ITU GREEN STANDARDS WEEK
17–21 September 2012
Paris, France
Training Session :
ITU-T Recommendation L.1420
Slide 1
What is L.1420 ? What is it for?
•
It is a Recommendation providing guidance on how to assess
environmental impacts of ICT in organizations.
– It has been built with a large number of representatives from the ICT sector and
governments. It deals with energy consumption and GHG emissions.
– It is in line with widely used international voluntary measuring and reporting
schemes.
• It complements ISO 14064-1 and the GHG Protocol.
•
This Recommendation covers:
– The assessment of the life cycle environmental impact of ICT Goods, Networks
and Services used by an organization (“Non-ICT organizations”)
– The assessment of the environmental impact of an ICT organization (“ICT
organizations”)
– The reporting of these impacts to ensure fair and transparent communications
Agenda
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•
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General Concepts
L 1420 For ICT organizations
L-1420 for Non-ICT organizations
Conclusions
Back-up information
• This presentation includes also information on how Alcatel Lucent
uses this methodology
Agenda
•
•
•
•
•
General Concepts
L 1420 For ICT organizations
L-1420 for Non-ICT organizations
Conclusions
Back-up information
Scope
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The assessment of the environmental impact of an ICT organization.
– An ICT organization is an organization, the core activity of which is directly
related to the design, production, promotion, sales or maintenance of ICT goods,
networks or services.
•
The assessment of the life cycle environmental impact of ICT Goods,
Networks and Services used by an non-ICT organization .
– Other organizations
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The interpretation of these impacts and their fair and transparent reporting
– Documentation is required
•
This Recommendation does not address GHG removals or rebound effects
– GHG removals for ICTs is not the highest priority
– Rebound effects are still under study
Scope
•
The Recommendation covers the 3 scopes:
– Scope 1 (Direct emissions): Activities owned or controlled by your organization
that release emissions straight into the atmosphere.
• Examples of scope 1 emissions include emissions from combustion in owned or
controlled boilers, furnaces, vehicles.
– Scope 2 (Energy indirect): Emissions being released into the atmosphere
associated with your consumption of purchased electricity, heat, steam and
cooling.
• These are indirect emissions that are a consequence of your organisation’s activities
but which occur at sources you do not own or control.
– Scope 3 (Other indirect): Emissions that are a consequence of your actions,
which occur at sources which you do not own or control and which are not
classed as scope 2 emissions.
• Examples of scope 3 emissions are business travel by means not owned or controlled
by your organization, waste disposal, or purchased materials or fuels.
•
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Assessment and reporting for scope 1 and scope 2 emissions are
mandatory.
Assessment and reporting for scope 3 emissions are optional
Principles
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Relevance
– Select GHG sources, data and methods appropriate to the assessment of the
GHG emissions of ICT activities and organizations.
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Completeness
– Include all specified GHG emissions that provide a material contribution to the
assessment of GHG emissions arising from products.
•
Consistency
– Enable meaningful comparisons in GHG-related information.
•
Accuracy
– Reduce bias and uncertainties as far as practicable.
•
Transparency
– The organization shall disclose the information sufficiently to allow a third party to
make decisions with confidence.
Agenda
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•
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•
General Concepts
L 1420 For ICT organizations
L-1420 for Non-ICT organizations
Conclusions
Back-up information
L-1420 for ICT organizations
• Setting the Organizational boundary
• Setting the Operational boundary
• Selection of quantification methodology
• Annual assessment/Establishment of a base year
• Recalculation of energy and GHG inventory
(restatements)
• Uncertainties
• Reporting
Setting the Organizational
boundary
•
The organizational boundaries should include all operations and
subsidiaries used by the organization according to the consolidation
approach
– The equity share approach – under which a company accounts for GHG
emissions from operations according to its interest in the operation.
– The control approach – under which a company accounts for 100% of the GHG
emissions from operations over which it has control. Control can be defined in
either operational or financial terms.
