122-14-5 Usage
Description
Fenitrothion is a selective acaricide and contact insecticide of low ovicidal properties. It is a brown to yellow liquid with a characteristic odour. Fenitrothion belongs to the organophosphate family of insecticides. It acts by inhibiting cholinesterase, thus it is an effective pesticide against a wide range of pests such as chewing, penetrating, and sucking insect pests.
Used in Agriculture:
Fenitrothion is used as an insecticide and acaricide for controlling sucking, chewing, and boring insects in cereals, soft fruit, tropical fruit, vines, sugar cane, vegetables, turf, and forestry. It is also used as a public health insecticide for the control of flies, cockroaches, and mosquitoes.
Used in Household and Public Health:
Fenitrothion is used as a residual contact spray for farms and public health programs to control flies, mosquitoes, and cockroaches. It is also effective against household insects and all nuisance insects listed by the World Health Organization.
Used in Malaria Vector Control:
Fenitrothion is used as a vector control agent for malaria, with its effectiveness confirmed by the World Health Organization.
Used in Various Forms:
Fenitrothion is available in various formulations such as dust, emulsifiable concentrate, flowable, fogging concentrate, granules, ULV, oil-based liquid spray, and wettable powder, making it compatible with other neutral insecticides.
History
Both Bayer Leverkusen and Sumitomo Chemical Company introduced Fenitrothion in 1959. Fenitrothion has minimal toxicity as compared to parathion, albeit with a range of insecticidal activity that is very similar. Fenitrothion is marketed in emulsifiable concentrate, dust, fogging concentrate, flowable, wettable powder formulations, and oil-based liquid spray.
Toxicity Effects
Acute Toxicity
Fenitrothion has acute toxicity to mammals, which is normally considered to be low. However, tests done on rats with doses considerably higher than those of applied for parathion reveal typical symptoms of acute poisoning. It also reduced the energy of birds in acute doses. Acute toxicity reported for a human female was a TDIo of 800 mg/kg.
Chronic Toxicity
In humans, chronic symptoms include fatigue, general malaise, headache, anorexia, and loss of memory, thirst, cramps, loss of weight, tremors, and muscular weakness. Half of the fenitrothion minimally effective dose changed the thyroid structure of a freshwater murrel.
Reactivity Profile
Organophosphates, such as Fenitrothion, are susceptible to formation of highly toxic and flammable phosphine gas in the presence of strong reducing agents such as hydrides. Partial oxidation by oxidizing agents may result in the release of toxic phosphorus oxides.
Hazard
Cholinesterase inhibitor, use may be
restricted.
Health Hazard
Fenitrothion is toxic to animals and humans. After prolonged periods of exposures to high concentrations of fenitrothion, occupational workers show poisoning. The symptoms include, but are not limited to, general malaise, fatigue, headache, loss of memory and ability to concentrate, anorexia, nausea, thirst, loss of weight, cramps, muscular weakness, and tremors, and at suffi ciently high dosage produce typical cholinergic poisoning. The formulation product, sumithion 50EC, causes delayed neurotoxicity in adult rats, as well as humans.
Health Hazard
Fenitrothion is an organophosphate insecticide. It is a highly toxic cholinesterase inhibitor, that acts on the nervous system. Does not cause delayed neurotoxicity and contact produces little irritation.
Fire Hazard
When heated to decomposition, Fenitrothion emits very toxic fumes of oxides of nitrogen, phosphorus and sulfur. Decomposition at 212-284F produces a mixture of organophosphorus polymers. Unstable in alkaline media. Stable for 2 years if stored at 68-77F. Do not store above 104F.
