cu m/mole. Azadirachtin is not expected to volatilize from dry soil surfaces based upon its vapor pressure. When incubated with soil in the dark at pH 7 azadirachtin had reported half-lives of 43.9 and 19.8 days at 15 and 25 deg C, respectively. When the soil was autoclaved to remove microbes the half-lives of azadirachtin increased to 91.2 and 31.5 days at 15 and 25 deg C under similar conditions. In a separate study azadirachtin had soil half-lives ranging from 26-29 days at 18 deg C, pH 6.0 and exposed to natural light. If released into water, azadirachtin is not expected to adsorb to suspended solids and sediment based upon the estimated Koc. Volatilization from water surfaces is not expected to be an important fate process based upon this compound's estimated Henry's Law constant. An estimated BCF of 1.3 suggests the potential for bioconcentration in aquatic organisms is low. A measured hydrolysis half-life of 282 hours was observed at 25 deg C when azadirachtin was placed in a phosphate buffer at pH 7. Occupational exposure to azadirachtin may occur through inhalation of powder and dermal contact with this compound at workplaces where azadirachtin is produced or used. The greatest potential for dermal and inhalation exposure to azadirachtin is expected when the material is being applied to fields and crops for use in insect control. (SRC)
**PEER REVIEWED**


Probable Routes of Human Exposure:
Occupational exposure to azadirachtin may occur through inhalation and dermal contact with this compound at workplaces where azadirachtin is produced or used. The greatest potential for dermal and inhalation exposure to azadirachtin is expected when the material is being applied to fields and crops for use in insect control. (SRC)
**PEER REVIEWED**


Natural Pollution Sources:
Azadirachtin oil is the main component of neem seed extract(1,2).
[(1) Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003) (2) US EPA; Recognition and Management of Pesticide Poisonings. 5th ed. Reigart JR, Roberts JR, eds. 1999. U.S. Environ Prot Agency/Off Prev Pest Toxic Sub. USEPA 735-R-98-003. Available at http://www.epa.gov/oppfead1/safety/healthcare/handbook/handbook.htm as of Nov 14, 2005.] **PEER REVIEWED**


Artificial Pollution Sources:
Azadirachtin's production may result in its release to the environment through various waste streams; it's use as an insecticide(1) will result in its direct release to the environment(SRC).
[(1) Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**


Environmental Fate:
TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 93(SRC), determined from a log Kow of 1.07(2) and a regression-derived equation(3), indicates that azadirachtin is expected to have high mobility in soil(SRC). Volatilization of azadirachtin from moist soil surfaces is not expected to be an important fate process(SRC) given an estimated Henry's Law constant of 9.9X10-14 atm-cu m/mole(SRC), derived from a vapor pressure of 2.7X10-11 mm Hg(4) and a water solubility of 260 mg/L(4). Azadirachtin is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(4). The half-life range of azadirachtin in soil at 18 deg C, pH 6.0 and exposed to natural light was 26-29 days(5). Soil half-lives in non-autoclaved soils ranging from 19.9 to 43.9 days(6,7) as opposed to half-lives of 37.6 to 91.2 days in autoclaved soils(6,7) suggesting that biodegradation may be an important environmental fate process in soil(SRC).
[(1) Swann RL et al; Res Rev 85: 17-28 (1983) (2) Tomlin CDS, ed; The Pesticide Manual. 11th ed., Surrey, England: British Crop Protection Council p. 59 (1997) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9 (1990) (4) Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003) (5) Thompson DG et al; Bull Environ Contam Toxicol 69: 250-256 (2002) (6) Sundram KMS; J Environ Sci Health B31 4: 913-914 (1996) (7) Stark JD, Watler JF; J Enivon Sci Health B30: 685-698 (1995)] **PEER REVIEWED**

AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 93(SRC), determined from a log Kow of 1.07(2) and a regression-derived equation(3), indicates that azadirachtin is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is not expected(3) based upon an estimated Henry's Law constant of 9.9X10-14 atm-cu m/mole(SRC), derived from a vapor pressure of 2.7X10-11 mm Hg(4) and a water solubility of 260 mg/L(4). According to a classification scheme(5), an estimated BCF of 1.3(SRC), from its log Kow(2)and a regression-derived equation(6), suggests the potential for bioconcentration in aquatic organisms is low(SRC). A measured half-life of 282 hours was observed at 25 deg C when azadirachtin was placed in a phosphate buffer at pH 7(7). Soil half-lives in non-autoclaved soils ranging from 19.9 to 43.9 days(8,9) as opposed to half-lives of 37.6 to 91.2 days in autoclaved soils(8,9) suggest that biodegradation may be an important environmental fate process in water(SRC).
[(1) Swann RL et al; Res Rev 85: 17-28 (1983) (2) Tomlin CDS, ed; The Pesticide Manual. 11th ed., Surrey, England: British Crop Protection Council p. 59 (1997) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9, 15-1 to 15-29 (1990) (4) Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003) (5) Franke C et al; Chemosphere 29: 1501-14 (1994) (6) Meylan WM et al; Environ Toxicol Chem 18: 664-72 (1999) (7) Szeto SY, Wan MT; J Agric Food Chem 44: 1160-1163 (1996) (8) Sundram KMS; J Environ Sci Health B31: 913-914 (1996) (9) Stark JD, Watler JF; J Enivon Sci Health B30: 685-698 (1995)] **PEER REVIEWED**

AQUATIC FATE: In-situ enclosures treated with azadirachtin concentrations ranging from 0.035 to 1.75 mg/L were deployed in a lake in Ontario Canada(1). Thirteen different samples from these enclosures were taken over a 50 day period. A dissipation half-life of azadirachtin with natural sun light, pH6, and 18 deg C is 24.7 days which is similar to the half-life of 30.5 days from an experiment done in the dark at 20 deg C and pH 7(1).
[(1) Thompson DG; Bull Environ Contam Toxicol 69: 250-6 (2002)] **PEER REVIEWED** PubMed Abstract

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), azadirachtin, which has a vapor pressure of 2.7X10-11 mm Hg at 25 deg C(2), is expected to exist solely in the particulate phase in the ambient atmosphere. Particulate-phase azadirachtin may be removed from the air by wet and dry deposition(SRC). The half-life for photolysis of azadirachtin is 50 days(2). Azadirachtin has a reported half-life of 3.9 days when exposed to UV light(3).
[(1) Bidleman TF; Environ Sci Technol 22: 361-367 (1988) (2) Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003) (3) Sundaram KMS, Curry J; Chemosphere 32: 649-59 (1996)] **PEER REVIEWED**


Environmental Biodegradation:
AEROBIC: Azadirachtin degradation in soil was studied in a laboratory setting. The soil, autoclaved and non-autoclaved, was treated with azadirachtin incubated at either 15 or 25 deg C and monitored for degradation. Azadirachtin had reported soil half-lives of 43.9 and 19.8 days at 15 and 25 deg C, respectively(1). When the soil was autoclaved to remove microbes the half-lives increased to 91.2 and 31.5 days at 15 and 25 deg C, respectively(1). In a similar study, soil half-lives of autoclaved and nonautoclaved soils were 37.65 and 25.77 days, respectively, when soil was kept in a greenhouse at 21 deg C and a moisture level of 40%(2).
[(1) Stark JD, Watler JF; J Enivon Sci Health B30: 685-698 (1995) (2) Sundram KMS; J Environ Sci Health B31: 913-914 (1996)] **PEER REVIEWED**


Environmental Abiotic Degradation:
The rate constant for the vapor-phase reaction of azadirachtin with ozone has been estimated as 8.3X10-17 cu cm/molecule-sec at 25 deg C(SRC) that was derived using a structure estimation method(1). This corresponds to an atmospheric half-life of about 0.14 days at an atmospheric concentration of 7X10+11 ozone molecules per cu cm(2).
[(1) Meylan WM, Howard PH; Chemosphere 26: 2293-99 (1993) (2) Atkinson R, Carter WPL; Chem Rev 84: 437-70 (1984)] **PEER REVIEWED**

