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<1>
MRV Demonstration Study (DS) using a Model Project 2012
Final Report
「Energy Saving through Building Energy Management System
(BEMS)」
(implemented by PricewaterhouseCoopers)
Study Partners Department of Alternative Energy Development and Energy (DEDE),
PricewaterhouseCoopers Thailand Azbil Corporation Mitsubishi UFJ Lease & Finance Company Limited Bright Management Consulting Co.,Ltd
Location of Project/Activity
Bangkok (Thailand)
Category of Project/Activity
Energy Efficiency Improvement
Description of Project/Activity
The objective of the project is to develop a measurement, reporting and verification approach for total energy consumption of a commercial building using a Building and Energy Management System (BEMS) and manage the operation of energy-consuming equipment to reduce both energy consumption and CO2 emissions. Using past energy consumption data as a baseline, data analysis allows identification of possible reductions in CO2 emission through an assessment of potential energy conservation measures. These are subsequently used to establish default values. Actual data on CO2 emissions following introduction of a BEMS is collected and evaluated, based on total building energy consumption. In Thailand’s metropolitan Bangkok area, this project is targeting four categories of building: hotels, offices, hospitals, and shopping centers. Activities under this project started in 2012 following on from the original study started in 2011. The project aims to achieve reductions in emissions in 12 cases achieving a total reduction of 11,538t CO2 per year.
Eligibility Criteria Case 1: BEMS shall be installed into existing buildings Case 2: Reduction of energy consumption shall be made by the operation and control of equipment and facilities by BEMS according to the indoor environment, not just upgrading equipments Case 3: The result of performance improvement shall be reported regularly (at least once every six months) by BEMS provider to beneficiaries of energy saving e.g. building owners after the introduction of BEMS, and this is secured by contracts
Reference Scenario and Project/Activity Boundary
With regard to reference scenarios, the following 2 scenarios are used:
・Scenario 1: it is Business as Usual (BaU) with the current situation
continuing with no introduction of BEMS
・Scenario 2: buildings become highly efficient as a result of non-BEMS
effects The rationale behind Scenario 1 is that there are almost no cases of BEMS introduction in Thailand and the current situation, where there are limited economic incentives for BEMS introduction, is assumed to continue. Scenario 2 is set based on the assumption that buildings will be more
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efficient than BaU as a result of non-BEMS effects. This scenario is
based on the “Energy Efficiency Development Plan (2011-2030)”
published by Ministry of Energy in Thailand.
Calculation Method Options
Default Values set in Methodology
Working from the assumption that the statistical analysis of default values results in the selection of conservative values, an assessment of commercial building energy efficiency was performed to understand the status of facility operation and energy consumption in Thailand. The results of this assessment were used in the determination of default values. In Thailand, there are a limited number of cases of BEMS introduction with no cases of BEMS being installed for a long period of time. As a result, the assessment tries to define quantitative and manageable defaults (percentage efficiency improvement of energy usage) by collecting information on past energy consumption of the whole building and detailed information on the building operation with an analysis of energy conservation following introduction of the BEMS. The effects of introduction a BEMS include energy savings resulting from operational improvements (intangible) and from automatic control and upgrade of energy consuming equipment (tangible). Operational improvements result from identification of energy saving opportunities and implementation of appropriate measures to realize these opportunities. Data output from the BEMS facilitates identification of aspects of energy consumption and facility operations that have not been previously been recognized and areas where operational performance can be improved leading to identification of energy saving opportunities. Automatic control of equipment enables the optimal operation of energy-consuming equipment resulting in energy saving. Additionally, energy saving benefits can be realized with the replacement of existing equipment with higher efficiency models.
Monitoring Method Energy Usage of a Building after the Introduction of BEMS
Result of Monitoring Activity
To create monitoring reports and verify the trial MRV, energy consumption monitoring was performed at four sites where BEMS's have been installed. The building owners or facility managers were asked to collect data after introduction of the BEMS.
Possible to obtain past three years data required for the calculation
Use the same sets of data after the project
Calculation
Method 3)
Use default value
for the efficiency
improvement factor.
Calculation
Method 1
Calculation
Method 2
Use original
efficiency
improvement factor
which set by project
operator
YES
YES
NO
NO
YES
YES
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Monitored Buildings Building Sector Monitoring Period
Building A Hotel
April 1, 2012 to October 31, 2012 (7 months)
Building B Commercial Facilities
May 1, 2011 to December 31, 2011 (8 months)
Building C Office January 31, 2010 to January 31, 2011 (12 months)
Building D Commercial Facilities
January 1, 2009 to November 31, 2011 (23 months)
GHG Emissions and its Reductions
GHG Emission and Reduction Building Total
Floor Area (m
2)
Reference Emission (t-CO2)
Reduction in Emission (t-CO2)
Percentage Reduction in Emission by
BEMS
Building A
67,562 4,995 524 Implemented at 10.5%
Building B
213,311 27,917 6,554 Implemented at 10.5%
Building C
9,952 1,693 18 Implemented at 1.1%
Building D
27,886 49,349 5,335 Implemented at 10.8%
Method and Result of Verification
Results of Verification Building Verified
Reduction in Emission
[t-CO2]
Results of Verification
Building A 524 1st Verification: The calculation is appropriate. It was pointed out that the source material for the individual technologies of the introduced BEMS was not clearly written.
