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EC number: 205-622-8 | CAS number: 144-29-6
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption
- Remarks:
- adsorption
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Justification for type of information:
- Estimation Programs Interface Suite by US EPA
- Qualifier:
- according to guideline
- Guideline:
- other: Modeling database
- Principles of method if other than guideline:
- KOCWIN Program (v2.00).
- GLP compliance:
- not specified
- Type of method:
- other: Log Kow method
- Media:
- soil
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Piperazine citrate / tripiperazine dicitrate- Molecular formula: C12H30N6•Cl2H16O14 - Molecular weight: 642.76 g/mole - Substance type: Organic - Physical state: Solid
- Radiolabelling:
- not specified
- Test temperature:
- 25 deg C
- Analytical monitoring:
- not specified
- Key result
- Type:
- Koc
- Value:
- 16.3 L/kg
- Temp.:
- 25 °C
- Remarks on result:
- other: log Koc=1.212
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The Soil Adsorption Coefficient i.e Koc value of Piperazine Citrate was estimated using EPI suite KOCWIN Program (v2.00) program as Koc 16.3 L/kg (log Koc is 1.212) at 25 deg.C. This Koc value indicates that the substance Piperazine Citrate has a has a Negligible sorption to soil and sediment along with rapid migration potential to groundwater.
- Executive summary:
The Soil Adsorption Coefficient i.e Koc value of Piperazine Citrate was estimated using EPI suite KOCWIN Program (v2.00) program as Koc 16.3 L/kg (log Koc is 1.212) at 25 deg.C. This Koc value indicates that the substance Piperazine Citrate has a Negligible sorption to soil and sediment
along with rapid migration potential to groundwater.
Reference
Description of key information
The Soil Adsorption Coefficient i.e Koc value of Piperazine Citrate was estimated using EPI suite KOCWIN Program (v2.00) program as Koc 16.3 L/kg (log Koc is 1.212) at 25 deg.C. This Koc value indicates that the substance Piperazine Citrate has a has a Negligible sorption to soil and sediment along with rapid migration potential to groundwater.
Key value for chemical safety assessment
- Koc at 20 °C:
- 16.3
Additional information
Predicted data of adsorption endpoint for the target chemical Piperazine citrate (Cas no. 144-29-6) and studies fro its read across chemical were reviewed and are presented as weight of evidence approach below:
In key study, the Soil Adsorption Coefficient i.e Koc value of Piperazine Citrate was estimated using EPI suite KOCWIN Program (v2.00) program as Koc 16.3 L/kg (log Koc is 1.212) at 25 deg.C (EPI Suite, 2016). This Koc value indicates that the substance Piperazine Citrate has a Negligible sorption to soil and sediment along with rapid migration potential to groundwater.
From predicted model Danish (Q)SAR data base (database developed by the National Food Institute, Technical University of Denmark, with support from the Danish Environmental Protection Agency, the Nordic Council of Ministers and the European Chemicals Agency) indicate that the soil adsorption coefficient (Koc) value of Piperazine citrate is estimated to be 20.55/kg (log Koc =1.3128), indicating that it is has a Negligible sorption to soil and sediment and therefore have rapid migration potential to groundwater.
And read across Piperazine (Cas no. 110-85-0) experimental study from HSDB database;2016 indicate that the adsorption coefficient (Koc) of substance Piperazine was found to be 3.6 using a log Kow of 1.50 and a regression derived equation. This Koc value suggests that piperazine is expected to have very high mobility in soil.
Other study from European Union Risk Assessment Report – PIPERAZINE, 3rd Priority List Volume: 56; Final Report, 2005 for same read across (Cas no. 110-85-0) indicate that adsorption study which is performed with three different soils (loam, sand and sandy loam) using the batch equilibrium method (OECD Guidelines 106) (Geurts, 2003). The optimal soil solution ratio of 1:5 was used for the final sorption test. Equilibrium was reached after approximately 8 hours. During experiment the Kdvalues was found to be 7.9-20. This result indicate that sorption of piperazine to soil is not correlated to the organic carbon content of the soils. Thus study finally concluded that the not to adsorb to or partition into solids to any significant extent, but remained in the water phase.
Thus based on the above all studies and by applying weight of evidence approach it is concluded that the test substance Piperazine citrate (Cas no. 144-29-6) have Negligible sorption to soil/sediment means not adsorb in soil compartment thus very high mobility in soil.
[LogKoc: 1.212]
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