A measured half-life of 282 hours was observed at 25 deg C when azadirachtin was placed in a phosphate buffer at pH 7(1). Solutions of azadirachtin with or without UV absorbing chemicals dihydroxybenzophenone, para-amino benzoic acid or florescent brightener 28, were placed on a glass slides and placed in a chamber where they were exposed to 2 halide and one sodium lamp with wavelenghts ranging from 300-1000 nm and an intensity that corresponded to about 26.3 % of natural sunlight on glass surfaces during that time period(2). Azadirachtin had a reported half-life of 3.9 days when exposed to UV light. Addition of dihydroxybenzophenone, para-amino benzoic acid increased the half-life to 22.54 and 7.37 days(2).
[(1) Szeto SY, Wan MT; J Agric Food Chem 44: 1160-1163 (1996) (2) Sundaram KMS, Curry J; Chemosphere 32: 649-59 (1996)] **PEER REVIEWED**

Azadirachtin was sprayed on both oak and balsam at rates of 7 g in 2.8 L/hour, 15 g in 5.9 L/hour and 40 g in 15.8 L/hour (1). Despite the fact that the initial concentrations ranged from 4-96 ug/g, azadirachtin had a half life of 17-22 hours on all of the plants(1).
[(1) Sundaram A; Am Chem Soc, Div Agrochem, 207th Nat. Meet. ACS Symposium Ser. 595, Ch 8 pp. 108-33 (1995)] **PEER REVIEWED**


Environmental Bioconcentration:
An estimated BCF of 1.3 was calculated for azadirachtin(SRC), using a log Kow of 1.09(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is low(SRC).
[(1) Tomlin CDS, ed; The Pesticide Manual World Compendium. 11th ed., Surrey, England: British Crop Protection Council. p. 59 (1997) (2) Meylan WM et al; Environ Toxicol Chem 18: 664-72 (1999)(3) Franke C et al; Chemosphere 29: 1501-14 (1994)] **PEER REVIEWED**


Soil Adsorption/Mobility:
The Koc of azadirachtin is estimated as 93(SRC), using a log Kow of 1.09(1)and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that azadirachtin is expected to have high mobility in soil.
[(1) Tomlin CDS, ed; The Pesticide Manual World Compendium. 11th ed., Surrey, England: British Crop Protection Council. p. 59 (1997) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9 (1990) (3) Swann RL et al; Res Rev 85: 17-28 (1983)] **PEER REVIEWED**


Volatilization from Water/Soil:
The Henry's Law constant for azadirachtin is estimated as 2.8X10-25 atm-cu m/mole(SRC)derived from a vapor pressure of 2.7X10-11 mm Hg(1) and a water solubility of 260 mg/L(1). This Henry's Law constant indicates that azadirachtin is expected to be essentially nonvolatile from moist soil and water surfaces(2). Azadirachtin is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(1).
[(1) Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990)] **PEER REVIEWED**


Environmental Standards & Regulations:


FIFRA Requirements:
An exemption from the requirement of a tolerance is established for the biochemical azadirachtin, which is isolated from the berries of the Neem tree (Azadirachta indica), when used as a pesticide ... on all raw agricultural commodities.
[40 CFR 180.1119; U.S. National Archives and Records Administration's Electronic Code of Federal Regulations. Available from, as of October 11, 2005: http://www.ecfr.gov **PEER REVIEWED**

New Active Ingredients ... includes pesticide active ingredients initially registered after November 1, 1984, that currently have active product registrations. By law, these newer pesticides are not subject to the reregistration program. They must, however, meet the new safety standard of the FQPA, and will be reviewed on a 15-year cycle under the registration review program. ... Active Ingredient Number: 121701; Type of Pesticide: conventional - insecticide; Use Site: food use; Year: 1985.
[United States Environmental Protection Agency/ Prevention, Pesticides and Toxic Substances; Status of Pesticides in Registration, Reregistration, and Special Review. (1998) EPA 738-R-98-002, p. 353] **PEER REVIEWED**


Allowable Tolerances:
An exemption from the requirement of a tolerance is established for the biochemical azadirachtin, which is isolated from the berries of the Neem tree (Azadirachta indica), when used as a pesticide at 20 grams or less per acre on all raw agricultural commodities.
[40 CFR 180.1119; U.S. National Archives and Records Administration's Electronic Code of Federal Regulations. Available from, as of October 11, 2005: http://www.ecfr.gov **PEER REVIEWED**


Chemical/Physical Properties:


Molecular Formula:
C35-H44-O16
[O'Neil, M.J. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. 13th Edition, Whitehouse Station, NJ: Merck and Co., Inc., 2001., p. 155] **PEER REVIEWED**


