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EC number: 213-911-5 | CAS number: 1066-33-7
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
The effect of ammonium sulfate solution on seed germination was studied for Avena sterilis spp macrocarpa Mo, in a 21 day test (Gonzalez Ponce and Salas, 1989). Seeds were wrapped with filter paper which was wetted with ammonium sulfate-solutions of 100 to 5000 mg/l. No significant increase in germination was found up to 2500 mg/l, compared with the control. An inhibitory effect was found at 5000 mg/l ammonium sulfate (=5980 mg/l Ammonium hydrogencarbonate) probably caused by a salt effect.
The effect of ammonium sulfate addition on the growth of the onion Allium cepa L. has been studied under laboratory conditions in 4 Canadian soils, in the presence of lime to raise the soil pH to approximately 6.5 (Abbés et al., 1995). After 84 days in a growth chamber, immature plants were harvested and fresh and dry weight of all plant parts were determined. Yield was greatest for 626 ammonium sulphate (= 749 mg ammonium hydrogencarbonate) / kg soil (calculated from 133 mg N / kg soil). An inhibitory effect was found at 1880 and 2506 ammonium sulphate (= 2250 and 3000 mg ammonium hydrogencarbonate) / kg soil (calculated from 399 and 532 mg N / kg soil), except for the sandy soil where only 2506 mg ammonium sulfate (=3000 Ammonium hydrogencarbonate) / kg soil was inhibitory. In general such observations could be explained by salt effects.
14 day old pinto bean plants (Phaseolus vulgaris L.) exposed to 26 mg/m3 ammonium sulfate aerosol for up to 320 hours (ca. 13 days) in an environmental growth chamber showed no changes in plant biomass or leaf area. However, visible foliar injury occurred, and both abaxial and adaxial leaf resistances were decreased from control values (Gmur, Evans and Cunningham, 1983). The ammonium sulfate application rate is stated to be about 2 orders of magnitude above ambient episode concentration.
The 6 year effect of ammonium sulfate spread as a solid fertilizer was investigated in a stand of trees (Picea abies, 12 years old at the beginning of the test) in southern Sweden (Rosengren-Brinck and Nihlgard, 1995). Spreading at 471 kg ammonium sulfate (= 564 kg Ammonium hydrogencarbonate, calculated from 100 kg N) per ha per year affected resistance to drought, which was evident in a reduction in the flushing of new shoots.
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