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TRIAZINE HERBICIDES

Classification   |    Detailed evidence-based information

Therapeutic Toxic Class

    A) Substituted triazine compounds are widely used as selective or nonselective herbicides. These herbicides are marketed in a wide variety of liquid and granular formulations. The TOXICITY of the formulation products may be determined mainly by ingredients other than the triazine herbicide. A Poison Control Center or the product manufacturer SHOULD be contacted to obtain product specific information in the event of serious toxicity.
    B) Triazoles are used as fungicides, herbicides, and insecticides.

Specific Substances

    A) Ametryn
    1) N-Ethyl-N'-(1-methylethyl)-6-(methylthio) -1,3,5-triazine-2,4-diamine
    2) 2-(ethylamino)-4-(isopropylamine) -6-(methylthio)-s-triazine
    3) CAS 834-12-8
    Atraton
    1) 2-(ethylamino)-4-(isopropylamino) -6-methoxy-s-triazine
    2) CAS 1610-17-9
    Atrazine
    1) 6-Chloro-N-ethyl-N'-(1-methylethyl) -1,3,5-triazine-2,4-diamine
    2) 2-chloro-4-ethylamino-6-isopropylamine-s-triazine
    3) fenamine (atrazine)
    4) fenamine (amitrole)
    5) herbicide (triazines)
    6) triazines
    7) CAS 1912-24-9
    Cyanazine
    1) 2-((4-Chloro-6-(ethylamino)-1,3,5-triazin-2yl) amino) -2-methyl-propanenitrile
    2) CAS 21725-46-2
    Cyprazine
    1) 2-chloro-4-(cyclopropylamino)-6-(isopropylamino) -s-triazine
    2) CAS 22936-86-3
    Desmetryn
    1) 2-isopropylamino-4-methylamino-6-methylthio -1,3,5-triazine
    2) N-methyl-N'-(1-methylethyl)-6-(methylthio) -1,3,5-triazine-2,4-diamine
    3) CAS 1014-69-3
    Hexazinone
    1) 3-Cyclohexyl-6-(dimethylamino)-1-methyl-1,3,5-triazine-2,4(1H,3H)- dione
    2) CAS 51235-04-2
    Isomethiozin
    1) 6-tert-butyl-4-iso butylideneamino-3-methylthio -1,2,4-triazine-5 (4H)-one
    2) CAS 57052-04-7
    Metribuzin
    1) 4-amino-6-tert-butyl-4,5-dihydro-3-methylthio -1,2,4-triazin-5-one
    2) 4-amino-6-(1,1-dimethylethyl)-3-(methylthio) 1,2,,4-triazin-5(4H)-one
    3) CAS 21087-64-9
    Prometon
    1) 6-Methoxy-N,N'-bis(1-methylethyl) -1,3,5-triazine-2,4-diamine
    2) 2,4-bis(isopropylamino)-6-methoxy-s-triazine
    3) primatol (atrazine)
    4) CAS 1610-18-0
    Prometryn
    1) N,N'Bis(1-methylethyl)-6-methylthio-1,3,5-triazine-2,4-diamine
    2) 2,4-bis(isopropylamino)-6-(methylthio)-s-triazine
    3) CAS 7287-19-6
    Propazine
    1) 6-Chloro-N,N'-bis(1-methylethyl)-1,3,5-triazine-2,4-diamine
    2) 2-chloro-4,6-bis(isopropylamino)-s-triazine
    3) CAS 139-40-2
    Simazine
    1) 6-Chloro-N,N'-diethyl-1,3,5-triazine-2,4-diamine
    2) 2-chloro-4,6-bis(ethylamino)-s-triazine
    3) CAS 122-34-9
    Terbuthylazine
    1) 2-tert-butylamino-4-chloro-6-ethylamino-1,3,5-triazine
    2) 6-chloro-N-(1,1-dimethylethyl)-N'-ethyl-1,3,5-triazine-2,4-diamine
    3) CAS 5915-41-3
    Terbutryn
    1) 2-tert-butylamino-4-ethylamino-6-methylthio-1,3,5-triazine
    2) CAS 886-50-0

Available Forms Sources

    A) FORMS
    1) Some of the most widely used triazine products and their commercial names include (Morgan, 1989; Reigart & Roberts, 1999):
    Generic NameTrade Name(s)
    AmetrynAmephyt
     Ametrex
     Cemerin
     Evik
     Gardopax
     Gesapax
     Primatol-Z80
    AtratonAtratone
     Gesatamin
    AtrazineAatrex
     Aktocon
     Atranex
     Atred
     Candex
     Chromozin
     Crisazine
     Cyazin
     Fenamin
     Fenatrol
     Gesoprim
     Griffex
     Primatol-A
     Purge
     Radzin
     Strazine
     Vectal SC
     Zeazine
    CyanazineBladex
     Fortrol
    CyprazineOutfox
    DesmetrynSamuron
     Semeron
     Topusyn
    HexazinoneVelpar
    IsomethiozineTantizon
    MetribuzinLexone
     Sencor
     Sencoral
     Sencorex
     Sengural
    PrometonGesafram
     Ontracic 800
     Ontrack
     Pramitol 5P
     Prometrone
    PrometrynCaparol
     Gesagard
     Mercasin
     Primatol-Q
     Promepin
     Prometrex
    PropazineGesamil
     Milogard
     Milo-Pro
     Plantulin
     Primatol-P
     Prozinez
    SimazineAquazine
     Bitemole
     Caliber 90
     Caliger
     Cekusan
     Gesatop
     Herbizin
     Primatol-S
     Princep
     Printop
     Simadex
     Simanex
     Tafazine
     Taphazine
    TerbuthylazineGardoprim
     Primatol-M
    TerbutrynClarosan
     Ingran
     Shortstop
     Shortstop-E
     Prebane
     Terbutrex
     Ternit

    2) Triazole herbicides are structurally and toxicologically similar to the triazine herbicides. A five-member ring (triazole) replaces the six-member ring of the triazine herbicide general structure (Morgan, 1989; Sine, 1991).
    Generic NameTrade Name(s)
    AmitroleAmerol
     Amitrol-t
     Amizol
     AT-90
     Azolan
     Azole
     Cytrol
     Diurol
     Herbizole
     Simazol
     Weedazol

    3) Triazoles are used as fungicides, herbicides, and insecticides (Stevens & Sumner, 1991).
    4) Amitrole is a synonym for triazole (CAS 61-82-5).
    B) USES
    1) Most triazine herbicides are used in selective weed control programs while others (ie, prometon) have nonselective properties. These agents have been available since the early 1950s. Members of this family include atrazine, hexazinone, metribuzin, prometon, prometryn and simazine. As herbicides they may be used alone or in combination with other agents to increase weed control (Fishel, 2012).
    2) The chemical structure of these agents are heterocyclic, and composed of carbon and nitrogen in their rings. Triazine and triazine-related herbicides inhibit aliphatic amino acid synthesis in plants. This pathway does not exist in mammalian species, and this class of herbicides generally has a low degree of mammalian toxicity in animal studies. Product formulations of these herbicides can vary widely and are marketed in a wide variety of liquid and granular formulations (Fishel, 2012).
    3) A great variety of substituted triazine compounds (symmetrical and asymetrical) are now used for selective and non-selective vegetation control. Technical concentrates in organic solvents are sprayed as emulsions and suspensions. Triazines are incorporated into many herbicidal mixtures for special applications.

Life Support

    A) This overview assumes that basic life support measures have been instituted.

