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EC number: 251-807-1 | CAS number: 34041-09-3
- 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
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- 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
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- Biological effects monitoring
- Biotransformation and kinetics
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
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- Repeated dose toxicity
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- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
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- Additional toxicological data

Monitoring data
Administrative data
- Endpoint:
- monitoring data
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Reliable ambient monitoring data were collected from various national and international environmental agencies. Main data were generated in the GEMAS-project. Methodology and procedures for data analyses were in line with the guidance given by ECHA (European Chermicals Agency) and with the methodology that was followed in existing compulsory and voluntary risk assessments for some other metals (e.g., Zn, Cu, Ni, Pb)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- other: ECHA, 2008. RIP 3.2: Guidance on information requirements and chemical safety assessment. Chapter R.16: Environmental Exposure Estimation
- Qualifier:
- according to guideline
- Guideline:
- other: EC, 2003. Technical Guidance Document in support of Commission Directive 93/67/EEC on risk assessment for new notified substances and Commission Regulation (EC) No 1488/94 on risk assessment for existing substances. Part II: Environment.
- GLP compliance:
- no
- Type of measurement:
- other: ambient concentration levels
- Media:
- soil
Test material
- Reference substance name:
- Molybdenum
- EC Number:
- 231-107-2
- EC Name:
- Molybdenum
- Cas Number:
- 7439-98-7
- Molecular formula:
- Mo
- IUPAC Name:
- molybdenum
- Details on test material:
- no Mo-compounds added to soil; determination of ambient levels in the environment
Constituent 1
Results and discussion
- Details on results:
- The regional (EU) ambient reasonable-worst-case concentration of molybdenum in european grazing land is 1.04 mg/kg dry wt.
The regional (EU) ambient reasonable-worst-case concentration of molybdenum in european agricultural land is 0.86 mg/kg dry wt.
Any other information on results incl. tables
Table 1 represents the country-specific 50th and 90th percentiles of Mo-levels in soil samples taken from grazing land and agricultural land.
Country-specific RWC-ambient Mo-levels in grassland soils ranged from 0.33 mg/kg dry wt (Lithuania) to 3.26 mg/kg dry wt (Croatia) (difference of a factor of 9.9). The median RWC-ambient PEC value for Europe is 1.04 mg/kg dry wt. The lowest values (<1.0 mg/kg dry wt) were mainly situated in Eastern/Central Europe (e.g., Baltic countries, Hungary, Czech Republic, Germany, Denmark. Countries with relatively higher RWC-ambient PEC (i.e., >30 mg/kg) were mainly situated in Southern Europe (e.g., Greece, Croatia, Italy, Cyprus, Montenegro, Macedonia).
In general the same trends that were found in grassland soils were also observed in agricultural soils: the lowest RWC-ambient PECs (i.e., below 1 mg Mo/kg) were observed in Eastern/Central Europe (e.g., Baltic States, Bulgaria, Hungary, Poland, Ukraine). Higher levels (> 1 mg/kg) were more typical for the Northern part of Europe (e.g., Scandinavian countries, British Islands) and some Mediterranean countries (e.g., Italy, Spain, Croatia). A difference of a factor of 7.1 was determined between the lowest (0.31 mg Mo/kg in Lithuania) and highest (2.19 mg Mo/kg; Sweden) country-specific RWC-ambient PEC. The typical value for Europe was 0.86 mg Mo/kg.
Table 1: Country-specific RWC-ambient PEC of molybdenum in grazing land and agricultural land
Country | RWC-ambient PEC for grazing land | RWC-ambient PEC for agricultural land |
mg/kg dry wt | ||
Austria | 1.23 | 1.41 |
Belgium | 0.93 | 0.73 |
Bosnia-Herzegowina | 0.94 | 1.15 |
Bulgaria | 0.68 | 0.55 |
Croatia | 3.26 | 2.03 |
Cyprus | 1.25 | 1.67 |
Czech Republic | 0.64 | 0.69 |
Denmark | 0.45 | 0.37 |
Estonia | 0.40 | 0.42 |
Finland | 1.18 | 1.47 |
France | 0.93 | 0.98 |
Germany | 0.85 | 0.73 |
Greece | 1.21 | 1.00 |
Hungary | 0.55 | 0.54 |
Ireland | 1.95 | 1.29 |
Italy | 1.37 | 1.37 |
Latvia | 0.35 | 0.35 |
Lithuania | 0.33 | 0.31 |
Macedonia | 2.34 | 1.03 |
Montenegro | 2.35 | 0.57 |
The Netherlands | 0.59 | 0.42 |
Norway | 1.85 | 1.47 |
Poland | 0.46 | 0.39 |
Portugal | 0.72 | 0.71 |
Switzerland | 2.36 | 1.00 |
Slovakia | 1.16 | 0.70 |
Slovenia | 1.14 | 1.30 |
Spain | 1.25 | 1.09 |
Serbia | 0.55 | 0.45 |
Sweden | 1.84 | 2.19 |
Ukraine | 0.57 | 0.56 |
United Kingdom | 1.22 | 1.29 |
Median for Europe | 1.04 mg/kg dry wt | 0.86 mg/kg dry wt |
The GEMAS-data set is the most robust and most recent data set for Europe which describes molybdenum concentration levels in two different types of soil: agricultural and grassland soils. The derived values of 1.04 mg/kg dry wt and 0.86 mg/kg dry wt for grazing land and agricultural land, respectively, are therefore put forward as the most relevant and reliable concentrations levels for molybdenum in European soils.
Ambient molybdenum concentrations for the terrestrial compartment were also determined with other available data sets. Based on these data the regional RWC-ambient PEC concentrations were situated between 0.45 mg/kg (Spain) and 5.78 mg/kg (Sweden). One should take in mind that the regional RWC-ambient PEC for arable soils was below the detection limit for four countries. Taking countries outside Europe into account, relevant Mo-levels in soil were situated between 0.2 and 9.5 mg/kg dry wt. All of these values are in line with the molybdenum concentration levels that were generated with the GEMAS data set.
Applicant's summary and conclusion
- Conclusions:
- Based on the monitoring data that were collected for different EU-countries, reliable regional RWC-ambient PEC of 0.86 and 1.04 mg/kg dry wt have been derived for agricultural soils and grazing land soils, respectively.
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