Standardized Approaches An overview Anja Kollmuss, head of consulting [email protected] Content • Framing the issue • Main points of standardization • Learning from existing experience.

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Transcript Standardized Approaches An overview Anja Kollmuss, head of consulting [email protected] Content • Framing the issue • Main points of standardization • Learning from existing experience.

Standardized Approaches
An overview
Anja Kollmuss, head of consulting
[email protected]
Content
•
Framing the issue
•
Main points of standardization
•
Learning from existing experience
2
Context: Keeping warming below 2°C
About 75% probability, if cumulative CO2 emissions between 2000-2050 are kept
below 1000 gigatons of CO2 and comparable reductions are made in non-CO2
GHGs.
45
40
BAU (2010 - 2030)
Annual CO2 emissions (GTCO2)
35
350ppm pathway (2010 - 2050)
30
Recent emissions (1900 - 2009)
25
20
15
10
5
0
1990
2000
2010
2020
2030
2040
2050
Figure shows recent emissions (1990 – 2009), our “representative 350 ppm pathway “ (2010 – 2050) and, for comparison, business-asusual pathway that’s consistent with the International Energy Agency’s standard “no climate policy” projections.
Source: Sivan Kartha, SEI
http://sei-us.org/publications/id/309
Context: Where are we at?
Consumed between 2000-2009:
nearly one-third of the 2°C budget
(330 out of 1000 gigatons CO2)
Global emissions currently about
50 gigatons CO2e per year
Expected CERs 1.4 gigatons
Remember: CDM currently zero sum
Source: Sivan Kartha, SEI
http://sei-us.org/publications/id/309
We need…
• Scaling-up mitigation
• Building and preserving capacity for post 2012 mechanisms
• Going beyond offsetting: beyond zero-sum
New
Better
Bigger
Ensure environmental integrity
Ensure equity between rich and poor
Improve efficiency: e.g. reduce transaction costs
Ensure attractiveness for investors
Improve regional and sectoral distribution
….
The lofty goals of standardization
Improved efficiency: e.g. reduce transaction costs and streamline
procedures for project implementation
Greater objectivity, consistency and predictability at project
implementation stage.
Reduced transaction costs at project implementation stage 
reducing barriers for project implementation
Improved regional and sectoral distribution  access to
underrepresented areas (e.g. LDCs) and sectors (e.g. transportation
and buildings)
 Ensured environmental integrity and attractiveness for
investors
What can be standardized?
Offset Programs
• Baseline emissions and/or
• Additionality determination and/or
• Certain parameters for project emission calculations
Standartization can also be used in other contexts (e.g.
allowance allocation, voluntary programs)
Terms, definitions, types
Term
Definition
Examples
Standardized
approaches
Catch all term that includes
performance related standards and
non-performance related approaches.
• Non-performance standard:
e.g. ‘not mandatory by law’;
• e.g. ‘does not generate non-carbon
related revenue’
• Performance related:
examples below
Benchmark or
Emission rate/intensity per unit of
output, input, or throughput or
market penetration rate
• Emissions rate:
0. 8 tons of CO2 per ton of cement
Performance
standard
Applied to baseline and/or
additionality determination
• Market Penetration rate:
Technology penetration of less than
20%
Default Values
Used to calculate baseline and/or
project emissions
• IPCC 2006 Guidelines
• 98% methane flare efficiency
Positive Lists
Usually a technology specific list that
deems all projects of that technology
additional.
• Agricultural methane destruction
• Small scale hydro
• Solar PV
The underlying rationale is usually
performance based
Terms, definitions, types
Term
Definition
Examples
Standardized
approaches
Catch all term that includes
performance related standards and
non-performance related approaches.
• Non-performance standard:
e.g. ‘not mandatory by law’;
• e.g. ‘does not generate non-carbon
related revenue’
• Performance related:
examples below
Benchmark or
Emission rate/intensity per unit of
output, input, or throughput or
market penetration rate
• Emissions rate:
0. 8 tons of CO2 per ton of cement
Performance
standard
Applied to baseline and/or
additionality determination
• Market Penetration rate:
Technology penetration of less than
20%
Default Values
Used to calculate baseline and/or
project emissions
• IPCC 2006 Guidelines
• 98% methane flare efficiency
Positive Lists
Usually a technology specific list that
deems all projects of that technology
additional.
• Agricultural methane destruction
• Small scale hydro
• Solar PV
The underlying rationale is usually
performance based
Project-based vs standardized approaches
Project Based
Standardized
Can take project specific conditions
into account (e.g. baseline,
monitoring, additionality).
Common standards applied to all
projects of a given type.