Clinical Effects

    0.2.1) SUMMARY OF EXPOSURE
    A) USES: Most triazine herbicides are used in selective weed control programs while others (ie, prometon) have nonselective properties. These agents have been available since the early 1950s. Members of this family include atrazine, hexazinone, metribuzin, prometon, prometryn and simazine. Cryomazine is an insect growth regulator and has been used in livestock, vegetable, and ornamental applications. These agents may be used alone or in combination with other herbicides.
    B) TOXICOLOGY: The chemical structure of these agents are heterocyclic, and composed of carbon and nitrogen in their rings. Triazine and triazine-related herbicides inhibit aliphatic amino acid synthesis in plants. This pathway does not exist in mammalian species, and this class of herbicides generally has a low degree of mammalian toxicity in animal studies. Product formulations of these herbicides can vary widely and are marketed in a wide variety of liquid and granular formulations.
    C) EPIDEMIOLOGY: Exposure has occurred but is uncommon.
    D) WITH POISONING/EXPOSURE
    1) OVERDOSE: Human overdose information is limited.
    2) CASE REPORTS: FATALITIES: Ingestion of an herbicide containing atrazine, aminotriazole, ethylene glycol and formaldehyde has been associated with coma, circulatory collapse, hepatic necrosis, renal failure, and disseminated intravascular coagulation. The patient died several days after exposure of circulatory collapse. In another case, a death was reported following ingestion of a mixture of amitrole and ammonium thiocyanate, with cyanosis, sweating, seizures, vomiting, diarrhea, hypotension, heart block, chest X-ray abnormalities, esophageal and gastric injury, and renal failure. However, the reported thiocyanate concentration was sufficient to account for the observed findings and the role of amitrole, if any, was not known. SURVIVAL: Ingestion of a triazine herbicide and alcohol produced vomiting and metabolic acidosis in an adult; the patient recovered with supportive care.
    3) INHALATION: A single case report suggests that lung injury may occur after inhalation of amitrole. It is not clear that there is a causal relationship in this isolated case report.
    4) OTHER: Ocular and skin irritation may occur following atrazine and triazole exposure. DERMAL: Atrazine is a skin sensitizer.
    5) ANIMAL DATA: When fed to sheep and cattle at high dosage, atrazine caused anorexia, salivation, depression of activity, muscle spasms and fasciculations, ataxia, increased body temperature and dyspnea. Hyperthyroidism and increased T3 levels with normal thyroxine and TSH levels were observed in animal studies. Atrazine appeared to interfere with hypothalamic control of pituitary-ovarian axis function in ovariectomized rats.
    0.2.3) VITAL SIGNS
    A) ANIMAL DATA: Increased body temperature has been reported in animal studies.
    0.2.4) HEENT
    A) Trizole and Atrazine may cause ocular irritation.
    0.2.20) REPRODUCTIVE
    A) Atrazine teratogenicity and embryotoxicity studies in rats and rabbits have produced mixed results.
    0.2.21) CARCINOGENICITY
    A) ACGIH lists atrazine in Category A4, "not classifiable as a human carcinogen" and amitrole in Category A3, "confirmed animal carcinogen with unknown relevance to humans." The EPA also listed atrazine as not likely to be carcinogenic in humans.

Laboratory Monitoring

    A) Monitor CBC in symptomatic patients.
    B) Monitor fluid status and electrolytes in patients that develop significant vomiting.
    C) Monitor renal function and liver enzymes following a large ingestion or in a symptomatic patient.
    D) Triazine herbicides can be measured in blood and urine by government, university, and industrial laboratories. However, these levels are not useful following an acute exposure.
    E) THYROID FUNCTION: Thyroid size and function should be evaluated following large acute exposures or long-term occupational exposures to amitrole. Daily administration of amitrole has been associated with thyroid enlargement in animal studies.

Treatment Overview

    0.4.2) ORAL/PARENTERAL EXPOSURE
    A) MANAGEMENT OF MIL TO MODERATE TOXICITY
    1) Limited overdose information. Product formulations of these herbicides can vary widely and a more toxic agent may be involved following an ingestion. Treatment is symptomatic and supportive. Vomiting may develop following ingestion. Monitor fluid status and electrolytes as indicated. Replace fluids (oral or IV) as necessary.
    B) MANAGEMENT OF SEVERE TOXICITY
    1) Treatment is symptomatic and supportive. Limited overdose information. Administer IV fluids for hypotension; add vasopressors if hypotension persists. Monitor mental status; drowsiness and CNS depression including coma may develop following a significant exposure. Assess airway and respiratory function frequently. Administer oxygen as needed; airway support and management as needed. A single case report exists of circulatory collapse including left ventricular failure, renal failure, hepatic necrosis, and disseminated intravascular coagulation following a mixed ingestion of atrazine, aminotriazole, ethylene glycol and formaldehyde. The patient died a few days later. In another case, a patient developed metabolic acidosis following the ingestion of prometryn and alcohol. Monitor ABGs as indicated following a significant ingestion.
    C) DECONTAMINATION
    1) PREHOSPITAL: INGESTION: A minor exposure to a triazine herbicide is generally NOT expected to result in significant toxicity. However, product formulations of these herbicides can vary widely and a more toxic agent may be involved. Do not induce emesis. Activated charcoal should only be considered if the patient is alert and not vomiting following a significant ingestion. Triazines can be moderately irritating to the skin, eyes, and respiratory tract. DERMAL: Remove contaminated clothing and wash exposed areas with soap and water. OCULAR: Irrigate exposed eyes thoroughly. INHALATION: Following an inhalational exposure, move patient to fresh air.
    2) HOSPITAL: INGESTION: Gastrointestinal decontamination is not recommended after ingestion unless a more toxic agent is also involved. DERMAL: Remove contaminated clothing and wash exposed skin with soap and water. OCULAR: Irrigate exposed eyes with water or 0.9% saline.
    D) AIRWAY MANAGEMENT
    1) Airway support is unlikely to be necessary after a minor or "taste" ingestion. Airway management may be necessary in patients who develop CNS depression or shock after a large ingestion.
    E) ANTIDOTE
    1) None.
    F) ENHANCED ELIMINATION
    1) Enhanced elimination is unlikely to be necessary in most cases of exposure. There is one report of a patient developing significant metabolic acidosis following the ingestion of prometryn and alcohol and he received hemodialysis. His underlying metabolic derangements did improve but hemodialysis had no affect on serum prometryn concentrations.
    G) PATIENT DISPOSITION
    1) HOME CRITERIA: Patients with no or minimal symptoms after inadvertent exposure may be observed at home.
    2) OBSERVATION CRITERIA: Symptomatic patients and those with deliberate exposure should be referred to a healthcare facility. Observe symptomatic patients until symptoms are resolved.
    3) ADMISSION CRITERIA: Patients with acidosis, coma, evidence of cardiovascular toxicity, or severe gastrointestinal symptoms should be admitted to the hospital.
    4) CONSULT CRITERIA: Consult a Poison Center or medical toxicologist for assistance in managing patients with severe toxicity or for whom diagnosis is unclear.
    H) PITFALLS
    1) Pitfalls include not evaluating for other coingestants such as solvents or surfactants, which may be ingredients included with the herbicide.
    0.4.3) INHALATION EXPOSURE
    A) 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.
    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) 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).

Range Of Toxicity

    A) TOXICITY: A toxic dose has not been established for these agents.
    B) Triazine herbicides are marketed in a wide variety of liquid and granular formulations which may contain other ingredients. NOTE: The TOXICITY of the formulated products may be determined mainly by ingredients other than the triazine herbicide. A poison control center or the product manufacturer SHOULD be contacted to obtain product-specific information in the event of serious clinical toxicity.
    C) LACK OF EFFECT: ATRAZINE: Ingestion of atrazine 800 mg in a child and 4 mg/kg in an adult resulted in no reported toxicity. ANIMAL DATA: Most triazines exhibit low systemic toxicity in laboratory rodents and farm animals.

Summary Of Exposure

    A) USES: Most triazine herbicides are used in selective weed control programs while others (ie, prometon) have nonselective properties. These agents have been available since the early 1950s. Members of this family include atrazine, hexazinone, metribuzin, prometon, prometryn and simazine. Cryomazine is an insect growth regulator and has been used in livestock, vegetable, and ornamental applications. These agents may be used alone or in combination with other herbicides.
    B) TOXICOLOGY: The chemical structure of these agents are heterocyclic, and composed of carbon and nitrogen in their rings. Triazine and triazine-related herbicides inhibit aliphatic amino acid synthesis in plants. This pathway does not exist in mammalian species, and this class of herbicides generally has a low degree of mammalian toxicity in animal studies. Product formulations of these herbicides can vary widely and are marketed in a wide variety of liquid and granular formulations.
    C) EPIDEMIOLOGY: Exposure has occurred but is uncommon.
    D) WITH POISONING/EXPOSURE
    1) OVERDOSE: Human overdose information is limited.
    2) CASE REPORTS: FATALITIES: Ingestion of an herbicide containing atrazine, aminotriazole, ethylene glycol and formaldehyde has been associated with coma, circulatory collapse, hepatic necrosis, renal failure, and disseminated intravascular coagulation. The patient died several days after exposure of circulatory collapse. In another case, a death was reported following ingestion of a mixture of amitrole and ammonium thiocyanate, with cyanosis, sweating, seizures, vomiting, diarrhea, hypotension, heart block, chest X-ray abnormalities, esophageal and gastric injury, and renal failure. However, the reported thiocyanate concentration was sufficient to account for the observed findings and the role of amitrole, if any, was not known. SURVIVAL: Ingestion of a triazine herbicide and alcohol produced vomiting and metabolic acidosis in an adult; the patient recovered with supportive care.
    3) INHALATION: A single case report suggests that lung injury may occur after inhalation of amitrole. It is not clear that there is a causal relationship in this isolated case report.
    4) OTHER: Ocular and skin irritation may occur following atrazine and triazole exposure. DERMAL: Atrazine is a skin sensitizer.
    5) ANIMAL DATA: When fed to sheep and cattle at high dosage, atrazine caused anorexia, salivation, depression of activity, muscle spasms and fasciculations, ataxia, increased body temperature and dyspnea. Hyperthyroidism and increased T3 levels with normal thyroxine and TSH levels were observed in animal studies. Atrazine appeared to interfere with hypothalamic control of pituitary-ovarian axis function in ovariectomized rats.

