Screening Assessment for the Challenge 2-Butanone, oxime (Butanone oxime) Chemical Abstracts Service Registry Number 96-29-7 Environment Canada Health Canada March 2010 Screening Assessment CAS RN 96-29-7 Synopsis Pursuant to section 74 of the Canadian Environmental Protection Act, 1999 (CEPA 1999), the Ministers of the Environment and of Health have conducted a screening assessment of 2-butanone, oxime (butanone oxime), Chemical Abstracts Service Registry Number 96-29-7. This substance was identified in the categorization of the Domestic Substances List as a high priority for action under the Ministerial Challenge. Butanone oxime was identified as a high priority as it was considered to pose greatest potential for exposure of individuals in Canada and had been classified by the European Commission on the basis of carcinogenicity. Although butanone oxime met the ecological categorization criteria for persistence, it did not meet the criteria for bioaccumulation potential or inherent toxicity to aquatic organisms. Therefore, the focus of this assessment of 2-butanone, oxime relates primarily to human health risks. Butanone oxime is widely used as an anti-skinning agent in the formulation of alkyd paints, varnishes, stains and coatings for both industrial and consumer use. In Canada, the substance has also been reported in a number of pesticide products, namely wood preservatives and antifouling marine paints, as well as in some adhesives, silicone sealants and printing inks. Furthermore, butanone oxime is used as a corrosion inhibitor in industrial boilers and water treatment systems and serves as a blocking agent in the manufacturing process of urethane polymers. According to the information submitted under section 71 of CEPA 1999, butanone oxime was not manufactured by any company in Canada in the 2006 calendar year. However, approximately 500 000 kg of the substance was imported in 2006, and nearly 120 000 kg was used in the same reporting year. There are few data on the release and fate of butanone oxime in environmental media in Canada or elsewhere. Butanone oxime is not a naturally occurring substance; thus, releases of the substance to the environment are expected to result directly from anthropogenic activities. Considering the quantity of butanone oxime in commerce in Canada and its use in a variety of consumer products, exposure of the general population to the substance is expected to be moderate. As butanone oxime was classified on the basis of carcinogenicity by the European Commission, carcinogenicity was a key focus for this screening assessment. Increased incidences of liver tumours were observed in rat and mouse lifetime studies, and there was also an increased incidence of mammary gland tumours in female rats; however, this was seen only at moderate and/or high concentrations of butanone oxime. Consideration of the available information regarding genotoxicity indicates that butanone oxime is not likely to be genotoxic. Accordingly, although the mode of induction of tumours is not fully elucidated, the tumours observed are not considered to have resulted from direct interaction with genetic material. Therefore, a threshold approach is used to assess risk to human health. Non-neoplastic effects were observed in the nasal cavity of rats and/or mice in inhalation studies of short-term through to chronic exposure duration. Also, repeated-dose studies based on oral exposure showed effects in the spleen, liver and kidney of rats as well as ii Screening Assessment CAS RN 96-29-7 hematological effects in both rats and rabbits. Based on comparison of estimated exposures to butanone oxime in Canada with the critical effect levels, and taking into account the uncertainties in the databases on exposure and effects, it is considered that the resulting margins of exposure, particularly for consumer exposure from products containing the substance, may not be adequately protective of human health for non- cancer effects. On the basis of the potential inadequacy of the margins between estimated exposures to butanone oxime and critical effect levels, it is concluded that butanone oxime is a substance that may be entering the environment in a quantity or concentration or under conditions that constitute or may constitute a danger in Canada to human life or health. On the basis of ecological hazard and estimated releases of butanone oxime, it is concluded that the substance is not entering the environment in a quantity or concentration or under conditions that have or may have an immediate or long-term harmful effect on the environment or its biological diversity or that constitute or may constitute a danger to the environment on which life depends. Butanone oxime does meet the criteria for persistence but does not meet the criteria for bioaccumulation potential as set out in the Persistence and Bioaccumulation Regulations. Based on the information available, it is concluded that butanone oxime meets one or more of the criteria set out in section 64 of CEPA 1999. This substance will be considered for inclusion in the Domestic Substances List inventory update initiative. In addition and where relevant, research and monitoring will support verification of assumptions used during the screening assessment and, where appropriate, the performance of potential control measures identified during the risk management phase. iii Screening Assessment CAS RN 96-29-7 Introduction The Canadian Environmental Protection Act, 1999 (CEPA 1999) (Canada 1999) requires the Minister of the Environment and the Minister of Health to conduct screening assessments of substances that have met the categorization criteria set out in the Act to determine whether these substances present or may present a risk to the environment or to human health. Based on the information obtained through the categorization process, the Ministers identified a number of substances as high priorities for action. These include substances that • met all of the ecological categorization criteria, including persistence (P), bioaccumulation potential (B) and inherent toxicity to aquatic organisms (iT), and were believed to be in commerce; and/or • met the categorization criteria for greatest potential for exposure (GPE) or presented an intermediate potential for exposure (IPE) and had been identified as posing a high hazard to human health based on classifications by other national or international agencies for carcinogenicity, genotoxicity, developmental toxicity or reproductive toxicity. The Ministers therefore published a notice of intent in the Canada Gazette, Part I, on December 9, 2006 (Canada 2006), which challenged industry and other interested stakeholders to submit, within specified timelines, specific information that may be used to inform risk assessment and to develop and benchmark best practices for the risk management and product stewardship of those substances identified as high priorities. The substance 2-butanone, oxime (butanone oxime) was identified as a high priority for assessment of human health risk because it was considered to present GPE and had been classified by another agency on the basis of carcinogenicity. The Challenge for butanone oxime was published in the Canada Gazette on August 30, 2008 (Canada 2008). A substance profile was released at the same time. The substance profile presented the technical information available prior to December 2005 that formed the basis for categorization of this substance. As a result of the Challenge, submissions of information were received. Although butanone oxime was determined to be a high priority for assessment with respect to human health and met the ecological categorization criteria for persistence, it did not meet the criteria for bioaccumulation or inherent toxicity to aquatic organisms. Therefore, this assessment focuses principally on information relevant to the evaluation of risks to human health. Screening assessments examine scientific information and develop conclusions by incorporating a weight of evidence approach and precaution. 1 Screening Assessment CAS RN 96-29-7 This screening assessment includes consideration of information on chemical properties, hazards, uses and exposure, including the additional information submitted under the Challenge. Data relevant to the screening assessment of this substance were identified in original literature, review and assessment documents and stakeholder research reports and from recent literature searches, up to November 2008 for the human health sections and May 2009 for the ecological sections. Key studies were critically evaluated; modelling results may have been used to reach conclusions. Evaluation of risk to human health involves consideration of data relevant to estimation of exposure (non- occupational) of the general population, as well as information on health hazards (based principally on the weight of evidence assessments of other agencies that were used for prioritizing the substance). Decisions for human health are based on the nature of the critical effect and/or margins between conservative effect levels and estimates of exposure, taking into account confidence in the completeness of the identified databases on both exposure and effects, within a screening context. The screening assessment does not represent an exhaustive or critical review of all available data. Rather, it presents a summary of the critical information upon which the conclusion is based. This screening assessment was prepared by staff in the Existing Substances Programs