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EC number: 235-227-6 | CAS number: 12136-45-7
- 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
Endpoint summary
Administrative data
Description of key information
Oral repeated dose toxicity
Potassium chloride (KCl) is the most common source of Potassium oxide (K2O). Therefore, the health effects of potassium chloride need to be considered in the assessment of Potassium oxide
Groups of male F344/Slc rats received 110, 450, 1820 mg/kg bw/day of KCl in feed over a period of 2 years and were observed for clinical signs and mortality and were examined for gross and histopathological changes at the end of the treatment period (Imai 1961) The NOAEL was set 1820 mg/kg bw/day since nephritis was reported in all treatment groups as well as in the control group. With respect to the observed gastritis which is regarded to be a local effect a LOAEL(local) of 110 mg/kg bw/d was determined (Imai 1961, UNEP 2003).
NOAEL -1820 mg/kg bw/day
Dermal repeated dose toxicity
There are no dermal repeated studies available.
For dermal exposure we taken that:
-the average weight of rats is 250g (200-300g),
-the dose is applied over an area which is approximately 10% of the total body surface=0.025 kg
corrected dermal NOAEL= oral NOAEL
1820 mg/kg bw/day x 0.025 kg =
NOAELrat = 45.5 mg/kg bw/day
Inhalation repeated dose toxicity
There are no Inhalation Repeated studies available.
The oral dose for the rat is converted to the corresponding air concentration using a standard breathing volume for the rat (1.15 m3/kg for 24 hours exposure. The resulting air concentration needs to be additionally corrected for 24 hlight activity (20 m3), assuming 100 % absorption for both routes.
NOAEL rat
1820 mg/kg bw/day
÷1.15 m3/kgbw
÷20m3/rat
NOAECrat 79.13 mg/m3
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- chronic toxicity: oral
- Type of information:
- other: Published data
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Principles of method if other than guideline:
- Groups of male F344/Slc rats received different doses of KCl in feed over a period of 2 years and were observed for clinical signs and mortality and were examined for gross and histopathological changes at the end of the treatment period
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- other: F344/Slc
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- no data to be identified because only abstract available
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- Groups of male F344/Slc rats received different doses of KCl in feed over a period of 2 years
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 2 years
- Frequency of treatment:
- daily
- Remarks:
- Doses / Concentrations:
0, 0.25, 1, 5 % in diet (corresponding to 0, 110, 450, 1820 mg/kg bw/day
Basis:
nominal in diet - No. of animals per sex per dose:
- 50
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Groups of male F344/Slc rats received different doses of KCl in feed over a period of 2 years and were observed for clinical signs and mortality and were examined for gross and histopathological changes at the end of the treatment period
- Positive control:
- no
- Observations and examinations performed and frequency:
- survival, food consumption, blood pressure, body weight development
urinalysis: protein, glucose, keton, bilirubin, urobilinogen, pH
hematology: RBC, HB, Ht, MCV, HCH, MCHC, Pt, WBC
biochemical analysis: GOT, GPT, ALP, LDH, Ch-E, Na, K, Cl, Nu, Clu, Tp, Glu - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
absolue and relative organ weight: brain, pituitary, thymus, heart, right and leftlungs, linver, spleen, pancreas, right and left kidneys, right and leftadernals. right and left testes, seminal vesicles, prostrate
HISTOPATHOLOGY: Yes
heart, lung, liver, kidney, stomach, aorta
(grading of nephrosis +, ++, +++) - Other examinations:
- no data
- Statistics:
- no data
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Details on results:
- MORTALITY:
after termination of the 2 year treatment period_
110, 450, 1820 mg/kg bw/day versus control:
18/50, 21/50, 8/50 versus 26/50
survival rate:
32/50, 29/50, 42/50 versus 24/50
HISTOPATHOLOGY: NON-NEOPLASTIC
KIDNEYS. nephritis
110, 450, 1820 mg/kg bw/day versus control:
32/32, 29/29, 42/42 versus 24/24
grading:
110 mg/kg: 23/32: +; 6/32: ++; 3/32: +++
450 mg/kg: 11/29:+; 6/29: ++; 12/29: +++;
1820 mg/kg: 28/42: +; 13/42: ++; 1/42: +++
control: 14/24: +; 6/24: ++; 4/24: +++
STOMACH.:
110, 450, 1820 mg/kg bw/day versus control:
gastritis
18/32, 18/29; 30/42 versus 6/24
ulcer
0/32, 2/29 , 2/42 versus 0/24
HISTOPATHOLOGY: NEOPLASTIC (if applicable)
HISTORICAL CONTROL DATA (if applicable)
In tumerous lesions, testicular tumor developed with a high incidence in all groups and the incidence of pheochromocytoma in the adrenals was moderately high in all groups.
