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EC number: 266-007-8 | CAS number: 65996-74-9 The oxidized surface of steel produced during reheating, conditioning, hot rolling, and hot forming operations. This substance is usually removed by process waters used for descaling, roll and material cooling, and other purposes. It is subsequently recovered by gravity separation techniques. Composed primarily of high-purity iron oxides. May contain varying amounts of other oxides, elements, and trace compounds.
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vitro / ex vivo
- Remarks:
- Bioaccessibility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2018-02-26 to 2018-09-26
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with national standard methods
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
Materials and methods
- Objective of study:
- bioaccessibility (or bioavailability)
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Series on Testing and Assessment No. 29 (23-Jul-2001): Guidance document on transformation/dissolution of metals and metal compounds in aqueous media
- Version / remarks:
- test medium, loading and test duration adopted for toxicokinetics assessment
- Principles of method if other than guideline:
- An internationally agreed guideline does not exist for this test (e.g. OECD). However, similar tests have been conducted with several metal compounds in previous risk assessments (completed under Regulation (EEC) No 793/93) and in recent preparation for REACH regulation (EC) No 1907/2006. The test was conducted on the basis of the guidance for OECD-Series on testing and assessment Number 29 and according to the bioaccessibility test protocol provided by the study monitor. The test media were artificial physiological media: gastric fluid (GST), phosphate-buffered saline (PBS), artificial lysosomal fluid (ALF) and Gamble's solution (GMB)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- signed 2016-05-31
Test material
- Reference substance name:
- Diiron trioxide
- EC Number:
- 215-168-2
- EC Name:
- Diiron trioxide
- Cas Number:
- 1309-37-1
- Molecular formula:
- Fe2O3
- IUPAC Name:
- diiron trioxide
- Test material form:
- solid: nanoform
- Details on test material:
- Appearance: red powder, odourless
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- other: in vitro (simulated human body fluids)
- Details on test animals or test system and environmental conditions:
- Test principle in brief:
- four different artificial physiological media,
- single loading of test substance of ~100 mg/L,
- GST and PBS media: samples taken after 2 and 24 hours agitation (100 rpm) at 37 ± 2 °C
- GMB and ALF media: samples taken after 2, 24 and 168 hours agitation (100 rpm) at 37 ± 2 °C
- two additional method blanks per medium, measurement (ICP-OES) of dissolved Fe concentrations after filtration and centrifugal filtration.
- the study was performed in triplicate
The aim of this test was to assess the dissolution of nano-size diiron trioxide in four artificial physiological media: Phosphate buffered saline (PBS, pH 7.2-7.4), Artificial gastric fluid (GST, 1.5-1.6), artificial lysosomal fluid (ALF) and Gamble’s solution (GMB). The test media were selected to simulate relevant human-chemical interactions (as far as practical), e.g. a substance entering the human body by ingestion into the gastro-intestinal tract (GST) or via the respiratory system (ALF).
Administration / exposure
- Duration and frequency of treatment / exposure:
- Iron concentrations in GST and PBS were determined after 2 and 24 h whereas iron concentrations in GMB and ALF media were assessed after 2, 24 and 168 hours of incubation.
Doses / concentrations
- Dose / conc.:
- 100 other: mg of test item/L artificial media
- Details on study design:
- Test setup
Three replicate flasks (500 mL glass flasks) per test medium (PBS, GST) were prepared with a loading of ~ 100 mg/L. The test item was weighed into flasks, adjusted to volume with the respective artificial physiological medium and agitated at 100 rpm at 37°C ± 2°C. Two control blank replicates (same procedure) per test medium were also prepared.