More subjective project evaluation
More objective project evaluation
Subjectivity during the design phase
of the performance standard. (e.g.
decisions on stringency levels)
Typically project specific
additionality tests (e.g. investment
and barriers analysis)
Additionality of a project easily
determined
Expensive and time consuming for
project developers and Evaluators
Costly to design
Simplified, more transparent and
streamlined project approval process
Key Points
Subjectivity is not eliminated, but shifted from project
registration process to the baseline setting stage.
Who decides?
Risks: One off decision, difficult / costly to reverse
Gaming with standard setting can lock in too lenient baselines /
non-conservative parameters
Key Points
Cost is not lowered but shifted from project developer /
project stage to standardization stage.
Who pays?
Data collection and analysis USD 1.7-6.3 million
Design of Performance Standard: USD 0.3-0.7
million
Are the ones who pay the ones who decide on stringency?
Much detailed data is necessary. Who will ensure reliability of such
data? Who will pay to collect the data?
How will the data be checked for accuracy and conservativeness?
Cost estimates taken from: Hayashi, D., N. Müller, S.
Feige and A. Michaelowa (2010). "Towards a More
Standardized Approach to Baselines and
Additionality Under the CDM." Perspectives Climate
Change, May 2010.)
Key Points
Can efficiency and environmental integrity really be
improved?
Average intensity
Output
Non-normal
distribution of
BAU generation
emission intensity
Emission intensity (tCO2 / t output)
Average intensity
Output
BAU generation
Free riders
Emission intensity (tCO2 / t output)
Key Points
Can efficiency and environmental integrity really be
improved?
Output
BAU generation
Additionality benchmark
and crediting baseline
Uncredited
Reductions
Benchmarkinduced
generation
Credited
Reductions
Free riders
Emission intensity (tCO2 / t output)
Additionality
Additionality threshold
Crediting baseline
Plant A: project emissions intensity
lower than additionality threshold
 receives credits up to baseline
Plant B: project emissions intensity
higher than additionality threshold
 receives no credits
BAU intensity
higher than
crediting baseline
Plant C: project emissions intensity
higher than additionality threshold
 receives no credits
Plant D: project emissions intensity
lower than additionality threshold
 receives credits up to baseline
BAU intensity
lower than
crediting baseline
Plant E: No project activity,
BAU emissions intensity lower
than additionality threshold
 receives credits up to baseline
No change
from BAU
intensity
= emission intensity
reductions due to
project activity
= awarded credits
= project emission intensity
= BAU emission intensity
Emission intensity (tCO2 / t output)
17
Lessons learned from existing standardizations
1. CDM
2. JI
3. Climate Action Reserve
Experience under the CDM
Large, concentrated emission sources
ACM13: Efficient fossil power generation
–
–
21 projects in pipeline since 2007 (mostly in China and India, where
data is readily available)
Benchmark emissions: top 15% power plants (same fuel)
NM302: Cement sector
–
Methodology in evaluation since 2009
–
CSI database offers a great potential for scaling up
–
Challenge in determination of benchmark stringency levels
Small, dispersed emission sources
AM70: Efficient refrigerators for households
– Average of top 20% of performers
– No project since 2008 due to heavy data requirement
NM328: Whole-building energy efficiency and fuel switch
– Methodology in evaluation since 2010
– Data requirement may become extensive
Performance Standards under JI
Example: N2O abatement in Nitric and Adipic Acid Production
• Baseline emissions benchmark:
– nitric acid: 1.85 or 2.5 kg of N2O per t of nitric acid.
– adipic acid: 90% abatement
 avoid risk of leakage
CAR Lessons Learned
• To maintain environmental integrity,
standardized baselines may need to be
conservative
• Use of standardized assumptions, emission
factors, and parameters may lead to inaccuracy at
the project level
• Protocols generally compensate by adopting
conservative assumptions, factors, parameters
CAR Lessons Learned
• Standardized protocols work better for some project
types than for others
• Standardized baselines are more difficult with complex
systems, where performance is subject to multiple
drivers, or where multiple baseline alternatives are
possible (e.g., forestry!)
• All protocols rely on project-specific details and
parameters to some degree
CAR Protocol Development
1. Internal research and scoping
2. Kick-off/scoping meeting
3. Multi-stakeholder workgroup formation
4. The Reserve drafts a protocol
5. Draft protocol considered by workgroup
–
Provides technical expertise and practitioner experience
–
Period meetings and individual consultation when needed
6. Revised draft released for public comment
7. Public workshop
8. Final version adoption by Reserve board in public
session
Questions, questions, questions...
•
•
•
•
•
•
What data is available?
What should the stringency be?
Who should pay for what?
Which sectors should be targeted?
Who should develop standardized methodologies?
What role will DNAs play?
 What is the goal of standardization?
And who decided what the goals should
be?