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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

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Description of key information

Additional information

Ziegler Bottoms are characterized as comprising of two primary constituents; icosan-1-ol and docosan-1-ol. Together these primary constituents represent a structural class of components (alcohols) that constitute approximately 82% of the composition of Ziegler Bottoms. Study data, where available, for each of these primary constituents has been evaluated and considered together. In a conservative approach the most sensitive study result from across the two constituents has been identified and used to address the Ziegler Bottoms endpoint in question. 

The REACH requirement in Annex IX for a study on bioaccumulation in aquatic species is not needed if the substance has a low potential for bioaccumulation and/or a low potential to cross biological membranes. The waiver argumentations are based on the technical difficulties associated with conducting bioaccumulation studies, the ready biodegradability of the test substance, the low toxicity in aquatic organisms and the low toxicity in mammals resulting in the unlikely potential for secondary poisoning, as presented in more detail below:

Study not technically feasible

The requirement to conduct bioaccumulation studies for icosan-1-ol and docosan-1-ol is waived due to technical difficulties in performing such a test. Guideline (standard) studies of bioaccumulation in fish would be confounded by the technical difficulties of maintaining the test alcohols (icosan-1-ol and docosan-1-ol) in solution, as was demonstrated in long-term invertebrate studies reported in the OECD SIDS Report for Long Chain Alcohols (2006). Severe difficulties were encountered when studies were conducted with ¿C15 alcohols, which are similar to constituents of the Ziegler Bottoms, as biodegradation in the test system was almost complete within the 24-hr test media renewal period.


Icosan-1-ol and docosan-1-ol are both readily biodegradable. The most recent reliable study (OECD 301B) using icosan-1-ol reported results of 87.9% (CO2) in 28 days confirming the readily biodegradable (P&G, 2009). The finding is consistent with very high levels of removal in other types of test systems where very fast degradation and metabolism in microorganisms and a range of trophic levels has been identified for alcohols in the range C6-24. Ready biodegradability means that the test substance will rapidly be unavailable for uptake and bioaccumulation in biological organisms.

Toxicity to Aquatic Organisms

Generally the short-term aquatic toxicity of the two primary constituent substances (icosan-1-ol and docosan-1-ol) is low. According to the OECD SIDS Report for Long Chain Alcohols (2006) long-term toxicity is also considered to be very low and below the limit of solubility for alcohols ¿ C15 in chain length.

Toxicity to Mammals

There is no requirement in REACH to conduct a secondary poisoning assessment in view of the lack of toxic effects in mammals. Chronic and sub-chronic mammalian toxicity studies have shown that long chain alcohols (LCA) are of low toxicity. Furthermore, combined repeated-dose studies with developmental endpoints, as well as reproductive and developmental studies, showed no effects at the highest dose tested. This evidence indicates that the test substance is not considered to be toxic (in PBT terms) to mammals and secondary poisoning is unlikely to occur in the environment.


The data requirement for bioaccumulation studies in aquatic and terrestrial organisms is waived on the evidence of technical difficulties, ready biodegradability and the absence of toxicity in aquatic organisms and mammals. A bioconcentration factor for icosan-1-ol and docosan-1-ol was calculated from the estimated log Kow value of 7.75 using the parabolic recalculated Connell and Hawker equation; the BCF is 31,800 L/kg. However, predicted BCFs for long chain alcohols are considered to be overestimates by orders of magnitude due to the natural ability of biochemical systems in organisms to metabolise alcohols (OECD SIDS Initial Assessment Report (2006); Veithet al(1979) and Connell and Hawker (1988)).


SIDS Initial Assessment Report on Long Chain Alcohols (2006). Organisation for Economic Cooperation and Development (OECD).

Veith GD, Defoe DL and Bergstedt BV (1979). Measuring and estimating the bioconcentration factor of chemicals in fish. J. Fish. Board Can. 36: 1040-1048.

Connell DW and Hawker DW (1988). Use of polynomial expressions to describe the bioconcentration of hydrophobic chemicals by fish. Ecotox. Environ. Safety 16: 242-257.