Registration Dossier

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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Hazard for aquatic organisms

Freshwater

Hazard assessment conclusion:
no data available: testing technically not feasible

Marine water

Hazard assessment conclusion:
no data available: testing technically not feasible

STP

Hazard assessment conclusion:
no data available: testing technically not feasible

Sediment (freshwater)

Hazard assessment conclusion:
no data available: testing technically not feasible

Sediment (marine water)

Hazard assessment conclusion:
no data available: testing technically not feasible

Hazard for air

Hazard for terrestrial organisms

Soil

Hazard assessment conclusion:
no data available: testing technically not feasible

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
no data available: testing technically not feasible

Additional information

Toxicity testing of chromium (II) oxide cannot be performed as the substance is unstable and classified as pyrophoric. As chromium (II) oxide will be completely converted into the most stable stage of chromium (III), it may be more appropriate to consider possible effects of chromium (III) compounds with regard to the environment. Therefore as an example, studies on the toxicity of chromium (III) acetate as analogue substance were reported. As chromium (III) acetate is water soluble and dissociates in the aquatic environment, possible effects would mainly be attributed to the Cr3+ion. However, the studies showed no toxicity potential for the aquatic compartment, and it is not to be expected for sediment and soil either.

Trivalent chromium is the most stable oxidation state, and it is ubiquitous in the environment as part of the earth’s crust, with a tendency to form kinetically inert complexes. Generally the bioavailability of chromium (III) is low and is to large parts depending on the existing pH-regime. In aqueous solutions at environmental pH values the insoluble Cr(OH)3 is the prevailing form. Furthermore, due to precipitation and/or adsorption processes chromium (III) becomes part of the sediment and soil, respectively. Studies have shown that the low bioavailability of chromium (III) is furthermore restricted by physiology, as it is normally not possible for chromium (III) compounds to cross cell membranes (Römpp Online 2008).

Conclusion on classification