Molecular Weight:
720.7
[Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**


Color/Form:
Microcrystalline powder
[O'Neil, M.J. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. 13th Edition, Whitehouse Station, NJ: Merck and Co., Inc., 2001., p. 155] **PEER REVIEWED**

Yellow green powder
[Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**


Odor:
Strong garlic/sulfur odor
[Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**


Melting Point:
154-158 deg C
[O'Neil, M.J. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. 13th Edition, Whitehouse Station, NJ: Merck and Co., Inc., 2001., p. 155] **PEER REVIEWED**


Octanol/Water Partition Coefficient:
log Kow = 1.09
[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium, 11 th ed., British Crop Protection Council, Surrey, England 1997, p. 59] **PEER REVIEWED**


Solubilities:
Readily soluble in ethanol, diethyl ether, acetone, and chloroform. Insoluble in hexane.
[Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**

In water, 0.26 g/L at 25 deg C
[Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**


Spectral Properties:
UV max = 217
[O'Neil, M.J. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. 13th Edition, Whitehouse Station, NJ: Merck and Co., Inc., 2001., p. 155] **PEER REVIEWED**

Specific optical rotation = -53 degrees (C=0.5 in chloroform)
[O'Neil, M.J. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. 13th Edition, Whitehouse Station, NJ: Merck and Co., Inc., 2001., p. 155] **PEER REVIEWED**


Vapor Pressure:
2.7X10-11 mm Hg at 25 deg C
[Tomlin CDS, ed; The e-Pesticide Manual: a world compendium. Azadirachtin. 13th ed. PC CD-ROM, Version 3.0, 2003-04. Surrey, UK: British Crop Protection Council, (2003)] **PEER REVIEWED**


Other Chemical/Physical Properties:
Henry's Law constant = 2.8X10-25 atm-cu m/mole at 25 deg C (est)
[US EPA; Estimation Program Interface (EPI) Suite. Ver.3.11. June 10, 2003. Available from, as of Oct 10, 2005: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm **PEER REVIEWED**

Hydroxyl radical reaction rate constant = 2.3X10-10 cu cm/molec-sec at 25 deg C (est)
[US EPA; Estimation Program Interface (EPI) Suite. Ver.3.11. June 10, 2003. Available from, as of Oct 10, 2005: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm **PEER REVIEWED**


Chemical Safety & Handling:


Flash Point:
>137 deg F (Closed cup)
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**


Protective Equipment & Clothing:
Chemical-resistant gloves. Long-sleeved shirt and long pants. Protective eyewear. Shoes plus socks.
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**


Preventive Measures:
/For applying the product/ wear the items of protective clothing the label requires: for example, non-absorbent gloves (not leather or fabric), rubber footwear (not canvas or leather), a hat, goggles, or a dust-mist filter. If no specific clothing is listed, gloves, long-sleeved shirts and long pants, and closed shoes are recommended. You can buy protective clothing and equipment at hardware stores or building supply stores.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.19 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

Indoor Applications. If the label directions permit, leave all windows open and fans operating after the application is completed. If the pesticide product is only effective in an unventilated (sealed) room or house, do not stay there. Put all pets outdoors, and take yourself any your family away from treated areas for at least the length of time prescribed on the label. Apply most surface sprays only to limited areas such as cracks; don't treat entire floors, walls, or ceilings. Don't let pesticides get on any surfaces that are used for food preparation. Wash any surfaces that may have pesticide residue before placing food on them.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.20 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

Indoor Applications. When using total release foggers to control pests, use no more than the amount needed and to keep foggers away from ignition sources (ovens, stoves, air conditioners, space heaters, and water heaters, for example). Foggers should not be used in small, enclosed places such as closets and cabinets or under tables and counters.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.21 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

Outdoor Applications. Never apply pesticides outdoors on a windy day (winds higher than 10 mph). Position yourself so that a light breeze does not blow pesticide spray or dust into your face.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.21 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

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.
**PEER REVIEWED**


Stability/Shelf Life:
Stable in the dark. DT50 50 days (pH 5, room temperature); rapidly decomposed at higher temperatures, in alkaline and strongly acidic media.
[Tomlin CDS, ed. Azadirachtin (11141-17-6). In: The e-Pesticide Manual, 13th Edition Version 3.1 (2004-05). Surrey UK, British Crop Protection Council.] **PEER REVIEWED**