Three replicates containing the test item and two method blanks per artificial medium were tested. All solutions were sampled after 2 and 24 h whereas GMB and ALF media were also sampled after 168h to measure total dissolved Fe concentrations (ICP-OES) after 0.2 µm filtration (Syringe Filter w / 0.2 μm, polyethersulfon membrane, DIA Nielsen, Dueren, Germany) and centrifugal filtration (i.e. 0.2 μm filtration and 3kDa centrifugal filtration, Sartorius, Göttingen, Germany). In addition, temperature, pH and observations, including the appearance of the solution (including colour, turbidity and particle film on the surface) were recorded.
Sample fortification:
In addition, samples of the artificial physiological media were fortified with a known amount of iron (by standard addition of commercial standards) to determine the standard recovery. For detailed information please refer to "Any other information on materials and methods incl. tables".
Mass balance:
After the test, aqua regia (3 : 1 mixture of concentrated hydrochloric and nitric acid) was added to the vessels containing the test item to reach a final volume of 500 mL, i.e. 120 mL aqua regia were added to approximately 380 mL GST or PBS medium, 180 mL aqua regia were added to approximately 320 mL ALF or GMB medium. From these solutions, 50 mL were taken after 3 - 14 days of “digestion” for mass balance determination.
The filters (Syringe Filter w / 0.2 μm, polyethersulfon membrane, DIA Nielsen, Dueren, Germany) used for sampling were extensively rinsed with a known volume of aqua regia (ca. 2.5 mL). The added aqua regia was let to drop slowly through the filters and was collected in a clean vial. This procedure was repeated with every syringe and filter used during the study. After collection, the volume was filled up to exactly 10 mL (for the media GST and PBS) and up to 15 mL (for the ALF and GMB media) with aqua regia. Afterwards the concentration of iron in the “filtrated” aqua regia was determined and considered for the determination of the mass balances.
Reagents:
Purified water (resistivity > 18 MΩ·cm, Pure Lab Ultra water purification system from ELGA LabWater, Celle, Germany)
Nitric acid - “Supra” quality (ROTIPURAN® supplied by Roth, Karlsruhe, Germany).
Hydrochloric acid – “Baker-instra-analyzed-plus” quality (J.T. Baker, Griesheim, Germany).
Sodiumhydroxide – pro Analysis quality (Chemsolute, Th. Geyer, Renningen, Germany)
MgCl2 x 6H2O (p.A., Merck, Darmstadt, Germany)
NaCl (p.A., Chemsolute, Renningen, Germany + Merck, Darmstadt, Germany (new GMB medium))
KCl (p.A., Chemsolute, Renningen, Germany + Merck, Darmstadt, Germany (new GMB medium))
Na2HPO4 (p.A. Merck, Darmstadt, Germany)
Na2SO4 (p.A. Merck, Darmstadt, Germany)
CaCl2 x 2H2O (p.A. Merck, Darmstadt, Germany)
NaAcetate (suprapur Merck, Darmstadt, Germany)
NaHCO3 (p.A. Merck, Darmstadt, Germany)
NaOH (p.A., Chemsolute, Renningen, Germany)
Citric acid anhydrous (p.A., Roth, Karlsruhe, Germany)
Glycine (p.A., Merck, Darmstadt, Germany)
Na3Citrate x 2H2O (p.A., Merck, Darmstadt, Germany)
Na2Tartrate x 2H2O (p.A., Merck, Darmstadt, Germany)
NaLactate (98+% Sigma Aldrich, Munich, Germany)
NaPyruvate (p.A., Applichem, Darmstadt, Germany)
KH2PO4 (p.A., Merck, Darmstadt, Germany)
Urea (pure, Applichem, Darmstadt, Germany)
Lactic acid (purum, Fluka, Munich, Germany)
HCl 30% (instra-analyzed, plus J.T. Baker, Griesheim, Germany)
METAL ANALYSIS
- Standards for metal analysis: A commercially available single element standard was used as iron standard (Merck Certipur Iron ICP standard 1000 mg/L lot no. HC68868126; Darmstadt, Germany) to prepare an appropriate stock solution and subsequently calibration solutions for ICP-OES measurements
- Certified reference materials: As quality control standards, certified aqueous reference material TM-DWS.3 (lot no. 0916) and TMDA-70.2 (lot no. 0916 and 0917) obtained from Environment Canada and a multielement standard (Merck Certipur IV ICP standard 1000 mg/L lot no. HC54938555 and HC73962555; Darmstadt, Germany) were analysed for total dissolved iron by ICP-OES.