Building B 2,931 1st Verification: Data was not properly entered or calculated. Modification was requested. 2nd Verification: Calculation was appropriate. CAR was resolved by correct data entry.
Building C 18 1st Verification: Calculation was not performed for a suitable monitoring period. Modification was requested. 2nd Verification: Calculation was appropriate. CAR was resolved through correct data entry. It was pointed out that there was lack of documentation justifying the introduction of individual technologies for the BEMS and information on the precision of actual LPG measurement.
Building D 5,329 1st Verification: Data was not properly entered or calculated. Modification was requested. 2nd Verification: Calculation was appropriate. CAR was resolved through correct data entry.
Environmental Impacts
The environmental impacts of the manufacture of BEMS systems are considered to be lower than other products. Similarly during the overall life cycle of a BEMS, the potential for increased environmental impacts e.g. release of hazardous chemicals, pollution etc is considered to be very low.
Promotion of Three key requirements are identified to support the successful
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Japanese Technology
introduction of Japanese technology: Strong business relationships with real-estate agents, developers, and construction consultants to gain entry to the local market; raising the capacity of Japanese manufacturers so that low-cost financing schemes becoming a viable option for the local market, and training BEMS operators.
Sustainable Development in Host Country
Introduction of BEMS acts as a driver to for reduction in peak power consumption, supports energy efficiency related technology transfer and human resource development, and contributes to reducing environmental pollution. These benefits are in line with the current Thai mid-term development policy and strategy.
MRV DS Report in 2012
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Study Title: MRV Demonstration Study using a Model Project
“Energy Conservation with a Building and Energy Management
System (BEMS)”
Study Entity: PricewaterhouseCoopers
1.Study Implementation Scheme
PricewaterhouseCoopers: Overall control of the project, creation of an MRV
methodology, MRV negotiation, evaluation of reduction effects
PricewaterhouseCoopers Thailand (Cooperative Organization/Subcontractor):
Selection of a verification authority, summarizing the results of verification,
identification of potential cases, arranging interview with public authorities
Azbil Corporation (Cooperative Organization/Subcontractor): The lead company of
2011 New Mechanism Feasibility Study. In cooperation with Azbil Thailand, the
principal tasks include collecting building data, arranging demonstrations,
introduction and demonstration of BEMS's and collection/measurement of MRV
data.
Mitsubishi UFJ Lease & Finance Company Limited (Cooperative
Organization/Subcontractor): In cooperation with Bangkok Mitsubishi UFJ Lease,
the principal tasks include arranging demonstrations, assistance in
collection/measurement of MRV data, and evaluation of financial feasibility.
Third Party Verification Entity(Bright Management Consulting Co. Ltd)
(Subcontractor): As a third party verification entity in Thailand, the principal tasks
include verifying reduction in GHG emission based on the MRV methodology
proposal and providing feedback on the verification results.
2.Overview of Project/Activity
(1) Description of Project/Activity Contents:
The objective of the project is to measure total energy consumption of a commercial building
using a Building and Energy Management System (BEMS) and manage the operation of
energy-consuming equipment to reduce energy usage and CO2 emissions. Using past energy
consumption data as a baseline, possible reductions in CO2 emission are estimated by
assessing potential energy conservation measures. These are subsequently used to determine
default values. Actual data on CO2 emissions following introduction of a BEMS is collected
and evaluated based on total building energy consumption.
In Thailand’s metropolitan Bangkok area, this project is targeting four categories of building:
hotels, offices, hospitals, and shopping centers. Activities under this project started in 2012
following on from the original study started in 2011. The project aims to achieve reductions in
emissions in 12 cases achieving a total reduction of 11,538t CO2 per year.
(2) Situations of Host Country:
There has recently been a significant increase in energy-originated CO2 emissions from the
commercial building sector in Thailand. This is leading to increased interest in energy saving
amongst building owners. Local companies are also voluntarily working on ESCO projects
and energy conservation.
The new Thai administration inaugurated in 2011 announced a proactive energy policy as part
of its inaugural policy speech. The administration expressed a positive attitude towards the
MRV DS Report in 2012
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introduction of energy saving systems, the promotion of energy saving in buildings, and the
active use of CDM as measures to reduce electricity consumption by 25% in the next 20 years.