Vital Signs

    3.3.1) SUMMARY
    A) ANIMAL DATA: Increased body temperature has been reported in animal studies.
    3.3.3) TEMPERATURE
    A) ANIMAL DATA: Increased body temperature has been reported in animal studies (Palmer & Radeleff, 1964).

Heent

    3.4.1) SUMMARY
    A) Trizole and Atrazine may cause ocular irritation.
    3.4.3) EYES
    A) IRRITATION: Atrazine is mildly irritating to the eyes (Technical Information, 1987). Trizole has also caused ocular irritation (Hartley & Kidd, 1987).

Cardiovascular

    3.5.2) CLINICAL EFFECTS
    A) HYPOTENSIVE EPISODE
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/FATALITY: Circulatory collapse was reported in a 38-year-old man approximately 7 hours after an intentional ingestion of 500 mL of a herbicide containing a total of atrazine 100 mg, aminotriazole 25 g, ethylene glycol 25 g and formaldehyde 0.15 g. Despite aggressive decontamination measures, the circulatory collapse progressed to left ventricular failure, with the subsequent development of renal failure, hepatic necrosis and disseminated intravascular coagulation. The patient died from intractable shock approximately 3 days after the ingestion (Pommery et al, 1993).
    3.5.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) CARDIOMYOPATHY
    a) SIMAZINE: Necropsy on sheep who died following chronic ingestion of simazine showed moderate to acute myocardial degeneration (Allender & Glastonbury, 1992).

Respiratory

    3.6.2) CLINICAL EFFECTS
    A) DISORDER OF RESPIRATORY SYSTEM
    1) WITH POISONING/EXPOSURE
    a) AMITROLE: A single case report suggests that lung injury may occur after inhalation of amitrole (Baxter et al, 2000). It is not clear that there is a causal relationship in this isolated case report.
    3.6.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) DYSPNEA
    a) Dyspnea has been reported in animal studies (Palmer & Radeleff, 1964).

Neurologic

    3.7.2) CLINICAL EFFECTS
    A) COMA
    1) CASE REPORT/FATALITY: A 38-year-old man who ingested 500 mL of a herbicide containing atrazine, aminotriazole, ethylene glycol and formaldehyde presented with coma (GCS 7), circulatory collapse, metabolic acidosis and gastric bleeding 7 hours after ingestion. The patient gradually deteriorated and died 3 days later due to intractable shock (Pommery et al, 1993).
    B) DROWSY
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/PROMETRYN: Somnolence was reported in an adult following a 50 g ingestion of prometryn, a triazine herbicide. Following supportive care, the patient completely recovered (Brvar et al, 2008).
    C) SEIZURE
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/MIXED INGESTION: A death occurred following the ingestion of a mixture of amitrole and ammonium thiocyanate, with cyanosis, sweating, seizures, vomiting, diarrhea, hypotension, heart block, chest X-ray abnormalities, esophageal and gastric injury, and renal failure. However, the reported thiocyanate concentration was sufficient to account for the observed findings and the role of amitrole, if any, was not known (Baxter et al, 2000).
    3.7.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) TWITCHING
    a) Muscle spasms, fasciculations and ataxia have been reported in animal studies (Palmer & Radeleff, 1964).
    b) Generalized muscle tremors progressing to tetany and complete collapse of hind legs occurred in sheep that ingested an unknown quantity of simazine over a 2-week period. Death occurred 2 to 3 days after the appearance of clinical signs (Allender & Glastonbury, 1992).

Gastrointestinal

    3.8.2) CLINICAL EFFECTS
    A) VOMITING
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/PROMETRYN: Vomiting was an early symptom observed in an adult following an intentional ingestion of 50 g of prometryn, a triazine herbicide (Brvar et al, 2008).
    3.8.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) ANOREXIA
    a) Anorexia and salivation have been seen in animal studies (Palmer & Radeleff, 1964).

Hepatic

    3.9.2) CLINICAL EFFECTS
    A) HEPATIC NECROSIS
    1) MIXED INGESTION: Hepatic necrosis was reported in a 38-year-old man several hours after intentional ingestion of 500 mL of a herbicide containing atrazine, aminotriazole, ethylene glycol and formaldehyde (Pommery et al, 1993).
    3.9.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) LIVER FATTY
    a) SIMAZINE: Post-mortem findings of sheep that died following chronic ingestion of simazine showed congestion of the liver, with the histopathology revealing mild to moderate acute hepatic fatty changes. Simazine hepatic concentrations in necropsied sheep ranged from 0.19 to 1.89 mcg/gm (Allender & Glastonbury, 1992).

Genitourinary

    3.10.2) CLINICAL EFFECTS
    A) RENAL FAILURE SYNDROME
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/FATALITY: Renal failure was reported in a 38-year-old man several hours after intentional ingestion of 500 mL of an herbicide containing atrazine, aminotriazole, ethylene glycol and formaldehyde (Pommery et al, 1993).

Acid-Base

    3.11.2) CLINICAL EFFECTS
    A) METABOLIC ACIDOSIS
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/TRIAZINE: A 62-year-old man intentionally ingested approximately 50 g (100 mL) of Prohelan T (TM) (suspension concentrate of prometryn, a triazine herbicide) and an unknown amount of wine. Upon arrival the patient was somnolent and had vomited. Approximately 5 hours after ingestion, the patient became uncooperative with Kussmaul pattern breathing. ABGs (pH 7.24, bicarbonate 7.3 mmol/L, base excess -17.5, pCO2 17.5 mmHg and pO2 108.5 mmHg on room air) confirmed the presence of metabolic acidosis. The patient improved clinically and laboratory studies normalized following 4-hours of bicarbonate hemodialysis. However, serum prometryn concentration was not affected by hemodialysis and the authors suggested that serum concentrations did not correlate with clinical symptoms and hemodialysis was only useful in correcting the underlying metabolic derangements. The patient was discharged on hospital day 6 with no permanent sequelae (Brvar et al, 2008).

Hematologic

    3.13.2) CLINICAL EFFECTS
    A) DISSEMINATED INTRAVASCULAR COAGULATION
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT/FATALITY: Disseminated intravascular coagulation developed in a 38-year-old man several hours after intentionally ingesting 500 mL of an herbicide containing atrazine, aminotriazole, ethylene glycol and formaldehyde. The patient died of intractable shock approximately 3 days after ingestion (Pommery et al, 1993).

Dermatologic

    3.14.2) CLINICAL EFFECTS
    A) DERMATITIS
    1) WITH POISONING/EXPOSURE
    a) OCCUPATIONAL EXPOSURE: Although workers in some triazine manufacturing plants suffer skin irritation from exposure to the primary reactants, the finished triazines have not caused significant skin or mucous membrane irritation in regular handlers (Yelizarov, 1973).
    B) HYPERSENSITIVITY REACTION
    1) WITH POISONING/EXPOSURE
    a) Atrazine is a skin sensitizer (Technical Information, 1987; Stevens & Sumner, 1991).

Endocrine

    3.16.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) THYROID CARCINOMA
    a) RATS: Daily oral administration of amitrole (up to 50 ppm) to rats for 2 years was associated with the development of enlarged thyroids. Carcinoma of the thyroid was noted in rats receiving 100 ppm amitrole in their diet for 2 years (Jukes & Schaffer, 1960).
    b) DOGS: Daily oral administration of up to 12.5 mg/kg (500 ppm) of amitrole to dogs did not cause any effects (ACGIH, 1986).
    2) THYROID DISORDER
    a) Hyperthyroidism has been reported following exposure of rats to various members of the triazine family including metribuzin (Porter et al, 1993).
    b) Increased triiodothyronine (T3) levels with normal thyroxine and TSH levels were noted in reproductive studies of atrazine (Stoker et al, 2000). Atrazine induces thyroid histological changes in rats with dose-related increases in follicle-building thyroid cells, increasing follicular volume and decreasing nuclear volume (Kornilovskasya et al, 1996).
    3) ESTROGEN INCREASED
    a) Estrogenic activity has been reported for a variety of triazine herbicides and/or their metabolites, including simazine, atrazine and propazine (Hanioka et al, 1999).
    b) Atrazine was negative for estrogenic activity in reported gene-transfected human MCF-7 and HeLa cell lines (Balaguer et al, 1999).
    4) PITUITARY INSUFFICIENCY
    a) Atrazine seemed to interfere with hypothalamic control of pituitary-ovarian axis function in ovariectomized rats (Cooper et al, 2000). Decreased LH production seems to cause full-litter resorption in rats during the LH-dependent phase of pregnancy (Norotsky et al, 2001)
    5) ALTERED HORMONE LEVEL
    a) Atrazine, prometryne and deethyl-atrazine demonstrated inhibition of testosterone conversion to 5-alpha-dihydroxytestosterone and also inhibited binding of the latter compound to its receptor complex (Kniewald et al, 1995).
    b) In whole-animal (rat) studies, abnormalities of male reproductive development and suppression of testosterone production have been reported (Stoker et al, 2000; Trentacoste et al, 2001). . Decreased testosterone levels and male reproductive organ changes were seen at doses of 100 mg/kg/day and greater, but the authors suggest that the findings may be an effect of reduced food intake, as demonstrated by the production of similar effects in food intake restricted animals (Trentacoste et al, 2001).

