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Various elements of standardisation are possible: - Deemed additionality, penetration rates, global benchmarks, default factors, minimum
levels of service, statistical databases, omission of negligible sources of emissions, assumptions on usage patterns, aggregated default leakage, etc.
Benefits…- Conservative default assumptions replace data collection, can unlock specific project
types for which the determination of a baseline is cumbersome- Increased simplicity and decrease of transaction costs => greater mobilisation
including small-scale
Risks…- Environmental integrity - Achieving standardisation can be costly (data gathering)
Development and operationalisation of standardised approaches requires resources and coordination
- Selection of most appropriate project types and methodological concepts- Awareness-raising and capacity-building of project developers, NGOs and DNAs
Guidelines (GL) SBL (EB 62): - Sector coverage: Transport is not covered- GL provides on a very high-level definitions and procedures- EB understanding of SBL seems to be limited to default factors/benchmarks- The GL does not provide methodologies, and content of GL is only a fraction of
required methodological work- Practical questions are not addressed
- How will the Board (or the submitting DNA?) determine and justify benchmark level and based on which criteria (transparency, conservativeness, etc)?
- What about methodology elements not addressed in the GL (e.g. applicability project emissions, leakage, etc)
- How do (or will) SBL relate to existing methodologies (will they simply replace BL/additionality elements of existing methodologies)
- If not, who is responsible for developing the “missing” elements for a full practically implementable methodology?
Procedures (EB 63, consideration)- Only applicable for DNA submissions and based on GL, approved meth or tool- New form for submission of SBLs- What are the criteria for assessment of adequacy of the SBL?