A Japan-Thailand summit held in March 2012 issued a joint communiqué regarding
cooperation between the two countries on the bilateral offset credit mechanism (BOCM). For
the bilateral offset credit mechanism, the Thailand Greenhouse Gas Management
Organization (TGO) currently serves as a contact and is in negotiations with the Japanese
government.
The current Thai regulatory framework for energy saving policies is based around the Energy
Saving Promotion Law (1992). The process of reporting on the energy usage of commercial
buildings and facilities has raised awareness of energy consumption levels and associated
costs. This acts as a driver for reduction of both energy consumption and energy related
expenses. To promote energy saving initiatives, the Thai government has established an
ESCO fund as a mechanism to provide support and preferential treatment for energy saving.
Additionally, tax incentives are in place to promote energy efficiency in private sector
buildings and factories.
(3) Complementarity of the CDM:
The purpose of this study is to promote energy saving of commercial buildings through the
introduction of BEMS leading to reductions in CO2 emissions. In CDM, the AMS-II.E.,
Energy efficiency and fuel switching measures for buildings is a methodology for reducing
building energy consumption. The methodology targets energy saving projects such as BEMS
control and equipment replacement. However, there are a number of issues, discussed below,
when implementing projects that control and replaces many pieces of equipment in a building.
In the first place, CDM requires calculation of total reduction in emissions from equipment
related energy saving for each piece of equipment. In a registered project using the AMS-II.E
methodology, baseline and project energy usage are calculated for each piece of equipment
that will be installed in the building to estimate the reduction in emissions from the building.
The reduction calculation requires collecting data regarding a large number of parameters that
are specific to each piece of equipment. As a result, once the project starts, it is necessary to
conduct monitoring for numerous parameters and emission calculations. Therefore, the CDM
methodology places a significant burden on the participants and requires a complicated
verification procedure. Additionally, the CDM methodology (based on calculating energy
saving for each piece of equipment) might not capture the additional energy saving obtained
by the management and control of the entire building using a BEMS as an emission in
reductions. For example, when controlling both lighting and air conditioning, reduction of
lighting time with a BEMS results in a decrease in heat generated in the room and a
subsequent reduction in energy consumption for air conditioning. The synergistic effects of
energy saving between various types of equipment is not be included a methodology which
targets only the individual components (without the considering the whole system).
Secondly, energy saving activities using a BEMS includes both benefits from equipment
replacement and improvements in operational efficiency as a result of BEMS introduction.
However, the CDM might not recognize the latter efforts, or energy savings resulting from
operational improvements made by humans, as a reduction in emissions. In Japan,
measurement of energy usage and equipment operation using a BEMS promotes energy
conservation through operational improvements. It is difficult in the CDM, including
AMS-II.E to include such energy saving efforts into a reduction in emissions. However,
Japanese companies have significant “know-how” on how to achieve operational
MRV DS Report in 2012
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improvements in energy efficiency through operation of a BEMS such as from operator
training, maintenance, and data analysis support. The effects of energy saving with a BEMS
are increased by including operational improvements which creates opportunities for Japanese
companies to capitalize on their knowledge.
For the above reasons, promoting energy saving with a BEMS at JCM/BOCM can
complement the CDM. It can greatly contribute to reducing CO2 emissions from the
commercial sector, a significant source of emissions in developing countries. Energy
conservation with a BEMS can be applied to countries other than Thailand. Creating an MRV
methodology through this study promotes energy saving and emission reduction in many
countries.
(4) Initial Investment for the Model Project:
The initial investment estimated based on the 2011 New Mechanism Feasibility Study is
1,304 million yen for 12 buildings.
The table below lists the results of a trial calculation of the cost of disseminating BEMS's
including running cost such as maintenance for different rate of introduction.
Initial Investment and Cost of Reducing CO2 Emissions at Buildings in Bangkok 20 Buildings per
Year
50 Buildings per
Year
100 Buildings per
Year
Initial Cost (million yen) 2,173 5,433 10,867
Annual Emission Reduction (t-CO2) 19,230 48,075 96,150
Emission Reduction per 10 Years (t-CO2) 192,300 480,750 961,500
Running Cost per 10 Years (million yen) 200 500 1,000
CO2 Reduction Cost (yen/t-CO2) 12,342 12,342 12,342
3. Contents of the Study
(1) Issues to be Addressed in the Study:
Creation of an MRV Methodology
- Macro Analysis (DEDE Data): For the regular notification under the Energy Saving
Promotion Law in Thailand, the data for fiscal 2011 needs to be requested from
DEDE.
- Creating Defaults (DEDE Seminar): DEDE has proposed co-hosting a seminar. It
is necessary to negotiate the details, obtain approval from DEDE, and make
preparations.
