plant growth regulator b nine daminozide 50% SP 92% SP 99% TC plant growth promoters

thiplant growth regulator b nine daminozide 50% SP 92% SP 99% TC plant growth promoters

NOMENCLATURE

Common name daminozide (BSI, E-ISO, (f) F-ISO, ANSI)

IUPAC name N-dimethylaminosuccinamic   

Chemical Abstracts name butanedioic  mono(2,2-dimethylhydrazide)  

Other names SADH  CAS RN [1596-84-5]  EEC no. 216-485-9  Development codes B-995  

PHYSICAL CHEMISTRY

Composition Tech. grade daminozide is >99% pure.  Mol. wt. 160.2  M.f. C6H12N2O3  Form Tech. is a white powder, with a faint amine-like odour.  M.p. 157-164   V.p. 22.7 mPa (23 )  KOW logP = -1.50 (pH 5, 7 and 9, 21 )  Solubility In distilled water 100 g/kg (25 ). In methanol 50,  25 (both in g/kg, 25 ). Insoluble in hydrocarbons.  Stability No measurable hydrolysis over 30 d at pH 5, 7 and 9. Hydrolysed by s and alkalis on heating. Solutions are slowly decomposed by light.  pKa 4.68 (20 )  

COMMERCIALISATION

History Plant growth regulator reported by J. A. Riddell et al. (Science, 1962, 136, 391). Introduced by Uniroyal Chemical Co., Inc. (now Crompton Corp.) in c. 1965.  Patents US 3240799; US 3334991  Manufacturers Agrowonderful cellphone 0086 17349771657

APPLICATIONS

Biochemistry Interferes with gibberellic  biosynthesis.  Mode of action Absorbed by the leaves, with translocation throughout the plant.  Uses To produce more compact plants (by inhibition of internodal elongation) of chrysanthemums, azaleas, hydrangeas, poinsettias, and other ornamentals. Applied at 0.106-0.425 kg/ha. Formulation types SP; WG.  Compatibility Incompatible with wetting agents, alkaline materials, oils, and copper-containing compounds.  Selected products: 'Alar' (Crompton); 'B-Nine' (Crompton)

OTHER PRODUCTS

'Dazide' (Fine) Discontinued products: 'Kylar' * (Uniroyal)

ANALYSIS

Product analysis by hplc. Details available from Crompton. Residues determined by glc of a derivative (J. R. Lane, Anal. Methods Pestic., Plant Growth Regul. Food Addit., 1967, 5, 499) or by alkaline hydrolysis to liberate 1,1-dimethylhydrazine which is determined colorimetrically (Anal. Methods Pestic. Plant Growth Regul., 1972, 6, 697; V. P. Lynch, ibid., 1976, 8, 491).  

MAMMALIAN TOXICOLOGY

Reviews FAO/WHO 62, 64 (see part 2 of the Bibliography).  Oral Acute oral LD50 for rats >5000 mg/kg.  Skin and eye Acute percutaneous LD50 for rabbits >5000 mg/kg.  Inhalation LC50 (4 h) for rats >2.1 mg/l air.  NOEL (1 y) for dogs 188 mg/kg b.w. daily, for rats 5 mg/kg b.w. daily. Non-oncogenic in 2 y feeding trials in rats and mice at 10 000 mg/kg diet. NOEL for teratogenicity and embryotoxicity in rabbits was 300 mg/kg diet. In 3-generation reproductive study, NOAEL for rats was 50 mg/kg b.w. daily. Non-mutagenic in in vivo test.  ADI (JMPR) 0.5 mg/kg b.w., for daminozide containing <30 mg 1,1-dimethylhydrazine/kg [1991].  Toxicity class WHO (a.i.) U; EPA (formulation) IV  EC classification R40: (the EC Working Group on Classification and Labelling of Dangerous Substances has proposed that this classification be deleted; it is expected that daminozide will be deleted from Annex I to 67/548/EEC with publication of the 29th ATP)  

ECOTOXICOLOGY

Birds Dietary LC50 (8 d) for mallard ducks and bobwhite quail >10 000 mg/kg diet.  Fish LC50 (96 h) for rainbow trout 149, bluegill sunfish 423 mg/l.  Daphnia LC50 (96 h) 76 mg/l.  Algae EC50 for Chlorella 180 ppm.  Bees Not toxic to bees; LD50 >100 mg/bee (85% formulation).  Worms LC50 for earthworms >632 ppm.  Other beneficial spp. In general, no or mild effects on insect parasites and predators and on predatory mites.  

ENVIRONMENTAL FATE

Animals Rapidly absorbed from the gastro-intestinal tract and widely and evenly distributed. Rapidly and completely metabolised and excreted through urine and faeces. No evidence of accumulation.  Plants Metabolites include 1,1-dimethylhydrazine.  Soil/Environment Daminozide quickly dissipates in soil with most residues becoming bound, with some CO2 formation. In aerobic soil, half of the daminozide is no longer recoverable after 17 h. No 1,1-dimethylhydrazine (UDMH) or N-nitrosodimethylamine were detected. In soil under anaerobic conditions, half of the daminozide had dissipated in 7.5 days. The major products were bound residues and CO2. In a field study on bare ground, about 90% of the daminozide had disappeared after 7 days. Neither hydrolysis nor photolysis are significant pathways for the degradation of daminozide.