• The operational control approach – a company has operational control over an
operation if the company or one of its subsidiaries has the full authority to introduce and
implement its operating policies at the operation.
• The financial control approach – a company has financial control over an operation if
the company has the ability to direct the financial and operating policies of the operation
with a view to gaining economic benefits from its activities.
•
The Recommendation does not mandate any particular approach BUT the
chosen approach shall be the only applied approach.
Consolidation Approach
• In setting organizational boundaries and for corporate reporting of
consolidated GHG emissions ALU employs the “operational control”
approach in establishing organizational boundaries.
Alcatel Lucent
– Under this approach, ALU will account for 100 percent of GHG emissions from
operations over which it has operational control.
– Thus, ALU is not required to account for GHG emissions from facilities in which it
owns or leases, yet does not exert operational control.
• “Operational control” means that ALU has the full authority to
introduce and implement its operating policies at the operation.
– For leased facilities, “operational control” means that ALU has the ability to track
energy use and/or emissions from the lease (i.e., ALU pays the utility bills of the
leased facility).
– In addition, facilities which are leased by ALU and have been subleased by ALU
to tenants of which ALU does not have control of or responsibility for utility
payments, are not considered to be under the Operational Control of ALU.
Setting the Operational boundary
•
Establishing operational boundaries involves
– identifying GHG emissions and energy consumption associated with the
organization’s activities
– Categorizing them as direct or indirect
– Assigning the appropriate scope for accounting and reporting
•
Not always an easy task!!
Setting the Operational boundary
Alcatel Lucent
•
ALU has elected to include world-wide Scope 1, Scope 2 and Scope 3
activities within its operational boundaries, conducting emission
assessments of the following designated greenhouse gases: CO2, CH4,
N2O, HFCs, PFCs and SF6
Scope 1 Activities
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Facility Operations
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Stationary Source Fuel Combustion
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Alcatel Lucent
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Mobile Source Fuel Combustion
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Gasoline
Diesel
Ethanol
Liquified Natural Gas (LNG)
Compressed Natural Gas (CNG)
Liquified Petroleum Gas (LPG-Propane)
Jet Fuel
Other
Direct Emission of GHGs
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Distillate Fuel Oil (#1, #2 #4 and Diesel)
Residual Fuel Oil (#5 or #6)
Natural Gas
Propane
Coal Gas
Other
Refrigeration And Air Conditioning Equipment
Manufacturing, Laboratory or Product Development Operations
Fire Suppression Equipment
Corporate Function
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Mobile Source Fuel Combustion
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Owned/Leased Aircraft
Owned/Leased Vehicles
Owned/Leased Marine Vessels
Scope 2 Activities
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Facility Operations
Alcatel Lucent
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Electricity Consumption
Purchased Hot Water/Vapor Consumption
Purchased Chilled Water Consumption
Scope 3 Activities
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Purchased Goods & Services
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Fuel-and Energy-Related Activities Not Included in Scope 1 and 2
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Planned
Use of Sold Products
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Air Transport (Worldwide), Waterborne Craft Transport (Worldwide)
Processing of Sold Products
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Alcatel Lucent
Leased Vehicles and Facilities presently Assessed as Scope 1
Downstream Transportation and Distribution
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Employee Commuting (Worldwide)
Upstream Leased Assets
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Rental Cars (Worldwide), Rail (Worldwide), Air (Worldwide), Employee Personnel Vehicle Usage
(Worldwide)
Employee Commuting
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Energy Employed at Environmental Remediation Sites (United States), Energy Employed at Electrical
Equipment Recycling Facilities (United States)
Business Travel
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Air Transport (Worldwide), Waterborne Craft Transport (Worldwide)
Waste Generated in Operations
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Electric Transmission and Distribution losses
Upstream Transportation and Distribution
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Paper Purchase (Worldwide), Contract Manufacturing (Largest Suppliers), Contract Marine Vessels
Planned
End-of-Life Treatment of Sold Products
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Planned
Selection of quantification
methodology
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Selection or development of GHG emission factors
•
Calculation of GHG emissions as under
GWP factors for GHG taken from
IPCC Time frame of 100 years
Emission factors
•
According to L.1420, the organization shall select or develop emission
factors that :
– are derived from a recognized origin,
– are appropriate for the GHG source concerned,
– are valid at the time of quantification,
– take into account the quantification uncertainty and are calculated in a manner
intended to yield accurate and reproducible results, and
– are consistent with the intended use of the GHG inventory.