However the incidence and type of tumour in experimental and control group were comparable to those of spontaneous tumours in F344/Slc rats (data not shown). Therefore the tumours observed in this study were thought to be spontaneous in origin
OTHER FINDINGS - Dose descriptor:
- NOAEL
- Effect level:
- ca. 1 820 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: The high mortality in all groups including controls (>50%) . nephritits was reported in all treatment groups as well as in the control group (UNEP 2003)
- Dose descriptor:
- LOAEL
- Remarks:
- local
- Effect level:
- ca. 110 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: With respect to gastritis which is regarded to be a local effect; UNEP 2003
- Critical effects observed:
- not specified
- Conclusions:
- Groups of male F344/Slc rats received 110, 450, 1820 mg/kg bw/day of KCl in feed over a period of 2 years and were observed for clinical signs and mortality and were examined for gross and histopathological changes at the end of the treatment period (Imai 1961) The NOAEL was set 1820 mg/kg bw/day since nephritis was reported in all treatment groups as well as in the control group. With respect to the observed gastritis which is regarded to be a local effect a LOAEL(local) of 110 mg/kg bw/d was determined (Imai 1961, UNEP 2003).
- Executive summary:
Groups of male F344/Slc rats received 110, 450, 1820 mg/kg bw/day of KCl in feed over a period of 2 years and were observed for clinical signs and mortality and were examined for gross and histopathological changes at the end of the treatment period (Imai 1961) The NOAEL was set 1820 mg/kg bw/day since nephritis was reported in all treatment groups as well as in the control group. With respect to the observed gastritis which is regarded to be a local effect a LOAEL(local) of 110 mg/kg bw/d was determined (Imai 1961, UNEP 2003).
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 820 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
Repeated dose toxicity: inhalation - systemic effects
Link to relevant study records
- Endpoint:
- chronic toxicity: inhalation
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Critical effects observed:
- not specified
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEC
- 79.13 mg/m³
- Study duration:
- chronic
- Species:
- rat
- Quality of whole database:
- Inhalation exposure:
The oral dose for the rat is converted to the corresponding air concentration using a standard breathing volume for the rat (1.15 m3/kg for 24 hours exposure. The resulting air concentration needs to be additionally corrected for 24 hlight activity (20 m3), assuming 100 % absorption for both routes.
NOAEL rat
1820 mg/kg bw/day
÷1.15 m3/kgbw
÷20m3/rat
NOAECrat 79.13 mg/m3
Repeated dose toxicity: inhalation - local effects
Link to relevant study records
- Endpoint:
- chronic toxicity: inhalation
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Critical effects observed:
- not specified
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEC
- 79.13 mg/m³
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Inhalation exposure:
There are no Inhalation Repeated studies available.
The oral dose for the rat is converted to the corresponding air concentration using a standard breathing volume for the rat (1.15 m3/kg for 24 hours exposure. The resulting air concentration needs to be additionally corrected for 24 hlight activity (20 m3), assuming 100 % absorption for both routes.
NOAEL rat
1820 mg/kg bw/day
÷1.15 m3/kgbw
÷20m3/rat
NOAECrat 79.13 mg/m3
Repeated dose toxicity: dermal - systemic effects
Link to relevant study records
- Endpoint:
- chronic toxicity: dermal
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Critical effects observed:
- not specified
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 45.5 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
- Quality of whole database:
- Dermal repeated dose toxicity
There are no dermal repeated studies available.
For dermal exposure we taken that:
-the average weight of rats is 250g (200-300g),
-the dose is applied over an area which is approximately 10% of the total body surface=0.025 kg
corrected dermal NOAEL= oral NOAEL
1820 mg/kg bw/day x 0.025 kg =
NOAELrat = 45.5 mg/kg bw/day
Repeated dose toxicity: dermal - local effects
Link to relevant study records
- Endpoint:
- chronic toxicity: dermal
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Critical effects observed:
- not specified
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 5.62 mg/cm²
- Study duration:
- subacute
- Species:
- rat
Additional information
Oral repeated dose toxicity
Potassium chloride (KCl)is the most common sourceofPotassium oxide(K2O).Therefore, the health effects of potassium chloride need to be considered in the assessment of Potassium oxide
Groups of male F344/Slc rats received 110, 450, 1820 mg/kg bw/day of KCl in feed over a period of 2 years and were observed for clinical signs and mortality and were examined for gross and histopathological changes at the end of the treatment period (Imai 1961) The NOAEL was set 1820 mg/kg bw/day since nephritis was reported in all treatment groups as well as in the control group. With respect to the observed gastritis which is regarded to be a local effect a LOAEL(local) of 110 mg/kg bw/d was determined (Imai 1961, UNEP 2003).