Storage Conditions:
Store in a cool, well-ventilated, secure area out of reach of children and animals.
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**

Safe Storage of Pesticides. Always store pesticides in their original containers, complete with labels that list ingredients, directions for use, and first aid steps in case of accidental poisoning. Never store pesticides in cabinets with or near food, animal feed, or medical supplies. Do not store pesticides in places where flooding is possible or in places where they might spill or leak into wells, drains, ground water, or surface water.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.23 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**


Cleanup Methods:
If a spill occurs, clean it up promptly. Don't wash it away. Instead, sprinkle the spill with sawdust, vermiculite, or kitty litter. Sweep it into a plastic garbage bag, and dispose of it as directed on the pesticide product label.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.20 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

After Applying a Pesticide, Indoors or Outdoors. To remove pesticide residues, use a bucket to rinse tools or equipment three times, including any containers or utensils that you used when mixing the pesticide. Then pour the rinsewater into the pesticide sprayer and reuse the solution by applying it according to the pesticide product label directions. After applying any pesticide wash your hands and any other parts of your body that may have come in contact with the pesticide..To prevent tracking pesticides inside, remove or rinse your boots or shoes before entering your home. Wash any clothes that have been exposed to a lot of pesticide separately from your regular wash.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.22 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**


Disposal Methods:
Safe Disposal of Pesticides. The best way to dispose of small amounts of excess pesticides is to use them - apply them - according to the directions on the label. If you cannot use them, ask your neighbors whether they have a similar pest control problem and can use them. If all of the remaining pesticide cannot be properly used, check with your local solid waste management authority, environmental agency, or health department to find out whether your community has a household hazardous waste collection program or a similar program for getting rid of unwanted, leftover pesticides. These authorities can also inform you of any local requirements for pesticide waste disposal.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.24 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

Safe Disposal of Pesticides. An empty pesticide container can be as hazardous as a full one because of residues left inside. Never reuse such a container. When empty, a pesticide container should be rinsed carefully three times and the rinsewater thoroughly drained back onto the sprayer or the container previously used to mix the pesticide. Use the rinsewater as a pesticide, following label directions. Replace the cap or closure securely. Dispose of the container according to label instructions. Do not puncture or burn a pressurized container like an aerosol - it could explode. Do cut or puncture other empty pesticide containers made of metal or plastic to prevent someone from reusing them. Wrap the empty container and put it in the trash after you have rinsed it.
[USEPA/Prevention, Pesticides, and Toxic Substances; Citizen's Guide to Pest Control and Pesticide Safety p.25 (Septemper 1995) EPA 730-K-95-001] **PEER REVIEWED**

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 quality; potential migration in soil or water; effects on animal, aquatic, and plant life; and conformance with environmental and public health regulations.
**PEER REVIEWED**


Occupational Exposure Standards:


Manufacturing/Use Information:


Uses:
For azadirachtin (USEPA/OPP Pesticide Code: 121701) ACTIVE products with label matches. /SRP: Registered for use in the U.S. but approved pesticide uses may change periodically and so federal, state and local authorities must be consulted for currently approved uses./
[U.S. Environmental Protection Agency/Office of Pesticide Program's Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of October 11, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Insecticide; Disrupts insect molting by antagonizing the insect hormone ecdysone and also serve as feeding deterrent for some insects.
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**


Manufacturers:
Agridyne Technologies, Inc., 7500 Grace Dr., Columbia, MD 21044, (410) 532-4578 /Regristrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Agro Logistic Systems Inc., P.O. Box 5799, Diamond Bar, CA 91765 , (909) 594-7222 /Registant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

AMVAC Chemical Corp., 4695 Macarthur Court, Suite 1250, Newport Beach, CA 92660-1706, 949-260-1212 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Certis USA, LLC 9145 Guilford Road, Suite 175, Columbia, MD 21046 (301) 483-3806 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

E.I.D. Parry (India) Ltd., 1101 17th St., N.W. Washington, DC 20036, (415) 267-4123 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Fortune Biotech Limited, 1730 M Street, N.W., Suite 906, Washington, DC 20036, (703) 267-6905 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Grace Biopesticides, W.R. Grace & Co. - Conn., 7500 Grace Dr., Columbia, MD 21044-4098, (410) 531-4774 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Holy Terra Products, Inc., 115 Fox St., Portland, ME 04101-2539, (207) 871-8822 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