Flammability and Explosibility
Notclassified
Trade name
ACCOTHION?; ACEOTHION?; AGRIA
1050?; AGRIYA 1050?; AGROTHION?; AMERICAN
CYANAMID CL-47,300?; ARBOGAL?; BAY 41831?;
BAYER 41831?; BAYER S 5660?; CEKUTROTHION?;
CL 47300?; CP47114?; CYFEN?; CYTEL?;
CYTEN?; DICATHION?; DICOFEN?; DYBAR?;
EI 47300?; FALITHION?; FENITEX?; FENITOX?;
FENSTAN?; FOLETHION?; FOLITHION?; H-35-F
87 (BVM)?; 8057HC?; KALEIT?; KEEN SUPERKILL
ANT AND ROACH EXTERMINATOR?; KILLGERM
TETRACIDE INSECTICIDAL SPRAY?; KOTION?;
MEP (PESTICIDE)?; METATHION?; METATHIONE?;
METATION?; MICROMITE?; MONSANTO CP
47114?; NITROPHOS?; NOVATHION?; NUVAND?;
NUVANOL?; OLEOSUMIFENE?; OMS 43?;
OVADOFOS?; PENNWALT C-4852; PESTROY?; S
112A?; S 5660?; SMT?; SUMITHION?[C]; TURBAIR
GRAIN STORAGE INSECTICIDE?; VERTHION?
Safety Profile
Poison by ingestion,
inhalation, intravenous, and intraperitoneal
routes. Moderately toxic by skin contact,
intratracheal, and subcutaneous routes.
Human systemic effects: coma, diarrhea,
dyspnea, gastrointestinal changes,
hypermodtty, nausea or vomiting,
respiratory depression. Mutation data
reported. When heated to decomposition it
emits very toxic fumes of NOx, POx, and
sox
Potential Exposure
A potential danger to those involved
in the manufacture, formulation, and application of this
insecticide. It is a selective acaricide; and a contact and
stomach insecticide. Used to control chewing and sucking
insects on rice, orchard fruit; vegetables, cereals, cotton,
and in forests. Also protects against flies, mosquitoes, and
cockroaches
Metabolic pathway
Fenitrothion is a non-systemic insecticide, the biotransformations and
environmental fate of which have been intensively studied and reviewed.
Metabolism has been studied in mammals (including humans), birds,
fish, crustacea, molluscs, insects, algae, plants and soil. The major routes
of biotransformation involve desulfuration to the oxon analogue
(fenitrooxon) and hydrolysis to give dimethyl phosphate, O,O-dimethyl
phosphorothioate and 3-methyl-4-nitrophenol. Demethylation to give
desmethylfenitrothion and its decomposition products, reduction of
the nitro group and oxidation of the ring methyl group also
occur. Demethylation via glutathione-S-methyl transferases in the liver
is a particularly important mechanism in mammals. Reduction of
the nitro group to an amino group is important in anaerobic soils
and ruminants but this has also been shown to occur in rats, rabbits
and humans where it is presumably carried out by bacteria in the gut.
Oxidation of the 3-methyl group to hydroxymethyl and carboxylate
has been shown to be a degradative route in birds. The major routes of
phase II metabolism involve conjugation of 3-methyl-4-nitrophenol to the
glucoside in plants and insects, to the sulfate ester in birds and the sulfate
ester and glucuronide in mammals.
Metabolism
The main biotransformation routes involve oxidative
desulfuration to the oxon and dearylation to give
dimethyl hydrogen phosphate, O,O-dimethyl hydrogen
phosphorothioate and 3-methyl-4-nitrophenol. Demethylation
dependent on glutathion-S-alkyl transferase is particularly
important in mammals.Oxidation of the 3-methyl
group to hydroxymethyl and then carboxyl group is also
a degradative route. Reduction of the nitro group to an
amino group occurs in anaerobic soils and ruminants. The
DT50 in soils under upland and submerged conditions were
12–28 and 4–20 d, respectively.
Shipping
UN3017 Organophosphorus pesticides, liquid,
toxic, flammable, flash point not ,23C, Hazard class: 6.1;
Labels: 6.1-Poisonous materials, 3-Flammable liquid.
UN2810 Toxic liquids, organic, n.o.s., Hazard Class: 6.1;
Labels: 6.1-Poisonous materials, Technical Name Required
Toxicity evaluation
The acute oral LD50 values in mammals
range from 330 mg/kg in rats to 1850 mg/kg in the guineapig.
Inhalation LC50 (4 h) for rats is >1.2 mg/L air. NOEL
(2 y) for rats and mice is 10 mg/kg diet (0.5 mg/kg/d). ADI
is 5 μg/kg b.w.