- Creating Defaults (Questionnaires): Development of Questionnaires to be
completed by building owners and equipment managers has been started. It is
necessary to collect the results and understand the needs on energy saving control by
sector in Bangkok.
- Creation of an MRV Methodology: An MRV methodology should be established
with third party verification to conduct trial verification at sites where BEMS's have
been installed.
- Harmonization of the MRV Methodology and the Ministry of Environment
Proposal: Creation and development of an MRV methodology should be discussed
with the study subcontractor of the Ministry of Environment project (Mitsubishi UFJ
Research and Consulting)
- Energy Saving Diagnosis for Creating Defaults and MRV Methodology: Energy
saving analysis is being performed to quantitatively understand and verify the effects
MRV DS Report in 2012
<8>
of introducing a BEMS. Approximately 40 analyses are planned before submission of
the final report.
- Demonstration of BEMS Introduction: Collection of actual data from BEMS at
commercial facilities participating in the demonstration study is required. This data
will be used to confirm differences with the results of the energy saving analysis.
Conservative percentage efficiency improvement (defaults) should be set for BEMS
introduction based on the energy saving analysis.
Monitoring
- Obtaining Monitoring Data and Checking Its Storage: It is necessary to check the
data and evidence regarding energy usage and operation to confirm that it can be
measured reliably and easily, and the actual state of data storage. It is also required to
assess whether it can be measured and calculated by the facility manager.
- Checking the Accuracy of Monitoring Data: It is necessary to study the measuring
instruments and methods used for actual measurement of energy usage, etc. in
Thailand to understand required accuracy.
Third Party Verification
- Readiness to Verification: It is necessary to check that the local managers are ready
to respond to the requests made by the Thai verification entity during the verification
conducted based on the JCM/BOCM Verification Manual.
- Feasibility of Verification: It is necessary to check whether it is possible to conduct
local verification based on the JCM/BOCM Verification Manual and provide
feedback on any improvements in using the manual.
(2) Measures Implemented to Resolve Issues Identified in the Study: Field Study
- 1st Field Study: The staff visited the Department of Alternative Energy
Development and Efficiency (DEDE), a Thai government agency, to explain and
request cooperation on the MRV model demonstration project, and to ask them to
provide data from regular notifications under the Energy Saving Promotion Law.
They also visited financial institutions and private enterprises to explain and request
cooperation on the project.
- 2nd Field Study: The staff held a planning meeting with the local subcontractors.
They also visited the DEDE to discuss the details of the DEDE seminar planned for
October. Site surveys were conducted to understand the types of energy-consuming
equipment in commercial buildings in Bangkok, check the monitoring of energy
usage, etc., identifying emission sources, and conducting field hearings on
conformance to the Energy Saving Promotion Law in Thailand. The objective was to
determine the feasibility of the MRV and applicability of the methodology proposal.
- 3rd Field Study: A seminar was prepared and presented by PwC, sponsored by GEC
and DEDE. The purpose of the seminar was to invite companies who wish to receive
energy saving analysis and participate in the development of the defaults.
Discussions with a third party verification entity were held to confirm the terms of
contract and contents of the tasks.
- 4th Field Study: Verification by the third party verification entity was prepared and
implemented. Interviews were conducted with the DEDE and the Thai Green
Building Institute (TGBI). Discussions with the local subcontractors were held to
confirm the progress.
Creation of an MRV Methodology
- Macro Analysis (DEDE Data): The data from regular notifications in fiscal 2011
MRV DS Report in 2012
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under the Energy Saving Promotion Law was obtained from the DEDE. This was
used to assess the energy usage trend in four commercial sectors and specifications
such as total floor areas of the buildings. Based on this data, an analysis of CO2
emission units was performed.
- Creation of Defaults (DEDE Seminar): For the purpose of creating defaults, DEDE
held a seminar to invite companies who wish to receive an energy saving analysis.
160 persons applied and 103 persons attended. A total of 51 companies (offices,
hotels, commercial facilities, and hospitals) participated.
- Creating Defaults (Questionnaires): 275 buildings were selected from the targets of
the Energy Saving Promotion Law. For the buildings that responded, energy saving
analysis was arranged for creating defaults.
Numbers of Questionnaire Sent and Collected
Sector Sent Collected
Office 148 30
Commercial Facilities 21 10
Hotel 74 16
Hospital 32 10
Total 275 66
- Creation of an MRV Methodology: Based on the field studies, an MRV
methodology was created through a monitoring feasibility study based on the Energy
Saving Promotion Law in Thailand.
- Harmonization of the MRV Methodology and the Ministry of Environment
Proposal: Two discussions were held with the study subcontractor of the Ministry of
Environment project (Mitsubishi UFJ Research and Consulting) to exchange views
on the creation and development of an MRV methodology and related information.