•
Except for GWP factors, no strict recommendations are made
– A lot of emission factors databases exist
• National : ADEME, DEFRA, US EPA
• International : IEA (International Energy Agency)
– May be a need for improvement, since companies will choose their own emission
factors sources, making comparisons relatively difficult and result consistency
challengeable
Emission factors
•
Emission Factors employed within the GHG Inventory Management System are:
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Alcatel Lucent
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USEPA Climate Leaders Greenhouse Gas Inventory Protocol Core Module Guidance
Electricity Emission Factors were obtained from the following sources:
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United States Source - eGRID EMISSION FACTORS
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Canada: CO2e factors from Canada's "National Inventory Report”
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Australia: Australian Greenhouse Office Factors and Methods Workbook
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UK: 2009 Guidelines to Defra/DECC's GHG Conversion Factors for Company Reporting
International Sources (unless noted otherwise):
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CO2: International Energy Agency, "CO2 Emissions from Fuel Combustion”
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CH4/N2O: International Electricity Emission Factors by Country
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International Energy Agency
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Intergovernmental Panel on Climate Change (IPCC)
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ALU will annually verify that references and emission factors are kept current
•
When updated emissions rates become available, the inventory will subsequently be
updated to reflect the correct emission rates for each year.
Alcatel Lucent
Example of calculation
•
Emissions associated with marine fleet operations are dependent upon the Fuel Type
and the volume of Fuel Used. Alcatel Submarine Networks Marine maintains a listing
of all owned vessels with associated fuel consumption. All GHG estimation
procedures are based on individual vessel assessments.
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Vessel: Lodbrog : 4,816 tonnes of Heavy Fuel Oil (HFO)
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Fuel Oil Density (kg/gal) : 3.75 (Residual Fuel Oil)
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Emission factors
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11.27 kg CO2/gallon
0.86 g CH4/gallon
0.30 g N2O/gallon
Calculation
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4,816,000 kg HFO/3.75 = 1,284,267 gallons HFO
1,284,267 gallons×11.27 = 14,473,689 kg CO2
1,284,267 gallons×0.86/1000 = 1,104 kg CH4
1,284,267 gallons×0.30/1000 = 385 kg NO2
Total = [14,473,689 +1,104 +385]/1000 = 14,616 tonnes CO2e
Data Collection
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Identify the relevant GHG activity data required under chosen GHG
quantification methodology.
•
Extract the data which is further required for GHG emission quantification.
– Facility usage rates of electricity, fossil fuels, purchased steam and chilled water
are obtained from invoices supplied by the service provider.
– Mobile fleet usage is tracked via the corporate fueling card account program
– Aircraft usage is tracked by the corporate travel agency
– Employee personnel vehicle usage during business travel is tracked via
corporate reimbursement activities.
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Put in place a data collection quality assurance!
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Define a document retention and control policy
– What do you do with data in electronic form?
– Disclosure policy to be set up
Alcatel Lucent
Data Collection
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Throughout the year each authorized Contributor will input applicable data into a webbased tool
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Facility usage rates of electricity, fossil fuels, purchased steam and chilled water are
obtained from invoices and/or bills of lading.
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Refrigerant loss records are determined from maintenance reports provided by
equipment service providers.
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Mobile fleet usage is tracked via the corporate fueling card account program.