Reproductive

    3.20.1) SUMMARY
    A) Atrazine teratogenicity and embryotoxicity studies in rats and rabbits have produced mixed results.
    3.20.2) TERATOGENICITY
    A) EMBRYOTOXICITY
    1) ATRAZINE: Dietary studies in rats receiving 100 ppm showed no teratogenicity. Embryotoxicity and fetotoxicity were absent at doses of less than 75 mg/kg/day in rats and 5 mg/kg in rabbits (Technical Information, 1987; Peters & Cook, 1973). Embryotoxic effects were seen at maternal doses of 800 to 2000 mg/kg (Peters & Cook, 1973).
    2) Infurna et al (1988) reported atrazine was not teratogenic at maternally toxic dose levels in rats (70 mg/kg/day on gestational days 6 to 15) and rabbits (75 mg/kg/day on gestational days 7 to 19).
    3) Full-litter resorption is seen following atrazine administration to rat dams during the LH-dependant luteal phase of pregnancy and seemed to be due to the loss of LH-dependent luteal function. Strain sensitivity varied considerably (Cummings et al, 2000; Narotsky et al, 2001).
    4) Additional reproductive studies reported in secondary sources:
    CompoundSpeciesResultReference
    Atrazinerat, rabbit-Schardein, 2000
    Cyanazinerat+/-EPA, 1990; Schardein, 2000
    Propazinerat-Schardein, 2000
    Simazinerat+/-Schardein, 2000
    TerbutrynRat, rabbit-EPA, 1990

    3.20.3) EFFECTS IN PREGNANCY
    A) ATRAZINE
    1) A study of 3510 births over a 1-year period found no clear association between maternal exposure to atrazine in drinking water and an increased risk of low birth weight or small-for-gestational-age infants. However, correlating with atrazine levels peaking from May to September, there was a slight increased risk of small-for-gestational-age status in those whose third trimester occurred partly or completely from May through September, compared with third trimesters that occurred at other times during the year. There was also a borderline significant increased risk of prematurity if the first trimester occurred from May to September (Villanueva et al, 2005).
    B) LACK OF EFFECT
    1) ATRAZINE
    a) In a systematic review of the literature, epidemiologic studies were identified that looked at the association between atrazine or related exposures and various pregnancy and birth outcomes. However, the poor quality of the data and lack of robust findings across all studies resulted in the inability to draw a causal link between atrazine and adverse pregnancy outcomes. Overall, the evidence was found to be inadequate and there was no consistency of findings across studies. The authors suggested that studies needed to focus on an individual-level assessment of exposure (Goodman et al, 2014).

Carcinogenicity

    3.21.2) SUMMARY/HUMAN
    A) ACGIH lists atrazine in Category A4, "not classifiable as a human carcinogen" and amitrole in Category A3, "confirmed animal carcinogen with unknown relevance to humans." The EPA also listed atrazine as not likely to be carcinogenic in humans.
    3.21.3) HUMAN STUDIES
    A) CARCINOMA
    1) ATRAZINE: ACGIH (2000) lists atrazine in Category A4, "not classifiable as a human carcinogen." IARC: Overall evaluation downgraded from 2B to 3 with supporting evidence from other data relevant to carcinogenicity and its mechanisms. The EPA listed atrazine as not likely to be carcinogenic in humans.
    2) AMITROLE: ACGIH (2000) lists amitrole in Category A3, "confirmed animal carcinogen with unknown relevance to humans." IARC lists it in Group 2B, "possibly carcinogenic to humans."
    B) OVARIAN CARCINOMA
    1) Donna et al (1989) reported women previously exposed to triazines showed a significant relative risk of 2.7 for ovarian neoplasms in a population-based case-referent study.
    2) Minder (1989) found the study flawed based on statistical aspects, possible confounders and biases, and the classification of the exposed women.
    3) A population-based case-controlled study of 256 women with ovarian cancer and 1122 controls found that cases were slightly but not significantly more likely to have been occupationally exposed to triazines compared with controls (adjusted OR=1.34; 95% CI=0.77 to 2.33). No evidence of a dose-response relationship was observed (Young et al, 2005).
    C) LACK OF EFFECT
    1) Loosli (1995) reviewed the available studies regarding atrazine, including the reports of ovarian cancer and associations with non-Hodgkin lymphoma and concluded that there was no convincing evidence of causation given the various flaws in these studies.
    2) Based on a systematic review of epidemiologic studies of atrazine exposure and risk of cancer, it is unlikely to pose a cancer risk. The review included studies that analyzed the association of atrazine exposure and multiple cancer sites (ie, ovaries, thyroid, hairy-cell leukemia, non-Hodgkin lymphoma, prostate, breast, esophageal and liver, and childhood cancers) (Boffetta et al, 2013).
    3) In a prospective study of 36,357 pesticide applicators that reported using atrazine, there was no increased overall cancer risk among workers applying atrazine (Freeman et al, 2011).
    4) Sathiakumar and Delzell (1997) and MacLennan et al (2003) found that pooled epidemiological data were inadequate to associate atrazine or triazines with many cancer types.
    5) In a nested case-control study, there was no association between atrazine exposure and prostate cancer (Hessel et al, 2004).
    3.21.4) ANIMAL STUDIES
    A) BREAST CARCINOMA
    1) Atrazine, cyanazine and simazine seem to cause prolactin-dependent mammary tumors in selected rat strains. This mechanism is not believed to have relevance to human breast cancer (O'Connor et al, 2000; Eldridge et al, 1999; Stevens et al, 1999).
    B) THYROID CARCINOMA
    1) RATS - Daily oral administration of amitrole (up to 50 ppm) to rats for 2 years was associated with the development of enlarged thyroids. Carcinoma of the thyroid was noted in rats receiving 100 ppm amitrole in the diet for 2 years (Jukes & Schaffer, 1960).

Genotoxicity

    A) Conflicting results have been obtained in various genetic tests for atrazine, and there is no consensus about its genotoxicity. The weight of evidence approach indicates that atrazine is not a genetic hazard.

Monitoring Parameters Levels

    4.1.1) SUMMARY
    A) Monitor CBC in symptomatic patients.
    B) Monitor fluid status and electrolytes in patients that develop significant vomiting.
    C) Monitor renal function and liver enzymes following a large ingestion or in a symptomatic patient.
    D) Triazine herbicides can be measured in blood and urine by government, university, and industrial laboratories. However, these levels are not useful following an acute exposure.
    E) THYROID FUNCTION: Thyroid size and function should be evaluated following large acute exposures or long-term occupational exposures to amitrole. Daily administration of amitrole has been associated with thyroid enlargement in animal studies.
    4.1.2) SERUM/BLOOD
    A) HEMATOLOGIC
    1) Monitor CBC in symptomatic patients.
    B) BLOOD/SERUM CHEMISTRY
    1) Monitor renal function and liver enzymes following a large ingestion or in a symptomatic patient.
    C) ENDOCRINE
    1) Daily administration of amitrole was associated with thyroid enlargement (ACGIH, 1986). Thyroid size and function should be evaluated following large acute exposures or long-term occupational exposures to amitrole.

Methods

    A) MULTIPLE ANALYTICAL METHODS
    1) The triazines can be measured in blood and urine by government, university, and industry laboratories. Methods include GLC, UV spectroscopy, TLC, and titrimetry (Clayton & Clayton, 1981).
    2) High-performance liquid chromatography was used to determine the concentration of atrazine in human post-mortem tissues, including liver, pancreas, small intestine, kidney, lung, and heart (Pommery et al, 1993).

Life Support

    A) Support respiratory and cardiovascular function.