Instrumental and analytical set-up for the ICP-OES instrument:
Agilent 720, Agilent Technologies, Waldbronn, Germany
Nebulizer: Sea spray nebulizer, from Glass Expansion
Spray chamber: Iso Mist with Twister Helix from Glass Expansion
Plasma stabilization time: at least 30 min before start of the measurements
Plasma gas flow: 15.0 L/min
Additional gas flow: 1.50 L/min
Carrier gas flow: 0.75 L/min
RF power: 1200W
Stabilization time of sample: 15 sec
Repetition time (three internal measurements per sample): 30 sec
Wavelengths: Fe: 238.204 nm, 240.489 nm, 241.052 nm, 258.588 nm and 259.940 nm
- Correlation coefficients (r) for the wavelengths used for evaluation of data were at least >0.999603
The applied LOD/LOQ calculations for the Agilent 720 ICP-OES:
LOD: 3 * standard deviation of calibration blank/slope of the calibration
LOQ: 3 * LOD
The resulting LODs/LOQs are reported in "Any other information on results incl. tables" - Details on dosing and sampling:
- Loading:
Detailed loadings of the test vessels are given in "Any other information on materials and methods incl. tables".
Results and discussion
Main ADME resultsopen allclose all
- Type:
- other: Bioaccessibility ALF, 2h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- 16.4 µg Fe/L (dissolved)
- Type:
- other: Bioaccessibility ALF, 24h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- 72.1 µg Fe/L (dissolved)
- Type:
- other: Bioaccessibility ALF, 168h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- 185 µg Fe/L (dissolved)
- Type:
- other: Bioaccessibility GST, 2h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- 9.27 µg Fe/L (dissolved)
- Type:
- other: Bioaccessibility GST, 24h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- 57.5 µg Fe/L (dissolved)
- Type:
- other: Bioaccessibility GMB, 2h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- 0.03 µg Fe/L (dissolved)
- Type:
- other: Bioaccessibility GMB, 24h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- below background
- Type:
- other: Bioaccessibility GMB, 168h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- below background
- Type:
- other: Bioaccessibility PBS, 2h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- < LOD/LOQ (1.54 µg Fe/L)
- Type:
- other: Bioaccessibility PBS, 24h @ 37°C (100 mg/L loading, 0.2 µm + 3 kDa filtration for phase separation)
- Results:
- < LOD (0.761 µg Fe/L)
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- Please refer to "any other information on results incl. tables" below.
Any other information on results incl. tables
Iron concentrations in simulated artificial body fluids:
The bioaccessibility of nano-size diiron trioxide was determined in vitro by simulating dissolution under physiological conditions considered to mimic artificial body fluids with a loading of 100 mg test item/L. Dissolved iron concentrations were operationally defined as the dissolved Fe fraction after 0.2 µm filtration and centrifugal filtration (~2.1 nm), see Table 3. With a maximum mean released fraction of <0.2% after 168 h, dissolution of Ferroxide 212P E172 was highest in artificial lysosomal fluid (ALF).
In addition, dissolved/dispersed mean iron concentrations (operationally defined as the dissolved Fe fraction after 0.2 µm filtration) are summarized in table 4.