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ALU’s corporate aircraft usage is tracked by Corporate Center personnel.
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Employee personnel vehicle usage during business travel is tracked via corporate
reimbursement activities.
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Records are to be retained on-site or stored at a designated location. At least
annually, the Climate Change Department will request copies of the facility usage
data.
Annual assessment / Base year
•
Assessments shall be carried out on an annual basis with the date of
publication of L.1420 as a reference.
•
However, a different base year could be chosen when:
– The organization estimates that the quantity and/or quality of available verifiable
data for this particular different year would guarantee a more accurate evaluation
of its GHG emissions and energy consumption.
– The organization has already put in place an assessment and reporting process
based on a different base year, compliant with this Recommendation.
– The activities carried out by the organization generate unusual fluctuations of
GHG emissions and/or energy consumption in such a way that the base year
might not be significant.
•
Any choice of a different base year shall be documented
Annual assessment / Base year
• Base Year
Alcatel Lucent
– The base year is 2008.
Recalculation of energy and
GHG inventory
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Applies under 2 circumstances:
– Structural changes which include mergers, acquisitions and divestments and/or
outsourcing or in-sourcing of GHG emitting activities.
– Discovery of significant errors contained within the base year emission
calculations which can necessitate a change in the emissions inventory.
•
L.1420 makes no recommendations as to what constitutes a “significant”
change and thus the need to adjust base year emissions
Recalculation of energy and
GHG inventory
•
Structural changes include mergers, acquisitions, and divestments and/or outsource
or in-sourcing of GHG emitting activities.
Alcatel Lucent
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Changes in the status of leased assets are considered structural changes.
•
Methodology changes include changes in activity data accuracy, changes in emission
factors, and/or changes in the methodology used to calculate GHG emissions.
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Alcatel Lucent defines a “Significance Threshold” requiring a change in the “base
year” emissions : if it results in a 5% change in total GHG emissions.
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Changes due to New Emission Factors:
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Changes due to Errors:
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The emission factors will be changed for each of the previous years as well as the current
one and the “base year”.
Should errors be identified and corrections to the “base year” emissions will be made.
Changes due to Data Accuracy and Availability:
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an adjustment to the “base year” emissions may be required.
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In such cases the Significance Threshold will be evaluated
Uncertainties
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An uncertainty assessment for GHG emissions and energy consumption
shall be performed in accordance with ISO 14064-1 clause 5.4 to the extent
needed to understand the inventory results.
– It is part of a broader learning and quality process
•
There are several type of uncertainties associated with GHG inventories
(scientific, estimation, parameter, model, statistical, systematic).
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Analyzing and quantifying some uncertainty aspects are extremely difficult
and likely beyond the scope of most organization’s inventory efforts
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At present, there is no precise guidance on how to address all uncertainty
related issues
Reporting
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The energy and GHG report content should contain:
– A description of the reporting organization and the person responsible the
reporting period or periods covered
– Documentation of organizational boundaries and operational boundaries
– A description of the quantification methodologies used within the framework of
the study
– The principles for collection of energy data, GHG activity data and emission
factors
– The results of the uncertainty assessment for GHG emissions and energy
consumption performed according to ISO 14064-1
– The results of energy consumption assessment and GHG emissions assessment
– Any recalculations including corrections of the corresponding clauses of the
previous report(s).
– A statement that the energy report and the GHG inventory report has been
prepared in accordance with the principles outlined in the Recommendation.
Alcatel Lucent
Reporting and other
management tools
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Alcatel Lucent provides a report in line with L.1420 Recommendation
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All documents will be retained indefinitely in electronic form. Hardcopy
versions of documents will be retained until goal year reporting is complete.
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The GHG Inventory reporting mechanism will be audited for compliance
with current protocols and guidance annually.
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A third-party validation/verification organizations to audit our inventory
management plan and greenhouse gas inventory program, annually.