PBI/Gordon Corp., P.O. Box 014090, 1217 West 12th Street, Kansas City, MO 64101-0090. (816) 460-6292 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

PBT International, 13532 Hunting Hill Way, North Potomac, MD 20878-4834 (301) 926-9873 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Vikwood Botanicals, Inc., 1817 North 5th St., Sheboygan, WI 53081, (414) 452-4975 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**

Vikwood Ltd., P.O. Box 554, 1221A Super, Sheboygan, WI 53081 /Registrant/
[National Pesticide Information Retrieval System's USEPA/OPP Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of Oct 25, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**


Methods of Manufacturing:
... Isolated from the berries of the Neem tree (Azadirachta indica).
[40 CFR 180.1119; U.S. National Archives and Records Administration's Electronic Code of Federal Regulations. Available from, as of October 11, 2005: http://www.ecfr.gov **PEER REVIEWED**


Formulations/Preparations:
Discontinued products: Blokade, Bollwhip, Margosan-O, Neemazad, Turplex, SureFire, and Neemachtin
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**

Trade Names: Azatin EC, Azatin Technical and Azatin-Plus EC.
[U.S. Environmental Protection Agency/Office of Pesticide Program's Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of October 11, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**


Laboratory Methods:


Analytic Laboratory Methods:
Analysis by hplc.
[Tomlin CDS, ed. Azadirachtin (11141-17-6). In: The e-Pesticide Manual, 13th Edition Version 3.1 (2004-05). Surrey UK, British Crop Protection Council.] **PEER REVIEWED**


Special References:


Synonyms and Identifiers:


Synonyms:
dimethyl (3S,3aR,4S,5S,5aR,5a+1R,7aS,8R,10S,10aS)-8-acetoxy-3,3a,4,5,5a,5a+1,7a,8,9,10-decahydro-3,5-dihydroxy-4-((1S,3S,7S,8R,9S,11R)-7-hydroxy-9-methyl-2,4,10-trioxatetracyclo(6.3.1.0+3.7.0+9.11)dodec-5-en-11-yl)-4-methyl-10((E)-2-methylbuy-2-enoyloxy)-1H,7H-naphtho(1,8a,8-bc:4,4a-c')difuran-3,7a-dicarboxylate
**PEER REVIEWED**

dimethyl (2aR-(2aalpha,3beta,4beta(1aR*,2S*,3aS*,6aS*,7S*,7aS*),4abeta,5alpha,7aS*,8beta(E),10beta,10aalpha,10bbeta))-10-(acetyloxy)octahydro-3,5-dihydroxy-4-methyl-8-((2-methyl-1-oxo-2-butenyl)oxy)-4-(3a,6a,7,7a-tetrahydro-6a-hydroxy-7a-methyl-2,7-methanofuro(2,3-b)oxireno(e)oxepin-1a(2H)-yl)-1H,7H-naphtho(1,8-bc:4,4a-c')difuran-5,10a(8H)-dicarboxylate
**PEER REVIEWED**

USEPA/OPP Pesticide Code: 121701
**PEER REVIEWED**


Formulations/Preparations:
Discontinued products: Blokade, Bollwhip, Margosan-O, Neemazad, Turplex, SureFire, and Neemachtin
[Crop Protection Handbook 2005. (Formerly Farm and Chemicals Handbook) Willoughby, OH: Meister Publishing Co., 2005., p. D-30] **PEER REVIEWED**

Trade Names: Azatin EC, Azatin Technical and Azatin-Plus EC.
[U.S. Environmental Protection Agency/Office of Pesticide Program's Chemical Ingredients Database on Azadirachtin (11141-17-6). Available from, as of October 11, 2005: http://npirspublic.ceris.purdue.edu/ppis/ **PEER REVIEWED**


Administrative Information:


Hazardous Substances Databank Number: 7372

Last Revision Date: 20060420

Last Review Date: Reviewed by SRP on 1/12/2006

Update History:
Complete Update on 2006-04-20, 42 fields added/edited/deleted
Created 20050920