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EC number: 244-182-1 | CAS number: 21056-98-4
- 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: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Published paper with extensive description of methods and results.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 006
Materials and methods
- Principles of method if other than guideline:
- Studies on effect of fertiliser combinations
- GLP compliance:
- no
Test material
- Reference substance name:
- Potassium dihydrogen phosphite KH2PO3
- IUPAC Name:
- Potassium dihydrogen phosphite KH2PO3
- Test material form:
- other: solution
- Details on test material:
- 0.2% w/v solution
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- sampling of plant material
Study design
- Test type:
- other: biomass production
- Study type:
- extended laboratory study
- Substrate type:
- other: cleaned gravel sand amended with fertiliser
- Total exposure duration:
- 90 d
Test conditions
- Details on test conditions:
- Pot experiments carried out in Mitscherlich pots (columetric capacity 8 kg).
Cleaned gravel sand as substrate.
Three groups: 1: KH2PO4 added (1008 mg P per pot);
2. KH2PO3 added (1008 mgP per pot)
3. No P added
Alle other nutrients were adjusted for optimum supply.
12 replicates per treatment.
28 days after seeding, plant density was reduced to 4 plants per pot and group of 12 replicates was split into three soil/foliar fertilization treatments. KH2PO3 was applied in a 0.2% w/v solution. The solution was applied on the 3 youngest fully developed leaves by means of a paint brush. This was repeated 4 weeks later on the healthy growing plants. Plants were harvested after 90 days. Production of plant material was determined.
Results and discussion
Effect concentrations
- Species:
- Zea mays
- Duration:
- 90 d
- Dose descriptor:
- other: significant inhibition
- Effect conc.:
- 700 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- other: Phosphonic acid
- Basis for effect:
- other: growth and habitus
- Remarks on result:
- other: 1008 mg P added per pot of 8 kg wet weight. Assuming a water content of 20% (EUSES), this converts to 158 mg P per kg dry soil. MW Ratio H3PO3/P is 4.4. Thus the concentration in soil is estimated at circa 700 mg Phosphonic acid H3PO3 per kg dry soil.
Any other information on results incl. tables
Plants supplied with phosphite were smaller than control plants which did not receive any P-fertilisation.
Phosphite fertilised plants showed an abnormal habitus. They developed lateral tillers with brightened, malformed leaves.
When the nutritional status of the plant wast optimal, additional phosphite foliar fertilisation yield no effect.
However, in P-starved maize, foliar application of phosphite resulted in a lower yield (DM) as compared the control. Additional foliar application of K-phosphite (0.2% w/v solution) caused irreversible foliar injuries
Effect of different P-fertilisation treatments on the dry matter yield of maize (g DM)
Substrate P fertilisation |
Foliar P fertilisation |
||
|
Without |
Phosphate KH2PO4, 15 mg P in 0.2 w/v solution |
Phosphite KH2PO3, 15 mg P in 0.2 w/v solution |
|
Dry Plant Material [g/pot] |
||
Without |
9 b |
25 c |
4 a |
optimum P supply by KH2PO4 |
54 a |
59 b |
54 a |
optimum P supply by KH2PO3 |
4 b |
5 b |
1 a |
All values are means of 4 replicates. Means followed by dissimilar letters in rows are significantly different (Duncan's test, P = 0.05)
Phosphite was shown to be well absorbed by plant roots as well as through foliar absorption. Phosphite is obviously stable within the plant metabolism process as only small amounts appeared to be oxidised to phosphate.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Test with sufficient controls
- Conclusions:
- The reduced growth observed in phosphite treated plants was especially evident under conditions of P-deficiency. This could result from a suppression of the natural mechanisms of plants to respond to P-deficiency.
- Executive summary:
The efficiency of Potassium phosphite as P-source for maize plants has been studied in (among others) a pot experiment.
An inhibited growth was observed when phosphite was applied as the sole P-source (as compared to the control). The negatice effects ranged from a stunted growth of the plants to the complete die off. This effect was not observed or lower when phosphite was applied to maize under sufficient P-nutrition.
The detection of phosphite in the harvested maize plants also indicated that an oxidation to phosphate did not occur. Hence, Phosphite was not available to the plants as a P-source.
The concentration of phosphite in the soil was estimated at 700 mg (H3PO3) per kg soil dw.
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