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Corporate Climate Change Department to ensure that they have the
resources to establish, implement, maintain and improve this program.
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Training sessions are conducted annually to discuss program objectives
and requirements, including the goal and current progression towards the
goal year
Agenda
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General Concepts
L 1420 For ICT organizations
L-1420 for Non-ICT organizations
Conclusions
Back-up information
Recommendation L.1420
for Non-ICT organizations
• Evaluation of energy consumption and GHG impact
• Setting the Organizational boundary
• Setting the Operational boundary
• Selection of quantification methodology
• Annual assessment/Establishment of a base year
• Recalculation of energy and GHG inventory (restatements)
• Uncertainties
• Reporting
Slide 31
Evaluation of energy consumption
and GHG impact
•
For Non-ICT organizations, the methodology covers the use of ICT in any
kind of organization, including but not limited to organizations such as
banks, insurance companies and public administrations.
•
The evaluation of the life cycle energy consumption and GHG impact when
using ICT in organizations should be based
– on the Recommendation ITU-T L.1410 Part I and
– aggregated to an organizational level according to the principles outlined in this
Recommendation.
•
In a nutshell, you isolate your ICT-related activities from the rest of your
business!
Slide 32
Main differences with ICT
organizations’ requirements
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Setting the Organizational boundary
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Setting the Operational boundary
– Isolate the ICT-related part of the organization from the rest
– A list of equipment to be taken into account is given
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Selection of quantification methodology
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Annual assessment/Establishment of a base year
•
Recalculation of energy and GHG inventory
•
Uncertainties
•
Reporting
The other parts are
common to both types
of organizations
See Back-Up Slides
Slide 33
Agenda
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General Concepts
L 1420 For ICT organizations
L-1420 for Non-ICT organizations
Conclusions
Back-up information
Conclusions
•
This Recommendation is intending to help organizations to assess their
GHG emissions and energy consumption
•
This Recommendation is the unique standard (e.g. provided by an official
SDO) in this domain.
•
Nothing incredibly original – looks a lot like the GHG Protocol
– Main objective is to unify the various assessment methods, not to re-create the
wheel
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Several companies is in the act of checking the delta with their current
process
– Do we expect any big deviations ?
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Will certainly need improvements
– Nobody is perfect
– Sources of Emission factors
– Too complicated? Too flexible? Too rigid?
– ….
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Any feedbacks from other ITU Members and/or other stakeholders are
welcome and will improve the L.1420 Recommendation.
Thanks for your attention
Agenda
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General Concepts
L 1420 For ICT organizations
L-1420 for Non-ICT organizations
Conclusions
Back-up information
Scope 1
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It relates to the direct GHG emissions generated by facilities within its
organizational boundaries.
•
Direct GHG emissions are principally the result of the following types of
activities undertaken by the company:
– Physical or chemical processing. Most of these emissions result from
manufacture or processing of chemicals. It should be noted that this is applicable
to ICT to a limited extent.
– Transportation of materials, products, waste and employees. These emissions
result from the combustion of fuels in company owned/controlled mobile
combustion sources.
– Fugitive emissions. These emissions result from intentional or unintentional
releases such as SF6, equipment leaks from joints, seals, packing, and gaskets
during the use of refrigeration and air conditioning equipment, e.g. air
conditioning for data centers and making wafers.
– Combustion of fuels e.g. for power supply back-up of ICT goods and cooling of
ICT goods.
Scope 2
•
Scope 2 accounts for GHG emissions from the generation of purchased
electricity consumed by the company.
•
Purchased electricity is defined as electricity that is purchased or otherwise
brought into the organizational boundary of the company.
– For many companies, this represents one of the largest sources of GHG
emissions
– If the organization does not own the electricity lines, TD losses are not part of
scope 2
– Purchase of electricity for sale to end-user are not in scope 2.
Scope 3
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Scope 3 emissions are all of the indirect emissions that result from a
company’s activities that are not Scope 2 emissions.
