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EU ETS CO2 Monitoring Stakeholders day

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12 May 2005 - Cologne-CL. 1. EU ETS CO2 Monitoring Stakeholders day. MONITORING AND REPORTING ... 12 May 2005 - Cologne-CL. 10. BIOMASS FRACTION. No method ... – PowerPoint PPT presentation

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Title: EU ETS CO2 Monitoring Stakeholders day


1
EU ETS CO2 Monitoring Stakeholders
day MONITORING AND REPORTING GUIDELINES
By Ir. Claude Loréa, CEMBUREAU Technical
Director Cologne
2
INTRODUCTION
  • The experience acquired by the European cement
    industry has shown that the monitoring and
    reporting principles defined in the Guidelines,
    are either technically not completely correct, or
    that their implementation would lead to
    unreasonably high costs.
  • The cement industry has established methods for
    the detection of relevant production and energy
    consumption data, which have been in use for a
    long time and in respect of which extensive
    experience is therefore available.

3
TIER CONCEPT
  • Dependent on the total volume of emissions from a
    plant. Subdivision into three groups (emissions
    of up to 50,000 t CO2/year, between 50,000 and
    500,000 t CO2/year and above 500,000 t CO2/year).
  • High specific CO2 emissions of the clinker
    burning process gt almost all installations fall
    under Tier 3, none under Tier 1.
  • Tier approach ambiguous and creates difficulties
    with national authorities when defining the
    reporting requirements.
  • Creates implementation problems and leads to the
    fact that comparable installations are not always
    treated equally.

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6
SAMPLING AND ANALYSIS MEASUREMENT ACCURACY
  • As a general comment, high requirements that do
    not bring any additional know-how.
  • Reference to accredited labs is superfluous (ISO
    17 025). Sufficient in-house experience. Avoid
    unnecessary testing.
  • Accuracy requirements can frequently not be
    maintained during LT operations.
  • Table 3 of the Guidelines ( 4.3.3.)
  • OK for process emissions and solid fuels
  • KO for waste fuels heterogeneity
  • 10 overall uncertainty should be applied in all
    cases

7
LEGISLATION CONCERNING MONITORING REPORTING
  • ET Directive, Art. 14 (1)
  • The guidelines shall be based on the principles
    for monitoring and reporting set out in Annex IV.
  • ET Directive, Annex IV (Principles MR)
  • Accepted emission factors shall be used.
    Activity-specific emission factors are acceptable
    for all fuels. Default factors are acceptable for
    all fuels except non-commercial ones (waste fuels
    such as tyres and industrial process gases).
  • Monitoring Reporting Guidelines 29/01/2004
  • National implementation

8
USE OF EMISSIONS FACTORS INSTEAD OF MEASUREMENTS
  • In conformity with Annex IV, determination of
    carbon content is only relevant for secondary
    fuels derived from waste.
  • Secondary fuels
  • if not sufficient data available gt determination
    of carbon content for every fuel on a annual
    basis on an average sample
  • secondary fuels used in larger volumes collect
    data available and process information
    statistically
  • plausibility tests, within the framework of
    verification
  • in the medium term, determine statistically
    robust emission factors (standard values).

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10
BIOMASS FRACTION
  • No method available for the time being
  • Methods described e.g. Netherlands are not
    adequate
  • CEN TC 343 first tests show the method does not
    prove to work
  • gt CEMBUREAU proposes to make calculations on the
    basis of fixed values

11
PROCESS EMISSIONS
  • Emission factor
  • specific standard emission factor.
  • measured emission factors possible. Measurements
    performed by plant laboratories, possibly
    combined with periodic analysis by external
    accredited labs.
  • Activity data
  • whatever the calculation method used (input or
    output based) cross check is necessary gt
    adjustments should be allowed.
  • once a year makes sense.
  • any corrections should be documented.

12
CORRECTIONS FOR CKD AND BY- PASS DUST
  • Assuming complete decarbonation leads to
    overestimation of CO2
  • Required accuracy cannot be met and
    representativeness is poor in relation to
    activity data
  • gt Simplified treatment of CKD is needed
  • use of kiln feed/ Clinker factor for the input
    based method
  • neglect CO2 emissions relating to CKD for the
    output based method

13
CONCLUSIONS
  • Need to amend MRG correct technical errors and
    reduce (measurements) requirements in order to
    improve cost-efficiency  
  • CEMBUREAU has developed recommendations based on
    the broadest possible application of established
    reporting methods, which have proven their worth
    over many years.
  • This shall give operators of cement plant support
    and contribute to the definition of uniform
    reporting requirements while maintaining the
    necessary flexibility.
  • MRG should be reliable, legally enforceable, but
    nevertheless practice-oriented CO2

14
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