Patient Disposition

    6.3.1) DISPOSITION/ORAL EXPOSURE
    6.3.1.1) ADMISSION CRITERIA/ORAL
    A) Patients with acidosis, coma, evidence of cardiovascular toxicity, or severe gastrointestinal symptoms should be admitted to the hospital.
    6.3.1.2) HOME CRITERIA/ORAL
    A) Patients with no or minimal symptoms after inadvertent exposure may be observed at home.
    6.3.1.3) CONSULT CRITERIA/ORAL
    A) Consult a Poison Center or medical toxicologist for assistance in managing patients with severe toxicity or for whom diagnosis is unclear.
    6.3.1.5) OBSERVATION CRITERIA/ORAL
    A) Symptomatic patients and those with deliberate exposure should be referred to a healthcare facility. Observe symptomatic patients until symptoms are resolved.

Monitoring

    A) Monitor CBC in symptomatic patients.
    B) Monitor fluid status and electrolytes in patients that develop significant vomiting.
    C) Monitor renal function and liver enzymes following a large ingestion or in a symptomatic patient.
    D) Triazine herbicides can be measured in blood and urine by government, university, and industrial laboratories. However, these levels are not useful following an acute exposure.
    E) THYROID FUNCTION: Thyroid size and function should be evaluated following large acute exposures or long-term occupational exposures to amitrole. Daily administration of amitrole has been associated with thyroid enlargement in animal studies.

