Pyridaphenthion Chemical Properties

Melting point:

54.5～56.5℃

Boiling point:

416.2±28.0 °C(Predicted)

Density 

1.30±0.1 g/cm3(Predicted)

vapor pressure 

1.47×10^-6 Pa (20 °C)

Flash point:

-4 °C

storage temp. 

APPROX 4°C

Water Solubility 

100mg l^-1 （20°C）

pka

-2.09±0.40(Predicted)

BRN 

302741

CAS DataBase Reference

119-12-0(CAS DataBase Reference)

NIST Chemistry Reference

Phosphorothioic acid, o-(1,6-dihydro-6-oxo-1-phenyl-3-pyridazinyl) o,o-diethyl ester(119-12-0)

EPA Substance Registry System

Pyridaphenthion (119-12-0)

Safety Information

Hazard Codes 

F,Xi,N,Xn

Risk Statements 

11-36-66-67-57-51/53-20/22

Safety Statements 

26-61-33-16

RIDADR 

2783

WGK Germany 

3

RTECS 

TF2275000

HazardClass 

6.1(a)

PackingGroup 

II

Pyridaphenthion Usage And Synthesis

Description

Pyridaphenthion is a pale yellow solid, mp 54.5–56 ?C, vp 0.00147 mPa (20 ?C). Solubility in water is 100 mg/L (20 ?C). It is very soluble in acetone, methanol, and diethyl ether. Log Kow = 3.2.

Uses

Pyridaphenthion is used to control a wide range of chewing and sucking insects and mites in rice, vegetables, fruit and ornamentals.

Definition

ChEBI: Pyridaphenthion is an organic thiophosphate, an organothiophosphate insecticide and a pyridazinone. It has a role as an EC 3.1.1.7 (acetylcholinesterase) inhibitor and an agrochemical. It is functionally related to a 6-hydroxy-2-phenylpyridazin-3-one.

Safety Profile

Poison by intraperitoneal route. Moderately toxic by ingestion and skin contact. When heated to decomposition it emits very toxic fumes of SOx, POx, and NOx. Used to control chewing and suckmg insects on rice, fruits, vegetables, and cereals.

Metabolic pathway

Pyridaphentluon is photolytically transformed into the oxon and phenylmaleic hydrazide. In the mouse its metabolism involves oxidative dearylation, oxidative desulfuration to the oxon, de-ethylation and conjugation of phenylmaleic hydrazide produced as the ultimate product of stage I metabolism and is typical of many phosphorothioates. A marked difference between metabolism in mice and rats was shown, with rats excreting no desethylpyridaphenthion and excreting all of the phenyl-maleic hydrazide in an unconjugated form.

Metabolism

More than 70% of the dose administered to rats and mice was excreted within 24 h in the urine. The major metabolites excreted are phenylmaleic hydrazide and desethyl pyridafenthion-oxon. The half-life in soil is 11–24 d.

Degradation

The photolysis of pyridaphenthion on a glass slide irradiated with both short wavelength UV light and light of wavelength >300 nm was investigated by Tsao et al. (1989). Samples were irradiated for 48 hours at unrecorded light intensity as thin films spread on petri dishes or in solution in water, methanol or hexane under an oxygen atmosphere. The effects of photosensitisers was also assessed in the thin film experiments. The photoproducts were analysed by TLC, GC-MS and ¹H NMR spectroscopy. Under thin film conditions pyridaphenthion was photodegraded more quickly with light >300 nm than by 254 um light and was degraded faster as a thin film than in solution. The main photoproducts from the glass surface and aqueous solution were pyridaphenthion oxon (2) and phenylmaleic hydrazide (3) (Scheme 1); the only other products were small amounts of polymers. Photosensitisers accelerated photolysis markedly with the most effective being a plant-derived natural product, cis-dehydromatricaria ester. It is notable that a simple chemical oxidation using 3-chloroperoxybenzoic acid gave the same two products, 2 and 3.

Toxicity evaluation

The acute oral LD₅₀ for rats is 769–850 mg/kg. Inhalation LC50 (4 h) for rats is >1.13 mg/L air.

Pyridaphenthion(119-12-0)Related Product Information

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