The results of the discussions were reflected in the proposed methodology.
- Energy Saving Analysis for Creating Defaults and MRV Methodology: 23 results
were obtained as of the end of December for the quantitative analysis of energy
saving and to verify the benefits of introducing a BEMS. The analysis will be
conducted until the submission of the final report. A total of approximately 40
analyses are expected to be collected.
- Demonstration of BEMS Introduction: The collection of data on BEMS
demonstration at commercial facilities that are the targets of demonstration study
started in late December.
Monitoring
- Monitoring Data and Checking Its Storage: The data and evidence of energy
usage and operational information that can be measured reliably and easily, and the
actual state of storage were checked, and summarized as monitoring data.
- Checking the Accuracy of Monitoring Data: The applicable standards for
measuring instruments used for the actual measurement of energy usage, etc. in
Thailand were studied. This required referral to the Thai Industrial Standard (TIS).
Third Party Verification
- Readiness to Verification: Four sites were investigated based on the JCM/BOCM
Verification Manual to check that the local managers are ready to respond to the
requests made by Thai verification entity during the verification.
- Feasibility of Verification: Investigations were conducted based on the JCM/BOCM
Verification Manual. The feasibility of local verification and improvements on using
MRV DS Report in 2012
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the manual will be summarized through the discussion with the verification entity.
4. Results of MRV Demonstration Study
(1) GHG Emission Reduction Effects by the Implementation of Project/Activity:
In this study, the BEMS refers to the systems comprised of measurement/metering
components, control systems, monitoring systems and data saving/analysis/diagnosis
components etc. In regard to the buildings in the commercial sector etc., this refers to the
systems that are used to understand the indoor environment/energy consumption status as well
as opportunities to reduce energy consumption through operation control for components and
systems, optimized for each indoor environment. BEMS used only for measurement are not
included in the context of the current report as they do not contribute to the direct reduction of
emissions.
The introduction of BEMS in Japan has resulted in a 12.4% energy saving and 10.3%
reduction in CO2 emissions (Analysis of Energy Saving Rate of Total (BEMS) Subsidiary
Entities from 2005 to 2008 by NEDO). In the 2011 New Mechanism Feasibility Study, a field
study was conducted at commercial buildings in Thailand, and it was confirmed that energy
saving and emission reduction similar to Japan were feasible.
For emission reductions, the importance of the operation after BEMS introduction became
evident, as well as the introduction of BEMS technology that is suitable for the Thai climate.
The methodology was created based on the principles that BEMS technology could be used to
maximize emissions reduction, support dissemination of Japanese technology, a simple
method or a range of methods that can be selected according to the actual status, and emission
reduction could be rationally calculated. The following table shows the points of creation.
Points of Creating an MRV Methodology Points Reflection to the Methodology Proposal
Promotion of BEMS The methodology does not include the size of a building so that many buildings can be
the candidates.
Promotion of energy saving and
emission reduction with BEMS
The methodology targets offices, commercial facilities, hotels, and hospitals for which
large effects of introducing BEMS can be expected.
A flexible calculation method is prepared so that defaults can be defined based on the
efforts and achievements by the project participant.
Methodology with easy
calculation
Creation of defaults (percentage emission reduction by BEMS introduction) is
considered.
If defaults are used, monitoring items can be calculated only with the energy usage
following the start of the project (after BEMS introduction).
The required data is energy usage of the entire building, which can be collected from
evidence including power company bills and actual measurement at BEMS.
Appropriate reflection of
energy saving efforts by the
project proposer
In addition to the calculation method that uses the defaults generating conservative
reduction, the project includes a method that is based on operational information such
as past energy usage and total floor area and calculates emission reduction based on
the actual energy saving.
Maintenance and continuation
of energy saving and emission
reduction with BEMS
Maintenance of the operational and management structure after the introduction of
BEMS is required.
Rational calculation method The project targets only existing building and not new buildings that have no past data
that can be used for calculating reference emission.
(2) Eligibility Criteria for MRV Methodology Application:
The MRV eligibility criteria establish three conditions (positive list).
MRV DS Report in 2012
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Case 1: BEMS shall be installed into existing buildings
The project only targets existing buildings as for newly built buildings it is not possible to
estimate the reference emissions based on past emissions and the defaults (percentage energy
usage efficiency improvement after BEMS introduction) cannot be described.
Case 2: Reduction of energy consumption shall be made by the operation and control of
equipment and facilities by BEMS according to the indoor environment, not just
upgrading equipments Measurement of energy usage following BEMS introduction and energy saving through the
control of equipment and devices are the target of the project so that additional energy saving
is available. Energy conservation with only measurement is not considered as it is usually
conducted for cost reduction as opposed to emissions reduction.