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They represent emissions that occur in the life-cycle steps of a product or
process that occur before the company’s activities, such as those resulting
from the production and transport of raw materials.
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They also represent emissions that occur in the life-cycle steps of a product
after a company’s activities, such as from the transportation and use of
products, as well as the disposal of waste materials.
•
Trends in product use emissions must be interpreted carefully
– It could be hard to figure out a realistic way of accounting for the product use
– Not necessarily reflects the efforts made by the organization in reducing its
footprint
•
If an organization chooses to assess scope 3 GHG emissions, Appendix I in
the Recommendation lists categories that should be taken into account by
the organization when claiming compliance with this Recommendation.
Relevance
•
This means that it contains the information that report users—both external
and internal to the organization—consider significant and need for their
decision-making.
•
The selection of reporting boundaries for GHG emissions is an important
aspect of relevance.
– The accounting and reporting boundaries should appropriately reflect the GHG
emissions of the organization.
– The choice of appropriate boundaries depends on the characteristics of the
organization, the intended purpose of the GHG information, and the needs of the
users.
• organizational structures and operational boundaries
• The business context
• Specific exclusions or inclusions, which should be transparently identified and the
rationale provided.
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The boundaries should represent the substance and economic reality of the
business, and not merely its legal form.
Completeness
•
All emissions within the chosen organizational and operational boundaries
that are material to users should be reported to allow the reporting
organization’s emissions to be assessed.
•
In practice, a lack of data or the cost of gathering data may be a limiting
factor in the completeness of the inventory.
– When emissions have not been estimated, or have been estimated at an
insufficient level of quality to be included, the potential impacts and relevancy of
the exclusion should be transparently documented and explained.
•
The principle of completeness is not contradicting the possible exclusion of
negligible emissions.
– L.1420 allows their exclusion if an explanation is given as to why they are
excluded.
– if the totals of emissions that are excluded are not considered significant by the
users of the reported information, this should not be considered to be in violation
of the principle of completeness.
Consistency
•
Users of the report (and the organization itself!) may want to track and
compare GHG emissions information over time in order to identify trends
and to assess the performance of the reporting organization.
– The consistent application of boundary definitions, accounting practices and
calculation methodologies over time is essential for the production of comparable
GHG emissions data.
– The GHG information for all facilities within an organization’s reporting boundary
must be compiled in a manner that ensures that the aggregate information is
internally consistent and consistent over time.
– If there are changes in the scope, methods, data or any other factors affecting
emission estimates, they should be transparently documented and justified.
Accuracy
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As a means of promoting credibility in their reported emissions,
organizations should ensure accuracy in their emissions estimation process.
•
Data should be sufficiently accurate and precise to enable intended users to
make decisions with confidence.
– Because the intended uses of inventory data vary, the necessary level of
accuracy will also vary.
– Organizations should ensure that GHG measurements, estimates or calculations
are systemically neither over nor under the true emissions value, as far as
practicable.
•
Need to balance the cost-effectiveness of obtaining accurate emissions
estimates with the intended use for the emissions information.
Transparency
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Transparency relates to the degree to which information on the processes,
procedures, assumptions and limitations of the GHG inventory are
disclosed.
•
A transparent report will provide a clear understanding of the issues in the
context of the reporting company, and a meaningful assessment of
performance.
– Information should be reported in a clear, understandable, factual, neutral and
coherent manner.
– Any changes to the data, methods or other factors affecting a time series of
reported emissions should be transparently documented.
– Information on internal audits or external third-party reviews should be included
with the report.
– Information should be recorded, compiled and analyzed in a way that enables
internal reviewers and external verifiers to attest to its credibility.
Equity Share Approach
• Accounting for GHG emissions based on equity share is appropriate
for:
– Liability and risk management.
• GHG emissions accounting and reporting based on equity share provides a
more representative and complete picture.
• Therefore, it provides a realistic picture of liabilities and risks to
management, employees, shareholders.