Oral Exposure

    6.5.1) PREVENTION OF ABSORPTION/PREHOSPITAL
    A) SUMMARY
    1) INGESTION: A minor exposure to a triazine herbicide is generally NOT expected to result in significant toxicity. However, product formulations of these herbicides can vary widely and a more toxic agent may be involved. Do not induce emesis. Activated charcoal should only be considered if the patient is alert and not vomiting following a significant ingestion.
    2) Triazines can be moderately irritating to the skin, eyes, and respiratory tract. DERMAL: Remove contaminated clothing and wash exposed areas with soap and water. OCULAR: Irrigate exposed eyes thoroughly with copious amounts of water.
    B) ACTIVATED CHARCOAL
    1) PREHOSPITAL ACTIVATED CHARCOAL ADMINISTRATION
    a) Consider prehospital administration of activated charcoal as an aqueous slurry in patients with a potentially toxic ingestion who are awake and able to protect their airway. Activated charcoal is most effective when administered within one hour of ingestion. Administration in the prehospital setting has the potential to significantly decrease the time from toxin ingestion to activated charcoal administration, although it has not been shown to affect outcome (Alaspaa et al, 2005; Thakore & Murphy, 2002; Spiller & Rogers, 2002).
    1) In patients who are at risk for the abrupt onset of seizures or mental status depression, activated charcoal should not be administered in the prehospital setting, due to the risk of aspiration in the event of spontaneous emesis.
    2) The addition of flavoring agents (cola drinks, chocolate milk, cherry syrup) to activated charcoal improves the palatability for children and may facilitate successful administration (Guenther Skokan et al, 2001; Dagnone et al, 2002).
    2) CHARCOAL DOSE
    a) Use a minimum of 240 milliliters of water per 30 grams charcoal (FDA, 1985). Optimum dose not established; usual dose is 25 to 100 grams in adults and adolescents; 25 to 50 grams in children aged 1 to 12 years (or 0.5 to 1 gram/kilogram body weight) ; and 0.5 to 1 gram/kilogram in infants up to 1 year old (Chyka et al, 2005).
    1) Routine use of a cathartic with activated charcoal is NOT recommended as there is no evidence that cathartics reduce drug absorption and cathartics are known to cause adverse effects such as nausea, vomiting, abdominal cramps, electrolyte imbalances and occasionally hypotension (None Listed, 2004).
    b) ADVERSE EFFECTS/CONTRAINDICATIONS
    1) Complications: emesis, aspiration (Chyka et al, 2005). Aspiration may be complicated by acute respiratory failure, ARDS, bronchiolitis obliterans or chronic lung disease (Golej et al, 2001; Graff et al, 2002; Pollack et al, 1981; Harris & Filandrinos, 1993; Elliot et al, 1989; Rau et al, 1988; Golej et al, 2001; Graff et al, 2002). Refer to the ACTIVATED CHARCOAL/TREATMENT management for further information.
    2) Contraindications: unprotected airway (increases risk/severity of aspiration) , nonfunctioning gastrointestinal tract, uncontrolled vomiting, and ingestion of most hydrocarbons (Chyka et al, 2005).
    6.5.2) PREVENTION OF ABSORPTION
    A) SUMMARY
    1) If persons exposed to triazines exhibit symptoms of severe toxicosis, concurrent absorption of other or additional toxins should be considered.
    B) ACTIVATED CHARCOAL
    1) CHARCOAL ADMINISTRATION
    a) Consider administration of activated charcoal after a potentially toxic ingestion (Chyka et al, 2005). Administer charcoal as an aqueous slurry; most effective when administered within one hour of ingestion.
    2) CHARCOAL DOSE
    a) Use a minimum of 240 milliliters of water per 30 grams charcoal (FDA, 1985). Optimum dose not established; usual dose is 25 to 100 grams in adults and adolescents; 25 to 50 grams in children aged 1 to 12 years (or 0.5 to 1 gram/kilogram body weight) ; and 0.5 to 1 gram/kilogram in infants up to 1 year old (Chyka et al, 2005).
    1) Routine use of a cathartic with activated charcoal is NOT recommended as there is no evidence that cathartics reduce drug absorption and cathartics are known to cause adverse effects such as nausea, vomiting, abdominal cramps, electrolyte imbalances and occasionally hypotension (None Listed, 2004).
    b) ADVERSE EFFECTS/CONTRAINDICATIONS
    1) Complications: emesis, aspiration (Chyka et al, 2005). Aspiration may be complicated by acute respiratory failure, ARDS, bronchiolitis obliterans or chronic lung disease (Golej et al, 2001; Graff et al, 2002; Pollack et al, 1981; Harris & Filandrinos, 1993; Elliot et al, 1989; Rau et al, 1988; Golej et al, 2001; Graff et al, 2002). Refer to the ACTIVATED CHARCOAL/TREATMENT management for further information.
    2) Contraindications: unprotected airway (increases risk/severity of aspiration) , nonfunctioning gastrointestinal tract, uncontrolled vomiting, and ingestion of most hydrocarbons (Chyka et al, 2005).
    C) MULTIPLE DOSE ACTIVATED CHARCOAL
    1) ANIMAL DATA: Survival was enhanced in cattle receiving multiple-dose activated charcoal 4, 24, 48, and 72 hours after a lethal dose of atrazine (Kobel et al, 1985). There is no data regarding the use of multiple dose activated charcoal after human exposure to triazine herbicides and routine use is NOT recommended.
    6.5.3) TREATMENT
    A) SUPPORT
    1) MANAGEMENT OF MILD TO MODERATE TOXICITY
    a) Limited overdose information. Product formulations of these herbicides can vary widely and a more toxic agent may be involved following an ingestion. Treatment is symptomatic and supportive. Vomiting may develop following ingestion. Monitor fluid status and electrolytes as indicated. Replace fluids (oral or IV) as necessary.
    2) MANAGEMENT OF SEVERE TOXICITY
    a) Treatment is symptomatic and supportive. Limited overdose information. Administer IV fluids for hypotension; add vasopressors if hypotension persists. Monitor mental status; drowsiness and CNS depression including coma may develop following a significant exposure. Assess airway and respiratory function frequently. Administer oxygen as needed; airway support and management as needed. A single case report exists of circulatory collapse including left ventricular failure, renal failure, hepatic necrosis, and disseminated intravascular coagulation following a mixed ingestion of atrazine, aminotriazole, ethylene glycol and formaldehyde. The patient died a few days later. In another case, a patient developed metabolic acidosis following the ingestion of prometryn and alcohol. Monitor ABGs as indicated following a significant ingestion.
    B) MONITORING OF PATIENT
    1) Monitor vital signs and mental status.
    2) Monitor serum electrolytes in patients with severe gastrointestinal symptoms after a large or deliberate ingestion.
    3) Monitor CBC, renal function and liver enzymes following as necessary.
    4) Obtain an ECG and institute continuous cardiac monitoring after a large or deliberate ingestion.
    5) Monitor ABGs as indicated following a significant or mixed ingestion.
    6) Plasma concentrations of these herbicides are not readily available or clinically useful in guiding therapy.
    7) TRIAZOLE: Daily administration of amitrole was associated with thyroid enlargement (ACGIH, 1986). Thyroid size and function should be evaluated following large acute exposures or long-term occupational exposures to amitrole.
    C) HYPOTENSIVE EPISODE
    1) SUMMARY
    a) Infuse 10 to 20 milliliters/kilogram of isotonic fluid and keep the patient supine. If hypotension persists, administer dopamine or norepinephrine. Consider central venous pressure monitoring to guide further fluid therapy.
    2) DOPAMINE
    a) DOSE: Begin at 5 micrograms per kilogram per minute progressing in 5 micrograms per kilogram per minute increments as needed (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). If hypotension persists, dopamine may need to be discontinued and a more potent vasoconstrictor (eg, norepinephrine) should be considered (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    b) CAUTION: If ventricular dysrhythmias occur, decrease rate of administration (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). Extravasation may cause local tissue necrosis, administration through a central venous catheter is preferred (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    3) NOREPINEPHRINE
    a) PREPARATION: 4 milligrams (1 amp) added to 1000 milliliters of diluent provides a concentration of 4 micrograms/milliliter of norepinephrine base. Norepinephrine bitartrate should be mixed in dextrose solutions (dextrose 5% in water, dextrose 5% in saline) since dextrose-containing solutions protect against excessive oxidation and subsequent potency loss. Administration in saline alone is not recommended (Prod Info norepinephrine bitartrate injection, 2005).
    b) DOSE
    1) ADULT: Dose range: 0.1 to 0.5 microgram/kilogram/minute (eg, 70 kg adult 7 to 35 mcg/min); titrate to maintain adequate blood pressure (Peberdy et al, 2010).
    2) CHILD: Dose range: 0.1 to 2 micrograms/kilogram/minute; titrate to maintain adequate blood pressure (Kleinman et al, 2010).
    3) CAUTION: Extravasation may cause local tissue ischemia, administration by central venous catheter is advised (Peberdy et al, 2010).
    D) SEIZURE
    1) Seizure activity has NOT been reported following ingestion of a triazine herbicide alone; however, a mixed ingestion or other agents contained in a herbicide product may result in seizures.
    a) CASE REPORT: A death occurred after ingestion of a mixture of amitrole and ammonium thiocyanate, with cyanosis, sweating, seizures, vomiting, diarrhea, hypotension, heart block, chest X-ray abnormalities, esophageal and gastric injury, and renal failure. In this case, the thiocyanate concentration was sufficient to account for the observed clinical findings and the role of the amitrole, if any, was not known (Baxter et al, 2000).
    2) SUMMARY
    a) Attempt initial control with a benzodiazepine (eg, diazepam, lorazepam). If seizures persist or recur, administer phenobarbital or propofol.
    b) Monitor for respiratory depression, hypotension, and dysrhythmias. Endotracheal intubation should be performed in patients with persistent seizures.
    c) Evaluate for hypoxia, electrolyte disturbances, and hypoglycemia (or, if immediate bedside glucose testing is not available, treat with intravenous dextrose).
    3) DIAZEPAM
    a) ADULT DOSE: Initially 5 to 10 mg IV, OR 0.15 mg/kg IV up to 10 mg per dose up to a rate of 5 mg/minute; may be repeated every 5 to 20 minutes as needed (Brophy et al, 2012; Prod Info diazepam IM, IV injection, 2008; Manno, 2003).
    b) PEDIATRIC DOSE: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed (Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008).
    c) Monitor for hypotension, respiratory depression, and the need for endotracheal intubation. Consider a second agent if seizures persist or recur after repeated doses of diazepam .
    4) NO INTRAVENOUS ACCESS
    a) DIAZEPAM may be given rectally or intramuscularly (Manno, 2003). RECTAL DOSE: CHILD: Greater than 12 years: 0.2 mg/kg; 6 to 11 years: 0.3 mg/kg; 2 to 5 years: 0.5 mg/kg (Brophy et al, 2012).
    b) MIDAZOLAM has been used intramuscularly and intranasally, particularly in children when intravenous access has not been established. ADULT DOSE: 0.2 mg/kg IM, up to a maximum dose of 10 mg (Brophy et al, 2012). PEDIATRIC DOSE: INTRAMUSCULAR: 0.2 mg/kg IM, up to a maximum dose of 7 mg (Chamberlain et al, 1997) OR 10 mg IM (weight greater than 40 kg); 5 mg IM (weight 13 to 40 kg); INTRANASAL: 0.2 to 0.5 mg/kg up to a maximum of 10 mg/dose (Loddenkemper & Goodkin, 2011; Brophy et al, 2012). BUCCAL midazolam, 10 mg, has been used in adolescents and older children (5-years-old or more) to control seizures when intravenous access was not established (Scott et al, 1999).
    5) LORAZEPAM
    a) MAXIMUM RATE: The rate of intravenous administration of lorazepam should not exceed 2 mg/min (Brophy et al, 2012; Prod Info lorazepam IM, IV injection, 2008).
    b) ADULT DOSE: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist (Manno, 2003; Brophy et al, 2012).
    c) PEDIATRIC DOSE: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue (Brophy et al, 2012; Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008; Sreenath et al, 2009; Chin et al, 2008).
    6) PHENOBARBITAL
    a) ADULT LOADING DOSE: 20 mg/kg IV at an infusion rate of 50 to 100 mg/minute IV. An additional 5 to 10 mg/kg dose may be given 10 minutes after loading infusion if seizures persist or recur (Brophy et al, 2012).
    b) Patients receiving high doses will require endotracheal intubation and may require vasopressor support (Brophy et al, 2012).
    c) PEDIATRIC LOADING DOSE: 20 mg/kg may be given as single or divided application (2 mg/kg/minute in children weighing less than 40 kg up to 100 mg/min in children weighing greater than 40 kg). A plasma concentration of about 20 mg/L will be achieved by this dose (Loddenkemper & Goodkin, 2011).
    d) REPEAT PEDIATRIC DOSE: Repeat doses of 5 to 20 mg/kg may be given every 15 to 20 minutes if seizures persist, with cardiorespiratory monitoring (Loddenkemper & Goodkin, 2011).
    e) MONITOR: For hypotension, respiratory depression, and the need for endotracheal intubation (Loddenkemper & Goodkin, 2011; Manno, 2003).
    f) SERUM CONCENTRATION MONITORING: Monitor serum concentrations over the next 12 to 24 hours. Therapeutic serum concentrations of phenobarbital range from 10 to 40 mcg/mL, although the optimal plasma concentration for some individuals may vary outside this range (Hvidberg & Dam, 1976; Choonara & Rane, 1990; AMA Department of Drugs, 1992).
    7) OTHER AGENTS
    a) If seizures persist after phenobarbital, propofol or pentobarbital infusion, or neuromuscular paralysis with general anesthesia (isoflurane) and continuous EEG monitoring should be considered (Manno, 2003). Other anticonvulsants can be considered (eg, valproate sodium, levetiracetam, lacosamide, topiramate) if seizures persist or recur; however, there is very little data regarding their use in toxin induced seizures, controlled trials are not available to define the optimal dosage ranges for these agents in status epilepticus (Brophy et al, 2012):
    1) VALPROATE SODIUM: ADULT DOSE: An initial dose of 20 to 40 mg/kg IV, at a rate of 3 to 6 mg/kg/minute; may give an additional dose of 20 mg/kg 10 minutes after loading infusion. PEDIATRIC DOSE: 1.5 to 3 mg/kg/minute (Brophy et al, 2012).
    2) LEVETIRACETAM: ADULT DOSE: 1000 to 3000 mg IV, at a rate of 2 to 5 mg/kg/min IV. PEDIATRIC DOSE: 20 to 60 mg/kg IV (Brophy et al, 2012; Loddenkemper & Goodkin, 2011).
    3) LACOSAMIDE: ADULT DOSE: 200 to 400 mg IV; 200 mg IV over 15 minutes (Brophy et al, 2012). PEDIATRIC DOSE: In one study, median starting doses of 1.3 mg/kg/day and maintenance doses of 4.7 mg/kg/day were used in children 8 years and older (Loddenkemper & Goodkin, 2011).
    4) TOPIRAMATE: ADULT DOSE: 200 to 400 mg nasogastric/orally OR 300 to 1600 mg/day orally divided in 2 to 4 times daily (Brophy et al, 2012).

Inhalation Exposure

    6.7.1) DECONTAMINATION
    A) Move patient from the toxic environment to fresh air. Monitor for respiratory distress. If cough or difficulty in breathing develops, evaluate for hypoxia, respiratory tract irritation, bronchitis, or pneumonitis.
    B) OBSERVATION: Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
    C) INITIAL TREATMENT: Administer 100% humidified supplemental oxygen, perform endotracheal intubation and provide assisted ventilation as required. Administer inhaled beta-2 adrenergic agonists, if bronchospasm develops. Consider systemic corticosteroids in patients with significant bronchospasm (National Heart,Lung,and Blood Institute, 2007). Exposed skin and eyes should be flushed with copious amounts of water.

Eye Exposure

    6.8.1) DECONTAMINATION
    A) EYE IRRIGATION, ROUTINE: 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, an ophthalmologic examination should be performed (Peate, 2007; Naradzay & Barish, 2006).