Case 3: The result of performance improvement shall be reported regularly (at least
once every six months) by BEMS provider to beneficiaries of energy saving e.g. building
owners after the introduction of BEMS, and this is secured by contracts
It is often the case that only introducing a BEMS does not lead to longer term energy saving
and emissions reduction. Regular checks of energy saving performance and implementing
countermeasures are required to maximize the benefits of BEMS implementation. After
introducing BEMS, the BEMS provider should report semi-annual energy consumption and
propose measures to improve performance. The contract with the provider should include
clauses requiring the provision of operator training, data management services, and
analysis/evaluation reports.
Satisfying the above eligibility criteria is expected to result in additional CO2 emission
reductions in Thailand given the current conditions and experience in use of BEMS.
Condition 3 states provision of maintenance after the introduction of BEMS and support of
data utilization, which are strong points of Japanese companies. Inclusion of Condition 3
promotes the dissemination of Japanese BEMS technology.
(3) Calculation Method Options:
The following chart indicates the flow for selecting a calculation method option.
MRV DS Report in 2012
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Calculation Method Option Selection Flow
* The data required for calculation includes collection of energy consumption data for the past
three years and total floor area, the energy consumption and total floor area after project
launch, and the operating rate of the facility (in case of an office or commercial facility).
Calculation Method 1 is based around the use of default values. This approach uses energy
consumption of the entire building following introduction of the BEMS in combination with
the percentage efficiency improvement achieved following its introduction and the percentage
efficiency improvements of individual technologies.
Calculation Method 2 also relies on the energy consumption of the whole building following
introduction of the BEMS but replaces the default values approach used in Method 1 with
actual percentage of efficiency improvements achieved in similar buildings from the use of
similar technology.
Calculation Method 3 is based on the actual energy usage of the building, past energy
consumption, total floor area, and operation rate.
(4) Necessary Data for Calculation:
For each calculation method option, the information/data required for the calculation of GHG
emissions are summarized in tabular format below. The table lists the information/data
required for setting defaults and the information/data to be monitored after start of the project.
It also describes the status of information/data preparation in the project.
Information/Data Required for Calculating GHG Emissions Information/Data Monitoring (M)/Business
Specific Value Setting
(S)/Default Value Setting
Status of Preparation
Electric Power Usage of the Target
Building (kWh)
M (Calculation Methods 1, 2,
and 3)
Monthly electricity bills have been collated. In
many cases, data for three years is available.
Fossil Fuel Usage of the Target
Building (kl, t, or 1000Nm3/y)
M (Calculation Methods 1, 2,
and 3)
Possible to obtain past three years data required for the calculation
Use the same sets of data after the project
Calculation
Method 3
Use default value
for the efficiency
improvement factor.
Calculation
Method 1
Calculation
Method 2
Use original
efficiency
improvement factor
which set by project
operator
YES
YES
NO
NO
YES
YES
MRV DS Report in 2012
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Total Floor Area (m3) M (Calculation Method 3) The building certification application is stored in
many cases, allowing copies of the application
form to be made available.
Percentage Operating Area (%) M (Calculation Method 3) Lease contract
Percentage Energy Usage Efficiency
Improvement after the Introduction
of individual facilities (%)
D (Calculation Method 1)
-
Percentage Energy Usage Efficiency
Improvement by Building Type EMS
D (Calculation Method 1)
-
CO2 Emission Factor of Electric
Power (tCO2/MWh)
S (Calculation Methods 1, 2,
and 3)
Monitoring by the local facility manager is
possible based on Thailand Energy Statistics
2011 by DEDE.
NCVi,y: Net Caloric Value of fossil
fuel I (GJ/Nm3, t, etc)
S (Calculation Methods 1, 2,
and 3)
The factor for the calculation under the Energy
Saving Promotion Law in Thailand can be used
as the default. Default (fixed value) such as IPCC
was used.
EFf,i,y: CO2 Emission Factor of fossil
fuel I (tCO2/GJ)
S (Calculation Methods 1, 2,
and 3)
Same as above
(5) Default Value(s) Set in MRV Methodology:
The MRV process for emission reduction is streamlined by setting as defaults the energy
saving results of building where BEMS are introduced. In other words, introduction of BEMS
improves the efficiency of the entire building, and using those values as defaults, allows
reference emissions to be calculated. (Reference emissions can be calculated by dividing the
amount of emission after BEMS introduction by the default.)
This approach works from the assumption that conservative default values can be determined
from statistical analysis. Defaults were derived through data collection and detailed analysis
of energy savings associated with facility operation and energy consumption in commercial
buildings in Thailand. There are not many examples of BEMS being introduced in Thailand
with no cases of a BEMS being installed for a significant period of time. This study analyzed
energy consumption of the whole building and the resulting energy savings following from
BEMS introduction. It was thought that performing multiple analyses would result in the
generation of quantitative and reliable defaults (percentage energy usage efficiency
improvement).