– Situations where greater resources are available for conducting the
inventory.
• Reporting on the basis of equity share requires companies to obtain
information from other parties for operations they do not control.
– If this is not possible, they may need to estimate emissions from similar
operations for which they have data.
• In either case, costs may be expected to be greater than for calculating
emissions from sources under their operational control.
Operational Control Approach
•
Reporting based on the operational control approach is appropriate for:
– Performance tracking. Having operational control suggests a greater degree of
influence than merely holding a share of the equity.
– Situations where resources for inventorying emissions are limited.
• Reporting on the basis of operational control can be expected to be less costly than
reporting on the basis of equity share because the reporting company will, by definition,
have ready access to the data needed to estimate emissions.
Financial Control Approach
•
Reporting based on the financial control approach is appropriate for
alignment with financial accounting.
– Similarly to the equity share approach, the financial control approach results in
closer alignment between GHG accounting and financial accounting.
– It should be noted that the financial control boundary does not include some
arrangements that can be common in some industrial sectors.
• Petroleum sector
L-1420 for Non-ICT organizations
• Evaluation of energy consumption and GHG impact
• Setting the Organizational boundary
• Setting the Operational boundary
• Selection of quantification methodology
• Annual assessment/Establishment of a base year
• Recalculation of energy and GHG inventory (restatements)
• Uncertainties
• Reporting
Evaluation of energy consumption
and GHG impact
•
For Non-ICT organizations, the methodology covers the use of ICT in any
kind of organization, including but not limited to organizations such as
banks, insurance companies and public administrations.
•
The evaluation of the life cycle energy consumption and GHG impact when
using ICT in organizations should be based
– on the Recommendation ITU-T L.1410 Part I and
– aggregated to an organizational level according to the principles outlined in this
Recommendation.
•
In a nutshell, you isolate your ICT-related activities from the rest of your
business!
Setting the Organizational
boundary
•
The organizational boundaries should include all operations and
subsidiaries used by the organization according to the consolidation
approach
– The equity share approach – under which a company accounts for GHG
emissions from operations according to its interest in the operation.
– The control approach – under which a company accounts for 100% of the GHG
emissions from operations over which it has control. Control can be defined in
either operational or financial terms.
• The operational control approach – a company has operational control over an
operation if the company or one of its subsidiaries has the full authority to introduce and
implement its operating policies at the operation.
• The financial control approach – a company has financial control over an operation if
the company has the ability to direct the financial and operating policies of the operation
with a view to gaining economic benefits from its activities.
•
The Recommendation does not mandate any particular approach BUT the
chosen approach shall be the only applied approach.
Setting the Operational boundary
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Identify emissions related to…
– design, production and use of ICT goods and associated support equipment
present in the organization.
– design and production of ICT associated consumables present in the
organization.
– software and ICT services purchased by the organization concerned.
– disposal of all ICT goods present in the organization, disposal of consumables
(e.g. worn cartridges or waste paper) and end of life associated with software
and ICT services purchased by the organization.
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A list of ICTs is given in the Recommendation
List of ICTs to be considered
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Desktops;
Laptops;
Cathode Ray Tube (CRT) screens;
Flat screens;
Individual printers;
Cables;
Network printers and copiers;
Servers, switches and routers;
Fax machines;
Scanners;
Fixed phones;
Mobile phones;
Personal Digital Assistants (PDA) and tablets;
Projectors;
Videoconference installations;
Televisions;
Cooling systems for ICT goods;
Other small ICT goods;
Outsourced ICT goods, in particular outsourced datacenters;
ICT-Dedicated Power supply back-up generators.
Setting the Operational boundary
•
Emission sources including the following activities (in scope 3) may also be
considered:
– daily commute to work and business travel of Information Technology (IT)
department staff.
– freight of purchased ICT goods entering the organization.
– freight of ICT goods within the organization premises.