Table 3: Iron concentrations of artificial physiological media (filtrated through a 0.2 µm membrane and centrifugally filtrated) after exposure to diiron trioxide
medium & time |
LOD/LOQ of Fe measurement series |
Mean Fe±SD of method blanks |
Without background correction Mean Fe±SD |
With background correction* Mean Fe |
GST 2h |
LOD:0.677 µg/L LOQ:2.03 µg/L |
12.4±1.45 µg/L |
21.7±6.40 µg/L |
9.27 µg/L |
GST 24h(1d) |
LOD:0.689 µg/L LOQ:2.07 µg/L |
7.77±0.14 µg/L (after outlier exclusion) |
65.3±4.46 µg/L |
57.5 µg/L |
GMB 2h |
LOD:0.206 µg/L LOQ:0.619 µg/L |
2.49±0.59 µg/L |
2.52±1.07 µg/L |
0.03 µg/L |
GMB 24h (1d) |
LOD:0.190 µg/L LOQ:0.570 µg/L |
2.33±0.02 µg/L |
1.25±0.42 µg/L |
Negative value after correction |
GMB 7d |
LOD:0.242 µg/L LOQ:0.725 µg/L |
2.38±1.40 µg/L |
1.42±0.54 µg/L |
Negative value after correction |
ALF 2h |
LOD:0.287 µg/L LOQ:0.862 µg/L |
10.3±1.01 µg/L |
26.7±0.55 µg/L |
16.4 µg/L |
ALF 24h(1d) |
LOD:0.886 µg/L LOQ:2.66 µg/L |
5.64±1.83 µg/L |
77.7±2.19 µg/L |
72.1 µg/L |
ALF 7d |
LOD:0.434 µg/L LOQ:1.30 µg/L |
4.92±0.48 µg/L |
190±0.48 µg/L |
185 µg/L |
PBS 2h |
LOD:0.514 µg/L LOQ:1.54 µg/L |
All: <LOD(after outlier exclusion) |
All: <LOD/LOQ |
- |
PBS 24h (1d) |
LOD:0.761 µg/L LOQ:2.28 µg/L |
All: <LOD |
All: <LOD |
- |
*backgroundconcentration=meanofFeconcentrationsmeasuredafter 2h ,24 h or 168h
Table 4: Iron concentrations of artificial physiological media (filtrated through a 0.2 µm membrane) after exposure to diiron trioxide Ferroxide 212P E172
medium&time |
LOD/LOQ of Fe measurement series |
Mean Fe±SD of method blanks |
Without background correction Mean Fe±SD |
With background correction* MeanFe |
GST2h |
LOD:0.677 µg/L LOQ:2.03 µg/L |
All: <LOQ |
11.8±0.89 µg/L |
No correction |
GST24h(1d) |
LOD:0.689 µg/L LOQ:2.07 µg/L |
2.42±0.91 µg/L (1blank:<LOQ;3blanks:>LOQ) |
57.0±0.72 µg/L |
54.6 µg/L |
GMB 2h |
LOD:0.206 µg/L LOQ:0.619 µg/L |
0.724±0.023 µg/L (1blank<LOD;3blanks>LOQ) |
All: <LOD/LOQ |
|
GMB 24h |
LOD:0.190 µg/L LOQ:0.570 µg/L |
All: <LOD/LOQ(after outlier exclusion) |
All: <LOD (after outlier exclusion) |
|
GMB 168h |
LOD:0.242 µg/L LOQ:0.725 µg/L |
All: <LOD(after outlier exclusion) |
All: <LOD |
|
ALF2h |
LOD:0.287 µg/L LOQ:0.862 µg/L |
1.96±0.18 µg/L |
24.8±0.37 µg/L |
22.9 µg/L |
ALF24h |
LOD:0.886 µg/L LOQ:2.66 µg/L |
All: <LOQ(after outlier exclusion) |
76.6±0.58 µg/L |
No correction |
ALF168h |
LOD:0.434 µg/L LOQ:1.30 µg/L |
2.39±0.54 µg/L |
190±1.21 µg/L |
188 µg/L |
PBS 2h |
LOD:0.514 µg/L LOQ:1.54 µg/L |
All: <LOD (after outlier exclusion) |
All: <LOD/LOW (after outlier exclusion) |
|
PBS 24h |
LOD:0.761 µg/L LOQ:2.28 µg/L |
All: <LOD |
All: <LOD |
|
*background concentration=mean of Fe concentrations measured after 2h ,24 h or 168h
Mass balance
Total mass recoveries were determined by aqua regia digestion for each test item containing vessel at the end of the experiment. Regarding Ferroxide 212P E172, mass recoveries in all media investigated (GST, GMB, ALF, PBS) were > 95.0%.