Energy saving resulting from BEMS implementation includes the effects of operational
improvements, automatic control of facilities, and equipment replacement. Operational
improvements results from the effective use of the facilities by humans. BEMS allows the
measurement and collection of information on energy consumption and facility operations
that have not been previously available allowing identification of areas where people can
improve operations, resulting in energy savings. Changes in human behavior, the effects of
automatic control and equipment replacement allow for the optimal operation of facilities
thereby maximize energy efficiency. The study conducted energy saving analysis on BEMS
technology to investigate and quantify reductions.
The figure below shows the breakdown of energy saving by the introduction of BEMS. First,
it evaluates percentage efficiency improvement by equipment replacement. Then, it calculates
percentage efficiency improvement from BEMS control. Finally it considers the percentage
efficiency improvement resulting from operational improvements (human factors).
MRV DS Report in 2012
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Breakdown of Percentage Efficiency Improvement by BEMS Introduction
Determination of defaults for operational improvements requires data generated from BEMS
implementation in Thailand. As this is not possible at this stage, based on experience gained
from Japan, the default for operational improvement is provisionally set to 1%. This value
should be modified to reflect the actual circumstances in Thailand using data that becomes
available following installation of BEMS. Examples of operational improvements for offices
that can be implemented in Thailand are shown in the list below.
Percentage Energy Usage Efficiency Improvement by Operational Improvement by Sectors
Energy Usage Efficiency
Improvement
1%
Operational Improvements (Office)
■Air Conditioning
- Turning off air conditioners and exhaust fans in areas not used and when not required (Reduction in time of air conditioning
and exhaustion)/Education on and execution of temperature setting for power saving
- Effective use of shades to prevent entrance of heat through the windows
- Regular cleaning of filters
- Use of pipe friction reducer
■Lighting
- Turning off lights when not required (Reduction in lighting time)
- Removing some lighting (i.e. fluorescent tubes, lighting bulbs) near the windows and in the corridors with consideration
given to illumination levels.
- Turning off lights during a lunch break.
■Others
- Energy saving enlightenment posters, energy consumption display, etc. for raising awareness
- Establishment of a energy saving committee consisting of division representatives with an intention of making energy
saving efforts by all residents in the building, and regular discussions for full dissemination of energy saving activities
- Turning off PCs, copy machines and other office equipment, drink servers, and vending machines when not required.
- Partial operation of escalators and elevators during off-peak hours
- Limitation and management of electrical apparatuses using outlets
Example of Operational Improvement at an Office
Percentage Energy Usage Improvement by Automatic Control of Facilities and Facility
Replacement Purpose Individual technologies of
BEMS
Content Average
Percentage
Improvement
(Tentative)
Standard
Deviation
Number of
Samples
1. Lighting
1.1. Replacement with
high-efficiency lighting
(LED)
Replacement with LED
lighting
3.0 % 1.56% ~4.43%
23
Before After
Percentage Efficiency
Improvement (%)
Introduction of BEMS
(3)
(2)
(1)
(3) Percentage efficiency improvement by operational refinements such as changing operations (%)
(2) Percentage efficiency improvement by BEMS control (%)
(1) Percentage efficiency improvement by equipment replacement (%)
Percentage efficiency improvement should be considered in the order:
(1) → (2) → (3)
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1.2. Operation control of
lighting
Scheduled control, human
sensors, etc,
0.2 % 0.05% ~0.40%
10
2.
Heat Source
2.1. Optimal operation
control of heat sources
Control of number of units,
optimal start control, primary
pump inverter control, etc.
2.1 % 1.47% ~2.75%
28
2.2. Introduction of
high-efficiency chillers
Replacement with
high-efficiency chillers
6.8 % 3.83% ~9.70%
11
2.3. Optimal operation
control of cooling water
Cooling water variable flow
control, cooling tower
start/stop control, cooling
tower fan inverter control,
cooling water temperature
optimization, etc.
2.7 % 1.64% ~3.83%
28
2.4. Transfer pump variable
flow control
Secondary pump inverter
control
2.1 % - 9
3.
Air
Conditioning
3.1. HVAC outside air
intake control
CO2 concentration control 1.0 % - 6
3.2. Variable air flow air
conditioners
Fan inverter control 2.4 % 1.07% ~3.72%
15
3.3. Power save operation
(intermittent operation)
Intermittent operation control 1.5 % 0.40% ~2.59%
11
3.4. Power saving
temperature setting
Proper indoor temperature
setting
1.0 % - 7
3.5. Replacement with
high-efficiency Packaged
air conditioners (PAC)
Replacement with
high-efficiency PAC
17.2 % - 2
4.