Dermal Exposure

    6.9.1) DECONTAMINATION
    A) DERMAL DECONTAMINATION
    1) DECONTAMINATION: Remove contaminated clothing and wash exposed area thoroughly with soap and water for 10 to 15 minutes. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999).

Enhanced Elimination

    A) SUMMARY
    1) Enhanced elimination is unlikely to be necessary in most cases of exposure. There is one report of a patient developing significant metabolic acidosis following the ingestion of prometryn and alcohol and he received hemodialysis. His underlying metabolic derangements did improve but hemodialysis had no affect on serum prometryn concentrations.
    B) CASE REPORT
    1) PROMETRYIN: A 62-year-old man intentionally ingested approximately 50 g (100 mL) of Prohelan T (TM) (suspension concentrate of prometryn, a triazine herbicide) and an unknown amount of wine. Upon arrival the patient was somnolent and had vomited. Approximately 5 hours after ingestion, the patient became uncooperative with Kussmaul pattern breathing. ABGs (pH 7.24, bicarbonate 7.3 mmol/L, base excess -17.5, pCO2 17.5 mmHg and pO2 108.5 mmHg on room air) confirmed the presence of metabolic acidosis. The patient improved clinically and laboratory studies normalized following 4-hours of bicarbonate hemodialysis. However, his serum prometryn concentration was not affected by hemodialysis and the authors suggested that serum concentrations did not correlate with clinical symptoms and hemodialysis was only useful in correcting the underlying metabolic derangements. The patient was discharged on hospital day 6 with no permanent sequelae (Brvar et al, 2008).

Summary

    A) TOXICITY: A toxic dose has not been established for these agents.
    B) Triazine herbicides are marketed in a wide variety of liquid and granular formulations which may contain other ingredients. NOTE: The TOXICITY of the formulated products may be determined mainly by ingredients other than the triazine herbicide. A poison control center or the product manufacturer SHOULD be contacted to obtain product-specific information in the event of serious clinical toxicity.
    C) LACK OF EFFECT: ATRAZINE: Ingestion of atrazine 800 mg in a child and 4 mg/kg in an adult resulted in no reported toxicity. ANIMAL DATA: Most triazines exhibit low systemic toxicity in laboratory rodents and farm animals.

Minimum Lethal Exposure

    A) ATRAZINE
    1) A 38-year-old man intentionally ingested 500 mL of a herbicide containing a total of atrazine 100 g, aminotriazole 25 g, ethylene glycol 25 g and formaldehyde 0.15 g and subsequently developed circulatory collapse, coma, metabolic acidosis, gastric bleeding, renal failure, hepatic necrosis and disseminated intravascular coagulation. The patient died from intractable shock approximately 3 days after ingestion (Pommery et al, 1993).

Maximum Tolerated Exposure

    A) SPECIFIC SUBSTANCE
    1) AMITROLE
    a) A 39-year-old woman did not become ill following an ingestion of a mixture containing amitrole 20 mg/kg (Geldmacher-von Mallinckrodt & Schmidt, 1970).
    b) Threshold Dose: Very slight inhibition of (131)-iodine uptake by the thyroid for 24 hours in healthy people and people with hyperthyroidism was reported with 10 mg of amitrole (Astwood, 1960).
    c) ANIMAL DATA: The no-effect level (thyroid function) in RATS fed diets containing amitrole for 29 days is 0.5 part per million (ACGIH, 1986).
    2) ATRAZINE
    a) LACK OF EFFECT
    1) A farmer ingested 2 L of an aqueous formulation containing 50% atrazine and 5% ethylene glycol and developed evidence of severe ethylene glycol toxicity. However, there was no evidence of atrazine toxicity (Loosli, 1995).
    2) A woman gave her 6-year-old child and herself an undefined amount of 2 products (one containing atrazine and the other containing barium siliconfluoride). The woman developed significant barium toxicity but there was no evidence of atrazine poisoning, and the child did not develop any significant clinical events (Loosli, 1995).
    3) A farmer who ingested atrazine 4 mg/kg developed no signs or symptoms (Technical Information, 1972).
    4) A two-year-old child ingested 2 teaspoonfuls of 8% atrazine (approximately 800 mg) and developed no reported adverse effects (Technical Information, 1972).
    5) The acceptable dietary intake recommended by the World Health Organization is 0.0215 mg/kg/day (Technical Information, 1987).
    3) TRIAZINE
    a) CASE REPORT: A 62-year-old man intentionally ingested approximately 50 g (100 mL) of Prohelan T (TM) (suspension concentrate of prometryn, a triazine herbicide) and an unknown amount of wine. Upon arrival the patient was somnolent and had vomited. A few hours after presentation, the patient became uncooperative with Kussmaul pattern breathing. Metabolic acidosis was treated with bicarbonate hemodialysis. The patient also developed pneumonia during the course of his hospitalization. All laboratory and clinical findings improved and the patient was discharged on hospital day 6 with no permanent sequelae (Brvar et al, 2008).

Serum Plasma Blood Concentrations

    7.5.2) TOXIC CONCENTRATIONS
    A) TOXIC CONCENTRATION LEVELS
    1) SPECIFIC SUBSTANCE
    a) AMITROLE
    1) A 39-year-old woman had an unchanged amitrole concentration of 1,000 parts per million in the urine following ingestion of a mixture containing amitrole 20 milligrams/kilogram (Geldmacher-von Mallinckrodt & Schmidt, 1970).
    b) ATRAZINE
    1) A 38-year-old male intentionally ingested 500 milliliters of an herbicide containing atrazine 100 grams. He developed circulatory collapse, coma, renal failure and hepatic necrosis. Death, secondary to intractable shock, occurred approximately 3 days after ingestion. The plasma atrazine level was 1.49 micrograms/milliliter at the time of death (Pommery et al, 1993).
    c) TRIAZINE
    1) A 62-year-old man intentionally ingested 50 g (100 mL) of prometryn, a triazine herbicide, and had an initial serum concentration of 48.1 mg/L (2 hours after ingestion) and after hemodialysis the serum concentration was 67.7 mg/L (13 hours after ingestion). The authors concluded that serum concentrations do not correlate with clinical symptoms and that hemodialysis was ineffective in removing prometryn (Brvar et al, 2008). The patient fully recovered following hemodialysis and supportive care.

Toxicity Information

    7.7.1) TOXICITY VALUES
    A) LD50- (ORAL)RAT:
    1) Atrazine: 1780 mg/kg
    B) LD50- (ORAL)RAT:
    1) Cyromazine: 3387 mg/kg
    C) LD50- (SKIN)RAT:
    1) Hexazinone: 1690 mg/kg
    D) LD50- (SKIN)RAT:
    1) Metribuzin: Greater than 2000 mg/kg
    E) LD50- (SKIN)RAT:
    1) Prometon: 2980 mg/kg
    F) LD50- (SKIN)RAT:
    1) Prometryn: 5235 mg/kg
    G) LD50- (SKIN)RAT:
    1) Metribuzin: Greater than 2000 mg/kg
    H) LD50- (ORAL)RAT:
    1) Simazine: Greater than 5000 mg/kg
    I) LD50- (ORAL)MOUSE:
    1) 870 to 965 mg/kg
    J) LD50- (ORAL)RAT:
    1) 1110 to 1405 mg/kg
    K) LD50- (ORAL)RAT:
    1) 1465 to 2400 mg/kg
    L) LD50- (ORAL)MOUSE:
    1) 1750 mg/kg
    M) LD50- (ORAL)RAT:
    1) 1480 to 5100 mg/kg
    N) LD50- (ORAL)MOUSE:
    1) 380 mg/kg
    O) LD50- (ORAL)RAT:
    1) 149 to 334 mg/kg
    P) LD50- (ORAL)RAT:
    1) 1200 mg/kg
    Q) LD50- (ORAL)MOUSE:
    1) 700 mg/kg
    R) LD50- (ORAL)RAT:
    1) 1390 mg/kg
    S) LD50- (ORAL)RAT:
    1) 1690 mg/kg
    T) LD50- (SKIN)RAT:
    1) 5278 mg/kg
    U) LD50- (ORAL)MOUSE:
    1) > 2500 mg/kg
    V) LD50- (ORAL)RAT:
    1) > 10,000 mg/kg
    W) LD50- (SKIN)RAT:
    1) > 1000 mg/kg
    X) LD50- (ORAL)RAT:
    1) 1100 to 2300 mg/kg
    Y) LD50- (ORAL)MOUSE:
    1) 2160 mg/kg
    Z) LD50- (ORAL)RAT:
    1) 503 mg/kg
    2) 2980 mg/kg
    AA) LD50- (ORAL)MOUSE:
    1) 1330 mg/kg
    AB) LD50- (ORAL)RAT:
    1) 3750 mg/kg
    AC) LD50- (ORAL)MOUSE:
    1) 5000 mg/kg
    AD) LD50- (ORAL)RAT:
    1) > 5000 mg/kg
    AE) LD50- (ORAL)MOUSE:
    1) > 5000 mg/kg
    AF) LD50- (ORAL)RAT:
    1) > 5000 mg/kg
    AG) LD50- (ORAL)RAT:
    1) 2000 to 2160 mg/kg

Toxicologic Mechanism

    A) Laboratory animal studies and occupational exposure experience indicate triazines have low systemic toxicity.
    1) Following high chronic dosage in rats, some triazines cause growth retardation, slight leukopenia, and modification of liver metabolism (Clayton & Clayton, 1981).
    2) Extreme acute doses cause lung and brain edema, generalized hemorrhage, bronchopneumonia, nephrosis, and liver injury.
    B) Sheep and cattle exhibit neuromuscular disturbances.
    C) Although workers in some triazine manufacturing plants suffer skin irritation from exposure to the primary reactants, the finished triazines have not caused significant skin or mucous membrane irritation in regular handlers (Yelizarov, 1973).