Degradation
Fenitrothion is relatively stable to hydrolysis under normal conditions
(PM). Mikami et al. (1985) reported the hydrolysis of fenitrothion between
pH 5 and 10. Below pH 7 hydrolysis occurred by a pH-independent
mechanism and above pH 9 by a base-catalysed process. At intermediate
pH values both mechanisms were operative. The major mechanism below
pH 8 was demethylation to give desmethylfenitrothion and above
pH 9, cleavage of the P-O-aryl bond gave 3-methyl-4-nitrophenol.
Incompatibilities
Incompatible with oxidizers (chlorates,
nitrates, peroxides, permanganates, perchlorates, chlorine,
bromine, fluorine, etc.); contact may cause fires or explosions. Keep away from alkaline materials, strong bases,strong acids, oxoacids, epoxides. Strong oxidizers may cause
release of toxic phosphorus oxides. Organophosphates, in the
presence of strong reducing agents such as hydrides, may
form highly toxic and flammable phosphine gas. Keep away
from alkaline materials
Waste Disposal
Incineration (for large
amounts); alkaline hydrolysis and landfill (for small
amounts). In accordance with 40CFR165, follow recommendations for the disposal of pesticides and pesticide containers. Must be disposed properly by following package label
directions or by contacting your local or federal environmental
control agency, or by contacting your regional EPA office.
Check Digit Verification of cas no
The CAS Registry Mumber 122-14-5 includes 6 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 3 digits, 1,2 and 2 respectively; the second part has 2 digits, 1 and 4 respectively.
Calculate Digit Verification of CAS Registry Number 122-14:
(5*1)+(4*2)+(3*2)+(2*1)+(1*4)=25
25 % 10 = 5
So 122-14-5 is a valid CAS Registry Number.
InChI:InChI=1/C9H12NO5PS/c1-7-6-8(4-5-9(7)10(11)12)17-16(13,14-2)15-3/h4-6H,1-3H3
122-14-5Relevant articles and documents
31P NMR and ESI-MS study of fenitrothion-copper ion complex: Experimental and theoretical study
Choi, Hojune,Yang, Kiyull,Park, Jong Keun,Koo, In Sun
experimental part, p. 1339 - 1342 (2010/09/10)
31P NMR and ESI-MS studies of Cu2+ binding to Fenitrothion (FN) were performed by experimentally and theoretically. The calculated 31P NMR chemical shifts for FN-Cu2+ complexes are in good agreement with experim
Oil-in-water emulsions
-
, (2008/06/13)
The present invention relates to oil-in-water emulsions containing 0.001-70% by weight of at least one active substance from the group consisting of phosphates, thiophosphates and/or carbamates, 0.001-30% by weight of one or more surfactant compounds from the group consisting of nonionic surfactant compounds or phosphorylated surfactant compounds or sulfated surfactant compounds or sulfonated surfactant compounds, and also, if desired, adjuvants, and, water to make up 100% by weight.
Unequivocal Identification of Compounds Formed in the Photodegradation of Fenitrothion in Water/Methanol and Proposal of Selected Transformation Pathways
Durand, G.,Abad, J. L.,Sanchez-Baeza, F.,Messeguer, A.,Barcelo, D.
, p. 814 - 821 (2007/10/02)
The photodegradation of fenitrothion was examined in a mixture of distilled water/methanol (5:1).The UV irradiation was carried out with a high-pressure Hg lamp during 7 h.For the identification of further breakdown products, fenitrooxon and carboxyfenitrothion were also irradiated under experimental conditions identical to those for fenitrothion.The identification of the breakdown products formed was carried out by gas chromatography-mass spectrometry (GC-MS) with electron impact (EI) and comparison with authentic standards synthesized in the laboratory.A total of 21 photoproducts of oxidation, isomerization, denitration, and solvolysis that may be of concern in environmental studies were unequivocally identified.Among them were formyldenitrofenitrothion, carbomethoxydenitrofenitrooxon. and hydroxymethyldenitrofenitrooxon.A proposed mechanism of the process is presented.Selected pathways for the photodegradation of fenitrothion were examined: (i) degradation through hydrolysis, with eventual remethylation; (ii) P=S to P=O oxidation; (iii) denitration; and (iv) oxidation of the methyl substituent through hydroxymethyl and formyl to give the corresponding carboxy derivatives.