– and freight of ICT goods leaving the organization’s premises when
decommissioned.
•
Data ordinarily comes from invoices, reports for corporate reimbursement
activities, estimated energy usage and applied emission factors…
•
For each of the three scopes (if all covered) the selected emission sources
shall be clearly described and documented.
Selection of quantification
methodology
•
Selection or development of GHG emission factors
•
Calculation of GHG emissions as under
GWP factors for GHG taken from
IPCC Time frame of 100 years
Emission factors
•
According to L.1420, the organization shall select or develop emission
factors that :
– are derived from a recognized origin,
– are appropriate for the GHG source concerned,
– are valid at the time of quantification,
– take into account the quantification uncertainty and are calculated in a manner
intended to yield accurate and reproducible results, and
– are consistent with the intended use of the GHG inventory.
•
Except for GWP factors, no strict recommendations are made
– A lot of emission factors databases exist
• National : ADEME, DEFRA, US EPA
• International : IEA (International Energy Agency)
– May be a need for improvement, since companies will choose their own emission
factors sources, making comparisons relatively difficult and result consistency
challengeable
Data Collection
•
Identify the relevant GHG activity data required under chosen GHG
quantification methodology.
•
Extract the data which is further required for GHG emission quantification.
– Facility usage rates of electricity, fossil fuels, purchased steam and chilled water
are obtained from invoices supplied by the service provider.
– Mobile fleet usage is tracked via the corporate fueling card account program
– Aircraft usage is tracked by the corporate travel agency
– Employee personnel vehicle usage during business travel is tracked via
corporate reimbursement activities.
•
Put in place a data collection quality assurance!
•
Define a document retention and control policy
– What do you do with data in electronic form?
– Disclosure policy to be set up
Annual assessment / Base year
•
Assessments shall be carried out on an annual basis with the date of
publication of L.1420 as a reference.
•
However, a different base year could be chosen when:
– The organization estimates that the quantity and/or quality of available verifiable
data for this particular different year would guarantee a more accurate evaluation
of its GHG emissions and energy consumption.
– The organization has already put in place an assessment and reporting process
based on a different base year, compliant with this Recommendation.
– The activities carried out by the organization generate unusual fluctuations of
GHG emissions and/or energy consumption in such a way that the base year
might not be significant.
•
Any choice of a different base year shall be documented
Recalculation of energy and
GHG inventory
•
Applies under 2 circumstances:
– Structural changes which include mergers, acquisitions and divestments and/or
outsourcing or in-sourcing of GHG emitting activities.
– Discovery of significant errors contained within the base year emission
calculations which can necessitate a change in the emissions inventory.
•
L.1420 makes no recommendations as to what constitutes a “significant”
change and thus the need to adjust base year emissions
Uncertainties
•
An uncertainty assessment for GHG emissions and energy consumption
should be performed in accordance with ISO 14064-1 clause 5.4 to the
extent needed to understand the inventory results.
– It is part of a broader learning and quality process
•
There are several type of uncertainties associated with GHG inventories
(scientific, estimation, parameter, model, statistical, systematic).
•
Analyzing and quantifying some uncertainty aspects are extremely difficult
and likely beyond the scope of most organization’s inventory efforts
•
At present, there is no precise guidance on how to address all uncertainty
related issues
Reporting
•
The energy and GHG report content should contain:
– A description of the reporting organization and the person responsible the
reporting period or periods covered
– Documentation of organizational boundaries and operational boundaries
– A description of the quantification methodologies used within the framework of
the study
– The principles for collection of energy data, GHG activity data and emission
factors
– The results of the uncertainty assessment for GHG emissions and energy
consumption performed according to ISO 14064-1
– The results of energy consumption assessment and GHG emissions assessment
– Any recalculations including corrections of the corresponding clauses of the
previous report(s).
– A statement that the energy report and the GHG inventory report has been
prepared in accordance with the principles outlined in the Recommendation.