Registration Dossier

Administrative data

Endpoint:
toxicity to terrestrial plants: long-term
Type of information:
migrated information: read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Well performed study with several Zr compounds. However, only unbound NOEC values were obtained because limit tests were performed.

Data source

Reference
Reference Type:
publication
Title:
Unnamed
Year:
2006

Materials and methods

Test guideline
Qualifier:
equivalent or similar to
Guideline:
EPA OPPTS 850.4230 (Early Seedling Growth Toxicity Test)
Deviations:
yes
Remarks:
: only 7 days of exposure
GLP compliance:
not specified

Test material

Reference
Name:
Unnamed
Type:
Constituent
Type:
Constituent
Type:
Constituent
Details on test material:
Test substance 1:
- zirconium dichloride oxide
- Molecular formula : ZrOCl2
- Analytical purity: 98%
- Supplier: Sigma-Aldrich

Test substance 2:
- zirconium acetate
- Molecular formula : C2H4O2Zr
- Analytical purity: not reported (high purity)
- Supplier: Sigma-Aldrich

Test substance 3:
- zirconium(IV)hydroxide
- Zr(OH)4
- Analytical purity: 97%
- Supplier: Aldrich
Specific details on test material used for the study:
Details on properties of test surrogate or analogue material (migrated information):
ZrOCl2 and Zr acetate are water soluble Zr compounds, whereas Zr(OH)4 is not.

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
- Spiked soils were not sampled for analysis.
- Background Zr was determined in soil samples from both soils prior to testing.
- After 7 days of exposure, roots and aerial parts were separated for measuring weights and analyzing for Zr content.

Test substrate

Vehicle:
no
Details on preparation and application of test substrate:
- Method of mixing into soil (if used): soils were spiked with solutions of ZrOCl2 or Zr acetate (soluble) to increase the total soil Zr concentration by 100 mg Zr/kg dry soil - in a third experiment soils were spiked with Zr(OH)4 (insoluble) to increase the total soil Zr concentration by 286 mg Zr/kg dry soil
- Controls: in each experiment, five control replicates were used (unspiked cultivated soils)
- Background Zr concentrations in soil A and B were 417.4 and 164 mg Zr/kg dry soil. According to Kabata-Pendias and Pendias (1992) the main minerals of Zr present in soil are the low soluble zircon (ZrSiO4) and baddeleyite (ZrO2).
- In the experiments with the soluble Zr compounds total Zr concentrations were hence 517.4 and 264 mg Zr/kg dw in soil A and B, respectively.
- In the experiment with the insoluble Zr compound total Zr concentrations were hence 703.4 and 450 mg Zr/kg dw in soil A and B, respectively.

Test organisms

open allclose all
Species:
Pisum sativum
Plant group:
Dicotyledonae (dicots)
Details on test organisms:
- Common name: pea
- Plant family: Fabaceae
- Variety: cv. "Express"
- Prior seed treatment/sterilization: disinfected in a bath of 6% H2O2 and rinsed with deionized water
Species:
Lycopersicon esculentum
Plant group:
Dicotyledonae (dicots)
Details on test organisms:
- Common name: tomato
- Plant family: Solanaceae
- Variety: cv. St. Pierre
- Prior seed treatment/sterilization: disinfected in a bath of 6% H2O2 and rinsed with deionized water

Study design

Test type:
early seedling growth toxicity test
Study type:
laboratory study
Substrate type:
natural soil
Limit test:
yes
Total exposure duration:
7 d
Remarks:
Following the soil experiments, experiments were conducted in hydroponic conditions (details of tests conditions are quite similar and not discussed here).

Test conditions

Test temperature:
Ambient temperature (15-32°C), greenhouse conditions
pH:
Soil A: 5.45
Soil B: 8.3
Nutrient solution: 5.5
Moisture:
Air humidity = 80%
Soil water content = 38-39% (pF = 1.5)
Details on test conditions:
TEST SYSTEM
- Testing facility: greenhouse
- Test container (type, material, size): plastic pots containing 175 g of soil
- Amount of soil: 175 g
- Method of seeding: Seeds were placed in a preculture device composed of PVC cylinders, to which a base of a 500 µm grid had been glued. The seeds were germinated in a 5L aerated nutrient solution and were protected from excess light for the first 7 days. Germinated plants were placed in contact with 5L aerated nutrient solution in the soil experiments for another 14 days prior to exposure.
- No. of seeds per container: not reported
- No. of plants (retained after thinning): not reported
- No. of replicates per treatment group: 5
- No. of replicates per control: 5

SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
COLLECTION AND STORAGE
- Geographic location: two agricultural soils were sampled close to the underground research laboratory (Meuse/Haute Marne, France) of the National Agency for management of radioactive wastes (Andra)
- Sampling depth (cm): top soils 0-20 cm
- Soil preparation (e.g.: 2 mm sieved; air dried etc.): air-dry soils were crushed and sieved under 2 mm
PROPERTIES
Soil A (acidic sandy clayey loamy)
- % sand: 31.9
- % silt: 48.7
- % clay: 19.4
- pH: 5.45
- Organic carbon (%): 31.8
- CEC (meq/100 g): 9.0 cmol/kg
- Background Zr content: 417.4 mg/kg dw
Soil B (clayey calcareous soil)
- % sand: 10.7
- % silt: 50.7
- % clay: 38.6
- pH: 8.3
- Organic carbon (%): 33.6
- CEC (meq/100 g): 10.02 cmol/kg- Geographic location:
- Background Zr content: 164 mg/kg dw

NUTRIENT MEDIUM (if used)
- Description: only used during preculturing (see materials and methods section for composition)

GROWTH CONDITIONS
- Photoperiod: ambient (greenhouse experiment)
- Light source: natural sunlight
- Day/night temperatures: 15-32°C temperature range
- Relative humidity (%): 80
- Watering regime and schedules: initial water content 38-39%, afterwards deionised water was added when required
- Water source/type: initially nutrient solution, afterwards deionised water

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : at the end of testing, root and shoot fresh weight was determined
Nominal and measured concentrations:
- In the experiments with the soluble Zr compounds total Zr concentrations were 517.4 and 264 mg Zr/kg dw in soil A and B, respectively (i.e., 100 mg/kg added).
- In the experiment with the insoluble Zr compound total Zr concentrations were 703.4 and 450 mg Zr/kg dw in soil A and B, respectively (i.e., 286 mg/kg added).

Results and discussion

Effect concentrationsopen allclose all
Species:
Lycopersicon esculentum
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
>= 517.4 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
element
Remarks:
Zr
Basis for effect:
other: root and shoot fresh weight
Remarks on result:
other: For soil A and 100 mg Zr/kg dw added using ZrOCl2 or Zr acetate
Species:
Lycopersicon esculentum
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
>= 264 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
element
Remarks:
Zr
Basis for effect:
other: root and shoot fresh weight
Remarks on result:
other: For soil B and 100 mg Zr/kg dw added using ZrOCl2 or Zr acetate
Species:
Lycopersicon esculentum
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
>= 703.4 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
element
Remarks:
Zr
Basis for effect:
other: root and shoot fresh weight
Remarks on result:
other: For soil A and 286 mg Zr/kg dw added using Zr(OH)4
Species:
Lycopersicon esculentum
Duration:
7 d
Dose descriptor:
NOEC
Effect conc.:
>= 450 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
element
Remarks:
Zr
Basis for effect:
other: root and shoot fresh weight
Remarks on result:
other: For soil B and 286 mg Zr/kg dw added using Zr(OH)4
Details on results:
- Similar unbound NOECs were observed for Pisum sativum.
- Tomato and pea roots grown on the acidic soil (soil A) spiked with ZrOCl2 or Zr acetate were slightly less developed than the other ones. This lower growth can be correlated to the higher Zr uptake for these two forms.
- In the hydroponic experiments, some chlorotic leaves were observed but this could be attributed to lack of Fe in the nutrient solution.
Reported statistics and error estimates:
ANOVA + mean comparison by LSD Fisher test

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
The highest unbound NOEC was >= 703.4 mg Zr/kg dw for the acidic soil (1796.6 mg ZrCl4/kg dw) and the lowest unbound NOEC was >= 450 mg Zr/kgdw for the calcareous soil (i.e 1149.4 mg ZrCl4/kgdw), both soils amended with 286 mg Zr/kg Zr(OH)4.
Executive summary:

In this study, tomato and pea seedlings (ca. 21 days old) were exposed for 7 days to two different soils contaminated with either a soluble Zr compound (ZrOCl2 or Zr acetate) or an insoluble Zr compound (Zr(OH)4). In none of the experiments adverse effects were observed on root or shoot fresh weight of the plants. Unbound NOEC values were obtained for all experiments. The highest unbound NOEC was >= 703.4 mg Zr/kg dw (i.e. 1796.6 mg ZrCl4/kg dw) for the acidic soil (417.4 mg Zr/kg background) and the lowest unbound NOEC was >= 450 mg Zr/kgdw (i.e 1149.4 mg ZrCl4/kgdw), both soils amended with 286 mg Zr/kg Zr(OH)4.