Molecular Weight

    A) Ametryn: 227.33 (Hartley & Kidd, 1987)
    B) Atrazine: 215.69 (Hartley & Kidd, 1987)
    C) Cyanazine: 240.7 (Hartley & Kidd, 1987)
    D) Desmetryn: 213.31 (Hartley & Kidd, 1987)
    E) Hexazinone: 252.32 (Hartley & Kidd, 1987)
    F) Metribuzin: 214.29 (Hartley & Kidd, 1987)
    G) Prometon: 225.3 (Hartley & Kidd, 1987)
    H) Prometryn: 241.37 (Hartley & Kidd, 1987)
    I) Propazine: 229.7 (Hartley & Kidd, 1987)
    J) Simazine: 201.66 (Hartley & Kidd, 1987)
    K) Terbuthylazine: 229.72 (Hartley & Kidd, 1987)
    L) Terbutryn: 241.36 (Hartley & Kidd, 1987)

Clinical Effects

    11.1.2) BOVINE/CATTLE
    A) Extremely large amounts of these herbicides are required to produce toxicity. Normal exposure to forage sprayed at recommended rates of application causes no growth effects (Johnson et al, 1972). Under circumstances such as direct consumption of the triazine formulation, signs are hyperesthesia, moderate salivation, muscle tremors, weakness and ataxia, recumbency, and death.
    B) Initial clinical signs include salivation within 8 to 12 hours and scours, ataxia, and nervousness after 24 hours in treated animals. Untreated animals developed increased body temperature, increased respiratory rate, and scours after 12 hours. Ataxia, stiffness, and salivation preceded death within 48 to 72 hours (Kobel et al, 1985).
    11.1.3) CANINE/DOG
    A) Dogs who ate herbicide treated grass while exercising developed increased salivation, anorexia, and CNS depression. Subsequent symptoms were fever, seizures, hepatic damage, and renal damage (Campbell, 1992).

Treatment

    11.2.1) SUMMARY
    A) GENERAL TREATMENT
    1) Begin treatment immediately.
    2) Keep animal warm.
    3) Sample vomitus, blood, urine, and feces for analysis.
    4) If skin exposure has occurred, wash animal thoroughly with a mild detergent and flush with copious amounts of water.
    B) ANIMAL POISON CONTROL CENTERS
    1) ASPCA Animal Poison Control Center, An Allied Agency of the University of Illinois, 1717 S. Philo Rd, Suite 36, Urbana, IL 61802, website www.aspca.org/apcc
    2) It is an emergency telephone service which provides toxicology information to veterinarians, animal owners, universities, extension personnel and poison center staff for a fee. A veterinary toxicologist is available for consultation.
    3) The following 24-hour phone number is available: (888) 426-4435. A fee may apply. Please inquire with the poison center. The agency will make follow-up calls as needed in critical cases at no extra charge.
    11.2.4) DECONTAMINATION
    A) GASTRIC DECONTAMINATION
    1) SMALL ANIMALS
    a) Induce emesis with Syrup of Ipecac, 10 to 30 mL orally or hydrogen peroxide 5 to 25 mL orally repeated in 5 to 10 minutes if there is no response. DOGS ONLY may receive apomorphine 0.05 to 0.1 mg/kg IV, IM, or subcutaneously.
    b) Gastric lavage may be performed using tap water or normal saline.
    c) Administer activated charcoal, 5 to 50 g, orally, as a slurry in water.
    d) Then administer Milk of Magnesia 1 to 15 mL orally, mineral oil 2 to 15 mL orally, sodium sulfate 20%, 2 to 25 g orally or magnesium sulfate 20% 2 to 25 g orally, for catharsis.
    2) LARGE ANIMALS
    a) Repeated doses of activated charcoal, 454 g at 4, 24, 48, and 72 hours after a 400 mg dose of atrazine was effective in preventing lethality in cattle (Kobel et al, 1985).
    b) Give 250 to 500 g of activated charcoal in a water slurry, orally, to adsorb the toxic agent. Administer an oral cathartic: mineral oil (1 to 3 liters), 20% sodium sulfate (25 to 10,000 g), 20% magnesium sulfate (25 to 1,000 g), or Milk of Magnesia (20 to 30 mL).
    c) Ruminants (cattle and sheep) cannot be made to vomit. Horses should not be made to vomit.

Range Of Toxicity

    11.3.2) MINIMAL TOXIC DOSE
    A) CATTLE
    1) The lethal dose of atrazine in cattle has been reported to be 500 mg/kg within 24 hours. Single doses of 100 mg/kg have produced reversible intoxication (Palmer & Radeleff, 1964). Daily doses of 30 mg/kg for 25 days did not result in signs of toxicity (Johnson et al, 1972).
    B) RABBIT
    1) Daily oral doses of 75 mg/kg of atrazine given on gestational days 7 to 19 resulted in maternal toxicity (Infurna et al, 1988).
    C) RODENT
    1) RAT - Maternal toxicity was observed at daily oral doses of at least 70 mg/kg atrazine given on gestational days 6 to 15 (Infurna et al, 1988).

Continuing Care

    11.4.1) SUMMARY
    11.4.1.2) DECONTAMINATION/TREATMENT
    A) GENERAL TREATMENT
    1) Begin treatment immediately.
    2) Keep animal warm.
    3) Sample vomitus, blood, urine, and feces for analysis.
    4) If skin exposure has occurred, wash animal thoroughly with a mild detergent and flush with copious amounts of water.
    B) ANIMAL POISON CONTROL CENTERS
    1) ASPCA Animal Poison Control Center, An Allied Agency of the University of Illinois, 1717 S. Philo Rd, Suite 36, Urbana, IL 61802, website www.aspca.org/apcc
    2) It is an emergency telephone service which provides toxicology information to veterinarians, animal owners, universities, extension personnel and poison center staff for a fee. A veterinary toxicologist is available for consultation.
    3) The following 24-hour phone number is available: (888) 426-4435. A fee may apply. Please inquire with the poison center. The agency will make follow-up calls as needed in critical cases at no extra charge.
    11.4.2) DECONTAMINATION
    11.4.2.2) GASTRIC DECONTAMINATION
    A) GASTRIC DECONTAMINATION
    1) SMALL ANIMALS
    a) Induce emesis with Syrup of Ipecac, 10 to 30 mL orally or hydrogen peroxide 5 to 25 mL orally repeated in 5 to 10 minutes if there is no response. DOGS ONLY may receive apomorphine 0.05 to 0.1 mg/kg IV, IM, or subcutaneously.
    b) Gastric lavage may be performed using tap water or normal saline.
    c) Administer activated charcoal, 5 to 50 g, orally, as a slurry in water.
    d) Then administer Milk of Magnesia 1 to 15 mL orally, mineral oil 2 to 15 mL orally, sodium sulfate 20%, 2 to 25 g orally or magnesium sulfate 20% 2 to 25 g orally, for catharsis.
    2) LARGE ANIMALS
    a) Repeated doses of activated charcoal, 454 g at 4, 24, 48, and 72 hours after a 400 mg dose of atrazine was effective in preventing lethality in cattle (Kobel et al, 1985).
    b) Give 250 to 500 g of activated charcoal in a water slurry, orally, to adsorb the toxic agent. Administer an oral cathartic: mineral oil (1 to 3 liters), 20% sodium sulfate (25 to 10,000 g), 20% magnesium sulfate (25 to 1,000 g), or Milk of Magnesia (20 to 30 mL).
    c) Ruminants (cattle and sheep) cannot be made to vomit. Horses should not be made to vomit.

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