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EC number: 247-852-1 | CAS number: 26628-22-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Toxicity to terrestrial plants
Administrative data
- Endpoint:
- toxicity to terrestrial plants: short-term
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 004
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- GLP compliance:
- no
Test material
- Reference substance name:
- Sodium azide
- EC Number:
- 247-852-1
- EC Name:
- Sodium azide
- Cas Number:
- 26628-22-8
- Molecular formula:
- N3Na
- IUPAC Name:
- sodium azide
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
- Details on sampling:
- - Concentrations: 0, 50, 75, 100, 125, 150 lbs a.i. / acre.
which is equivalent to 0, 56, 84, 112, 140, 168 kg/ha.
Test substrate
- Vehicle:
- yes
Test organisms
- Species:
- other: Cyperus strigosus
- Plant group:
- Monocotyledonae (monocots)
- Details on test organisms:
- - Common name: false yellow nutsedge
- Plant family: Cyperaceae
Study design
- Test type:
- not specified
- Study type:
- field study
- Substrate type:
- natural soil
- Limit test:
- no
- Total exposure duration:
- 5 h
- Post exposure observation period:
- SEP 100 was applied in 3/4" (1.9 cm) water during a 5 hr period and this was followed 7 days later with an additional 1" (2.54 cm) of water to move the residual material deeper in the soil profile, and 1/2" (1.27 cm) one week later right before planting of cantaloupe on 4 July. The number of weeds per metre of bed was determined for each treatment 7 July.
Test conditions
- Test temperature:
- no data
- pH:
- 6.2
- Moisture:
- no data
- Nominal and measured concentrations:
- no data
- Reference substance (positive control):
- yes
- Remarks:
- methyl bromide, 350 lbs/acre (392 kg/ha)
Results and discussion
Effect concentrationsopen allclose all
- Species:
- other: Cyperus strigosus
- Duration:
- 5 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 50 lbs/acre
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- phytotoxicity
- Remarks on result:
- other: EC50 estimated by regression of data given in figure 1
- Species:
- other: Cyprerus strigosus
- Duration:
- 5 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 56 kg/ha
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- phytotoxicity
- Remarks on result:
- other: calculated from the above value of 50 lbs/acre
- Details on results:
- Applications of Sodium azide at all rates reduced weed populations. The relation between numbers of weed and Sodium azide dosage was best described by a negative exponential model with the greatest reductions in weed populations obtained with doses [D] in the range 50
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Executive summary:
The efficacy of Sodium azide for control of weeds was studied with field experiments in 2003. Sodium azide was delivered into soil by drip irrigation using the SEP 100R [American Pacific Corporation, Las Vegas, NV]. The compound was applied at rates within the range of 0 - 200 lbs a.i./acre (0 – 224 kg/ha) and methyl bromide [MB 67 - 33] was injected at 350 lbs/acre (392 kg/ha) to serve as positive control. The experiments were sited in fields naturally infested with severe nutsedge [Cyperus strigosus]. Effective weed control was obtained with rates of 75 lbs a.i./acre (84 kg/ha). Total and marketable yield increased significantly in response to rates of 50 and 75 lbs (56 and 84 kg/ha, respectively); however, there was no additional yield benefit obtained with the use of higher rates. Applications of Sodium azide at rates ≥100 lbs/acre (112 kg/ha) resulted in either no change or in gradual decline in yields with severe phytotoxicity observed for the two highest rates [175 & 200 lbs/acre (196 & 224 kg/ha)]. Control of root-knot, seedling and root diseases, and weeds with sodium azide at rates >75 lbs/acre (84 kg/ha) was equivalent to that obtained with methyl bromide. Results suggest that Sodium azide may be a good substitute for soil fumigation with methyl bromide in cantaloupe production.
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