Solution pH -GST
blank vessels
sample name |
target pH |
pH prior to the test |
pH after 2h |
pH after 24 h |
GSTblankvessel1 |
1.5–1.6 |
1.55 |
1.57 |
1.59 |
GSTblankvessel2 |
1.5–1.6 |
1.54 |
1.58 |
1.58 |
Ferroxide212P E172
sample name |
target pH |
pH prior to the test |
pH after 2h |
pH after 24h |
|
GSTvessel4 |
1.5–1.6 |
1.56 |
1.62 |
1.63 |
|
GSTvessel5 |
1.5–1.6 |
1.55 |
1.61 |
1.65 |
|
GSTvessel6 |
1.5–1.6 |
1.55 |
1.60 |
1.64 |
Solution pH - PBS
blank vessels
samplename |
targetpH |
pHpriortothetest |
pHafter2h |
pHafter24h |
PBSblankvessel1 |
7.2–7.4 |
7.30 |
7.30 |
7.33 |
PBSblankvessel2 |
7.2–7.4 |
7.30 |
7.33 |
7.33 |
Ferroxide212P E172
samplename |
targetpH |
pHpriortothetest |
pHafter2h |
pHafter24h |
PBSvessel4 |
7.2–7.4 |
7.31 |
7.35 |
7.33 |
PBSvessel5 |
7.2–7.4 |
7.29 |
7.32 |
7.33 |
PBSvessel6 |
7.2–7.4 |
7.30 |
7.32 |
7.36 |
Solution pH - GMB
blank vessels
samplename |
targetpH |
pHpriortothetest |
pHafter2h |
pHafter24h |
pHafter7d |
GMBblankvessel1 |
7.4 |
7.46 |
8.10 |
8.68 |
9.09 |
GMBblankvessel2 |
7.4 |
7.46 |
8.14 |
8.74 |
9.09 |
Ferroxide212P E172
samplename |
targetpH |
pHpriortothetest |
pHafter2h |
pHafter24h |
pHafter7d |
GMBvessel4 |
7.4 |
7.45 |
8.19 |
8.80 |
9.24 |
GMBvessel5 |
7.4 |
7.46 |
8.20 |
8.71 |
9.24 |
GMBvessel6 |
7.4 |
7.45 |
8.22 |
8.86 |
9.22 |
Solution pH - ALF
blank vessels
samplename |
targetpH |
pHpriortothetest |
pHafter2h |
pHafter24h |
pHafter7d |
ALFblankvessel1 |
4.5 |
4.56 |
4.57 |
4.62 |
4.62 |
ALFblankvessel2 |
4.5 |
4.56 |
4.59 |
4.62 |
4.62 |
Ferroxide212P E172
samplename |
targetpH |
pHpriortothetest |
pHafter2h |
pHafter24h |
pHafter7d |
ALFvessel4 |
4.5 |
4.56 |
4.59 |
4.62 |
4.63 |
ALFvessel5 |
4.5 |
4.55 |
4.60 |
4.62 |
4.62 |
ALFvessel6 |
4.5 |
4.55 |
4.59 |
4.62 |
4.62 |
Test temperature:
With 37 °C ± 2 °C, the temperature was stable during the test for all solutions
Method validation summary (ICP-OES)
Limits of detection (LODs), limits of quantification (LOQs) and correlation coefficients (r)
Limits of detection (LOD) within all measurement series: < 1.24 µg Fe/ L.
