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Experience

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Title: Experience


1
Experience Conclusions from testing the Draft
cTGD
  • Dr. Christine Stevens D.A.B.T.
  • Dow Corning

2
Characterization according to market risk
properties
  • Substance volatile siloxane
  • Classification and Labelling F N (R11, R50)
  • Use identification
  • Polymers Intermediates
  • Used in personal care
  • Off-site chemical intermediate
  • Automotive

3
(No Transcript)
4
Environmental Emission Estimation
  • Method Exposure Tools
  • ECETOC TRA
  • EUSES (European Union System for Evaluation of
    Substances)
  • cTGD Part A Questionnaire
  • AISE exemplification based on detailed
    discussions with a customer to obtain their
    estimation of potential losses
  • Output from AISE exemplification compared with
    EUSES output
  • At all stages where more accurate information was
    available, EUSES defaults were overwritten
  • Conducted for personal/domestic chemical
    intermediate use

5
Environmental Emission Estimation
6
Prediction of Regional Concentrations
PECRegional
  • Regional background reflects all EU inputs from
    all sources
  • Regional background obtained by dividing total
    tonnage by 10 (10 theoretical regions)
  • However this may be amended if all the production
    use occur in a single region
  • Quantities emitted to the various compartments
    depends on the phys/chem properties of the
    material. This is calculated by EUSES
    automatically
  • The Regional Background is also added when
    calculating Local Emissions

7
Prediction of Regional Concentrations
8
Prediction of Local Concentrations (PECLocal)
  • Local concentrations are calculated using the
    local production or processing tonnages, combined
    with EUSES defaults for emission fractions
    released to the environment number of emission
    days per year (the infamous A B tables)
  • These are highly conservative defaults should
    be overwritten if site specific data is
    available
  • Recognising this, ECB intends that in future
    re-iterations of the model, e.g. the EUSES
    Spreadsheet version, the AB tables will be
    replaced by specific information
  • To improve the output of the model very detailed
    information is required.

9
Prediction of Local Concentrations
10
Risk Characterization Ratios (RCRs)
11
Key Experience and conclusions
  • Draft cTGD part A questionnaire is too detailed
    for many DU.
  • Likely that will need two levels of detail for
    the questionnaire for customers with without
    expertise
  • Good quality feedback on the questionnaire is
    essential, but, more detail required to avoid
    generating over cautious RA
  • Questionnaire does not address re-use of waste
    (on DU site) or cleaning of vessels process
    lines, or maintenance

12
Key Experience and conclusions
  • Use descriptors in TGD EUSES do not correspond
  • Descriptor for technical function has limited
    value is difficult to assign What happens if
    product serves more than one technical function?
    e.g.
  • Adhesion Promoter
  • Curing Agent
  • Sizing Agent
  • Also may encounter confidentiality problems as
    customers do not want to reveal exact function of
    an ingredient in a formulation
  • Problem that procedures vary from one customer to
    another (even if doing same basic process), such
    that exposures will differ. Must therefore base
    it on worst-case or sub-divide into e.g. two
    levels of environmental protection.

13
Key Experience and conclusions (re environment)
  • ECETOC TRA Phase 1 not adequate for Tier 1
    Environmental assessment too simplistic
    automatically requires a Tier 2 assessment
  • Tier 2 Tool EUSES (European Union System for
    Evaluation of Substances)
  • Developed to support Existing Substance RAs
  • Based on Industry Use Categories (IC/UC) and A
    B Emission Tables
  • Complex requires expert user
  • Large amount of detailed information required to
    avoid the application of highly conservative
    defaults
  • Initial input data may generate RCRs gt 1.0 for
    some compartments

14
Key Experience and conclusions
  • EUSES is a good tool but require a high level of
    expertise unlikely that all but the large DUs
    have this. Therefore subdivide customers
  • Work with key customers to develop use-specific
    ES
  • Translate into generic form to send to other less
    skill-rich DU
  • Process has only evaluated a single substance,
    will be much more complex for preparations
  • It is not clear how useful these tools or the
    Phase II developments will be to assess
    environmental exposure of Preparations

15
Additional tools
  • EU TGD Spreadsheet Version
  • Simpler to use than EUSES
  • Not reliant on A B Tables (ECB to drop these as
    no substantiation for some emission values)
    specific emission data can be inputted
  • Enables impact of changes in input data to output
    data to be seen at once
  • But errors exist in the spreadsheet code, which
    still need rectifying

16
Improvements to Existing Tools
  • ECETOC TRA Phase II objective is to
  • Generate a user-friendly tool
  • Based on EU TGD Spreadsheet Version, with the
    proviso
  • Inconsistencies with EUSES are corrected
  • Will be able to calculate safe emission levels
  • Enable Tier 1 assessment based on minimal data
    input
  • Enable higher Tier assessment based on more
    detailed data input
  • Identifies the Target Compartment of concern
    calculates the quantity of material which can be
    used without exceeding RCR of 1
  • Provides a Customer Scaling Tool for the customer
    to conduct his/her own compliance check for
    specific site conditions
  • Should also include option to calculate partial
    vapour pressures for complex mixtures/preps
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