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CAS 50-65-7 Niclosamide 98% TC Clonitralid Hight Effect Niclosamide Olamine

Shanghai Molotus Chemical Co.,ltd

CAS 50-65-7 Niclosamide 98% TC Clonitralid Hight Effect Niclosamide Olamine

Brand Name : molotus

Model Number : niclosamide 98%TC

Place of Origin : china

MOQ : as demand

Payment Terms : Western Union, T/T, D/P, D/A, L/C

Delivery Time : 15-20 days for large package; 20-25 days for small package

Packaging Details : net 25kg in bag or drum or according to client’s requirement

item : niclosamide 98%TC

Solubility : In water 1.6 (pH 6.4)

Stability : Hydrolysed in aqueous solution

Form : Almost colourless crystals

content of Niclosamide : ≥98%

target : golden apple snail in rice

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Niclosamide 98% TC Clonitralid Hight Effect Niclosamide Olamine CAS 50-65-7



Common name niclosamide (BSI, E-ISO, (m) F-ISO, BAN, Germany (for veterinary use))

IUPAC name 2',5-dichloro-4'-nitrosalicylanilide

Chemical Abstracts name 5-chloro-N-(2-chloro-4-nitrophenyl)-2-hydroxybenzamide

CAS RN [50-65-7] Development codes Bayer 25 648; Bayer 73; SR 73


Common name niclosamide-olamine (BSI, E-ISO, (m) F-ISO, BAN); clonitralid (Germany, for public health use)

CAS RN [1420-04-8] Development codes SR73



Mol. wt. 327.1 M.f. C13H8Cl2N2O4 Form Almost colourless crystals. M.p. 230 V.p. <1 mPa (20) KOW logP = 1 (pH 9.6) Solubility In water 1.6 (pH 6.4), 110 (pH 9.1) (both in mg/l, 20). Soluble in common organic solvents such as ethanol and diethyl ether. Stability Hydrolysed in aqueous solution, DT50 (20) c. 7 d (pH 6.9), 18.8 d (pH 13.3). Stable to heat. Decomposes under u.v. irradiation. Hydrolysed by concentrated acid or alkali.


Mol. wt. 388.2 M.f. C15H15Cl2N3O5 Form Yellow, crystalline solid. M.p. Decomposes at 208 V.p. <<1 mPa (20) Solubility In water 0.1 g/l (20). In n-hexane, toluene <0.1, dichloromethane 0.015, isopropanol 0.25 (all in g/l, 20).


History Molluscicidal properties described by R. Gnert & E. Schraufstter (Proc. Int. Conf. Trop. Med. Malar., 1958, 2,5) and development discussed by R. Gnert et al. (Z. Naturforsch., Teil B, 1961, 16,95). The olamine salt introduced as a molluscicide by Bayer AG. Patents DE 1126374; US 3079297; US 3113067 Manufacturers Bayer CropScience


Mode of action Molluscicide with respiratory and stomach action. Uses Control of golden apple snail in rice. Control of schistosomiasis and fascioliasis in man by killing fresh-water snails which act as intermediate hosts. Also used for veterinary control of tapeworm infestations. Formulation types EC.


Compatibility Incompatible with acidic materials. Selected products: 'Bayluscide' (EC250) (Bayer CropScience) Formulation types WP.


Selected products: 'Bayluscide' (WP70) (Bayer CropScience); 'Trithin N' (Trithin)


Product analysis by redox titration (WHO Specifications Pesticides Used in Public Health, p. 309). Residues in water measured by colorimetry (R. Strufe, Pflanzenschutz-Nachr. (Engl. Ed.), 1962, 15, 42) or by titration (details from Bayer CropScience).



Oral Acute oral LD50 for rats ?000 mg/kg. Skin and eye Acute percutaneous LD50 for rats >1000 mg/kg (EC250). Strong eye irritant; skin reacts after repeated and long-lasting exposure (rabbits). Inhalation LC50 for rats (1 h) 20 mg/l air. NOEL (2 y) for male rats 2000, female rats 8000, mice 200 mg/kg diet; (1 y) for dogs 100 mg/kg b.w. ADI 3 mg/kg b.w. (proposed) Other No relevant mutagenic or embryotoxic effect. Toxicity class WHO (a.i.) U; EPA (formulation) II


Oral Acute oral LD50 for rats >5000 mg tech./kg. Skin and eye Acute percutaneous LD50 for rats >2000 mg (as 70% WP)/kg. Inhalation LC50 (4 ?1 h) 3630-8224 mg/m3 air (as 70% WP).



Birds LD50 for mallard ducks >500 mg/kg. Fish LC50 (96 h) for golden orfe 0.1 mg/l. Daphnia LC50 (48 h) 0.2 mg/l. Bees No significant mortality effects.


Animals Following oral administration, 14C-niclosamide was absorbed and metabolised in the rat. The major metabolite in the urine was the reduced compound 2',5-dichloro-4'-aminosalicylanilide ([10558-45-9]); several labile conjugates were also detected. The major constituent in the faeces was unchanged niclosamide, although considerable amounts of 2',5-dichloro-4'-aminosalicylanilide were also present; parent compound is present not only because of non-absorption, but also because of release from the biliary conjugate by b-glucuronidase of the intestinal microflora (L. A. Griffiths & V. Facchini, "The major metabolite of niclosamide: Identification by mass spectrometry" in Recent Developments in Mass Spectrometry in Biochemistry and Medicine, 2, 121-126 (1979)). Another study indicates that niclosamide is very poorly absorbed after dermal application. Radioactivity in the urine and faeces after application of 14C-niclosamide accounted for <2% and 10% of the labelled compound applied to pig and rat skin, respectively; c. 20% was recovered from the area of application (P. Brennan et al., "Dermal absorption of niclosamide in rats and minipigs" in Biopharmaceutics & Drug Disposition, Vol. 12, 547-556). Studies in fish with niclosamide and its 2-aminoethanol salt, indicate that niclosamide is rapidly excreted, as the glucuronide conjugate, and that there is little biomagnification; see D. P. Schultz & P. D. Harman, J. Agric. Food Chem., 26, 1226-1230 (1978); J. L. Allen et al., "Excretion of the Lampricide Bayer 73 by Rainbow Trout", Special Technical Publication, Philadelphia, 667, 52-61 (1979); and M. S. M. Marzouk, "Laboruntersuchungen an Karpfener Rkstde von Bayluscid und dessen Einwirkung auf das Karpfenblut", PhD Thesis, Univ. Munich, Germany (1981). Soil/Environment There was a rapid decline in niclosamide residues in paddy water; degradation followed pseudo-first order kinetics, DT50 0.3 d. At harvest, niclosamide residues were below the detection limit of 0.03 mg/kg in rice leaves, stalk and grain, indicating that the use of niclosamide as a molluscicide in rice production does not lead to persistent residues in the rice paddy ecosystem (S. M. F. Calumpang et al., Bull. Environ. Contam. Toxicol., 55, 494-501 (1995)). An aqueous solution of 14C-niclosamide was 95% degraded after 14 d exposure to long-wavelength u.v. light. No degradation occurred within 56 days either in buffered solution (pH 5.0, 6.9 and 8.7) or in pond water (initial pH 7.8) (D. P. Schultz & P. D. Harman, U.S. Fish and Wildlife Service: Investigations in Fish Control, 83, 1-5 (1978)).

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