Limits of quantification (LOQ) within all measurement series: < 3.73 µg Fe/ L.
Correlation coefficients (r) within all measurement series: >0.999603
GST
Mean recovery of fortified samples (n = 20): 98.6 - 104 %
Mean recoveries for certified reference materialTM-DWS.3andTMDA-70.2(concentration range 22.4 – 75.4 µg Fe / L, n = 24): 103 -105 %
Mean recoveries for quality control standard (concentration range 50 -500 µg Fe/ L, n = 24): 98.2 - 105 %
Mean recoveries for internal standard (concentration range 10 -300 µg / L, n = 24): 98.4 - 100 %
PBS
Mean recovery of fortified samples (n = 32): 90.5 - 108 %
Mean recoveries for certified reference materialTM-DWS.3andTMDA-70.2(concentration range 22.4 – 75.4 µg Fe / L, n = 20): 98.0-101 %
Mean recoveries for quality control standard (concentration range 5 -50 µg Fe/ L, n = 30): 97.0 – 99.9 %
Mean recoveries for internal standard (concentration range 10 -100 µg / L, n = 30): 97.5 – 99.8 %
GMB
Mean recovery of fortified samples (n = 48): 92.2 - 128 %
Mean recoveries for certified reference materialTM-DWS.3andTMDA-70.2(concentration range 22.4 – 75.4 µg Fe / L, n = 59): 95.5-107 %
Mean recoveries for quality control standard (concentration range 5 -50 µg Fe/ L, n = 60): 95.5 – 104 %
Mean recoveries for internal standard (concentration range 10 -100 µg / L, n = 60): 97.0 – 102 %
ALF
Mean recovery of fortified samples (n = 24): 85.5 - 106 %
Mean recoveries for certified reference materialTM-DWS.3andTMDA-70.2(concentration range 22.4 – 75.4 µg Fe / L, n = 48): 93.6-103 %
Mean recoveries for quality control standard (concentration range 5 -200 µg Fe/ L, n = 48): 96.1-100 %
Mean recoveries for internal standard (concentration range 10 -100 µg / L, n = 48): 95.0 – 106 %
Method validation – mass balance measurements
Mean recovery of fortified samples (n = 27): 89.4 - 106 %
Mean recoveries for certified reference materialTM-DWS.3andTMDA-70.2(concentration range 22.4 – 75.4 µg Fe / L, n = 30): 100-109 %
Mean recoveries for quality control standard (concentration range 250 -600 µg Fe/ L, n = 30): 100-103 %
Mean recoveries for internal standard (concentration range 100 -400 µg / L, n = 30): 100 – 106 %
Applicant's summary and conclusion
- Conclusions:
- The bioaccessibility of nano-size diiron trioxide was determined in vitro by simulating dissolution under physiological conditions considered to mimic artificial body fluids with a loading of 100 mg test item/L. After 2 and 24 h in phosphate buffered saline (PBS, pH 7.2-7.4) solution, dissolved iron concentrations (operationally defined as the dissolved Fe fraction after 0.2 µm filtration and centrifugal filtration (~2.1 nm)) were at least below the LOQ (<1.54 µg/L). With mean concentrations of 0.03 µg Fe/L after 2 h and negative values (after subtraction of background) after 24 and 168 h, dissolved iron concentrations in Gamble´s solution (GMB, pH 7.4) were also very low. In artificial gastric fluid (GST, pH 1.5-1.6), 9.27 µg Fe/L and 57.5 µg Fe/L were detected in the dissolved phase after 2 and 24 h, respectively. Mean iron concentrations were highest in artificial lysosomal fluid (ALF, pH 4.5): 16.4 µg/L, 72.1 µg/L and 185 µg/L of iron were found in the dissolved phase after 2, 24 and 168 h. Therefore, with a maximum mean released fraction of <0.2% after 168 h, the dissolution of diiron trioxide was highest in artificial lysosomal fluid (ALF).
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