NOAEL -1820 mg/kg bw/day
Dermal repeated dose toxicity
There are no dermal repeated studies available.
For dermal exposure we taken that:
-the average weight of rats is 250g (200-300g),
-the dose is applied over an area which is approximately 10% of the total body surface=0.025 kg
corrected dermal NOAEL= oral NOAEL
1820 mg/kg bw/dayx0.025 kg =
NOAELrat = 45.5 mg/kg bw/day
Inhalation repeated dose toxicity
There are no Inhalation Repeated studies available.
The oral dose for the rat is converted to the corresponding air concentration using a standard breathing volume for the rat (1.15 m3/kg for 24 hours exposure. The resulting air concentration needs to be additionally corrected for 24 hlight activity (20 m3), assuming 100 % absorption for both routes.
NOAEL rat
1820 mg/kg bw/day
÷1.15 m3/kgbw
÷20m3/rat
NOAECrat 79.13 mg/m3
Justification for selection of repeated dose toxicity dermal - local effects endpoint:
The generic modification from the NOAELtest (in mg/kg of body weight) to NOAELmodified (in mg/cm2/day) will be
NOAELin mg/cm2 = ((dose in mg/kg bw)x (average animal weight in kg)) / Treated surface in cm2)
NOAELtest* 0.25/44.5= NOAELmodified
The highest dose not causing irritation/corrosion was 1000 mg/kg bw in dermal toxicity study in rats of Merkel, D.J., N. 2000.
the modified dose descriptor would be
NOAELmodified =1000 mg/kg*0.25 kg/44.5cm2=5.62 mg/cm2
Repeated dose toxicity: via oral route - systemic effects (target organ) urogenital: kidneys; other: all gross lesions and masses
Repeated dose toxicity: inhalation - systemic effects (target organ) urogenital: kidneys; other: all gross lesions and masses
Repeated dose toxicity: dermal - systemic effects (target organ) other: all gross lesions and masses
Justification for classification or non-classification
Based on the hazard assessment of Potassium oxide/Dipotassium oxide in section 2.1 and 2.2. in IUCLID 5.4., available data for the substance and following the “Guidance onInformation Requirement and Chemical Safety Assessment R.8. Characterisation of dose [concentration]- response for human health”, according to the EU’s list of dangerous substances (OJEC No L200/130.7.99) and according to the criteria described in Directive 67/548 and in the CLP Regulation:
Directive 67/548 |
Repeated dose toxicity R33 Danger of cumulative effects. T; R48/23 Toxic; Toxic: danger of serious damage to health by prolonged exposure through inhalation. T; R48/23/24 Toxic; Toxic: danger of serious damage to health by prolonged exposure through inhalation and in contact with skin. T; R48/23/24/25 Toxic; Toxic: danger of serious damage to health by prolonged exposure through inhalation, in contact with skin and if swallowed. T; R48/23/25 Toxic; Toxic: danger of serious damage to health by prolonged exposure through inhalation, in contact with skin and if swallowed. T; R48/24 Toxic; Toxic: danger of serious damage to health by prolonged exposure in contact with skin. T; R48/24/25 Toxic; Toxic: danger of serious damage to health by prolonged exposure in contact with skin and if swallowed. T; R48/25 Toxic; Toxic: danger of serious damage to health by prolonged exposure if swallowed. Xn; R48/20 Harmful; Harmful: danger of serious damage to health by prolonged exposure through inhalation. Xn; R48/20/21 Harmful; Harmful: danger of serious damage to health by prolonged exposure through inhalation and in contact with skin. Xn; R48/20/21/22 Harmful; Harmful: danger of serious damage to health by prolonged exposure through inhalation, in contact with skin and if swallowed. Xn; R48/20/22 Harmful; Harmful: danger of serious damage to health by prolonged exposure through inhalation and if swallowed. Xn; R48/21 Harmful; Harmful: danger of serious damage to health by prolonged exposure in contact with skin. Xn; R48/21/22 Harmful; Harmful: danger of serious damage to health by prolonged exposure in contact with skin and if swallowed. Xn; R48/22 Harmful; Harmful: danger of serious damage to health by prolonged exposure if swallowed.
|
CLP |
Repeated dose toxicity STOT Rep. Exp. 1 STOT Rep. Exp. 2 H372: Causes damage to organs <or state all organs affected, if known> through prolonged or repeated exposure <state route of exposure if it is conclusively proven that no other routes of exposure cause the hazard>. H373: May cause damage to organs <or state all organs affected, if known> through prolonged or repeated exposure <state route of exposure if it is conclusively proven that no other routes of exposure cause the hazard>. |
It is concluded that the substance Potassium oxide/Dipotassium oxide does not meet the criteria to be classified for human health hazards for Repeated dose toxicity
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