Ventilation
4.1. Operation control of
ventilation fans
CO concentration control,
scheduled control, device
coordination control
0.7 % - 4
Business specific values used include the calorific value of fuel, fuel emission factors and
electric emission factor. For the calorific value, the specific value of the Energy Saving
Promotion Law by the DEDE is used with the IPCC value used for the fuel emission factor
and the value from the Thai Greenhouse Gas Management Organization (TGO) used as the
basis for the electric emission factor.
(6) Setting of Reference Scenario and Project/Activity Boundary
With regard to reference scenarios, the following 2 scenarios are used:
- Scenario 1: it is Business as Usual (BaU) with the current situation continuing with
no introduction of BEMS
- Scenario 2: buildings become highly efficient as a result of non-BEMS effects
The rationale behind Scenario 1 is that there are almost no cases of BEMS introduction in
Thailand and the current situation, where there are limited economic incentives for BEMS
introduction, is assumed to continue. In Thailand, due to the low energy costs, even if BEMS
that perform highly optimized equipment operation are introduced, the resulting cost saving
from the reduction in energy consumption will be very small with the investment payback
period (including running cost) longer than compared to Japan. The investment payback
period following introduction of BEMS is around 7 to 10 years which means that the
investment is not attractive to building owners. In terms of the applicability of subsidies,
according to DEDE, there are no plans to introduce subsidies for BEMS and it is assumed that
BEMS introduction will not be promoted in near future.
Scenario 2 is set based on the assumption that buildings will be more efficient than BaU as a
result of non-BEMS effects. For example, emission reduction and energy saving will be
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greater than BaU as a result of improvements in the efficiency of building facilities and
factors such as the use of higher performance building insulation. It can be assumed that in
the case that a BEMS is not installed but building energy efficiency increases, at the time of
BEMS introduction, the potential level of energy saving resulting from BEMS introduction
will be lower than compared to the current status and BaU. This scenario is based on the
“Energy Efficiency Development Plan (2011-2030)” published by Ministry of Energy in
Thailand. This plan establishes the policy direction to make buildings highly efficient by
focusing on installation of high efficiency building facilities and improving the performance
of insulation materials.
Diagram below demonstrates the two scenarios in commercial buildings. The assumption is
that the total number of commercial buildings in Thailand will increase with a resulting
increase in total emission levels. Although this project only targets existing buildings, new
buildings can be re-categorized as existing buildings once required energy usage data can be
collected. Therefore, it is assumed that the total number of buildings where BEMS can be
introduced will be increased.
Scenario 1, as BaU, shows that the current emission levels will continue. For scenario 2, if the
building that is set as reference emission becomes highly efficient, the amount of emission
will be increased but the rate of increase will be lower than that experienced with BaU. If
BEMS are introduced using the JCM/BOCM mechanism as a project, it is assumed that
project emission will remain below the reference scenario.
Reference scenario
If the reference scenario is set based on the above graph, for the quantification of emission
reduction resulting from the introduction of BEMS using the JCM/BOCM mechanism, the
following changes need to be implemented:
- Periodic modification of default values
- Periodic monitoring of emissions intensity of building in the commercial sector
The reason why periodic modification of default values is required is that the introduction of
BEMS and other improvements in building energy efficiency over a period of time will result
in higher levels of energy efficiency performance compared to the performance levels
identified in 2013. This means that the original default values will not represent actual
performance levels if they are not periodically modified.
To modify default values, it is necessary to collect data on the actual energy saving value for
each technology following BEMS introduction. As this process takes time and potentially
incurs cost, consideration should be given to establishing a subsidy system at the start of
BaU
Reference emission
Project emission
GH
G E
missio
n in
com
me
rcial b
uild
ing
s
2013
Introduction of BEMS
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JCM/BOCM introduction. Qualification for receipt of the subsidy should include the
requirement to collect data on energy consumption by individual technologies. The modified
default values will be used in calculation method 1 stated in section 4.
It is recommended that periodic monitoring of emission intensity in commercial buildings is
carried out every 3 years by JCM/BOCM participants. Systematic monitoring of
improvements in building energy efficiency buildings will generate data that can be used in
Calculation method 3, which uses past energy consumption data in determining emission
reductions following introduction of BEMS.
As an example, if the emissions from commercial buildings in Thailand have increased as
shown in diagram above, use of the conservative reference emission approach requires
incorporation of monitoring data to correct the reference emission value reflecting reductions
in emissions resulting from 5 years of implementation of BEMS. Although it is not easy to
monitor specific emission intensity values in commercial buildings in Thailand, it would be
possible to judge the required correction by statistically analyzing reporting data collected
under the Energy Saving Promotion Act.
The system boundary was set to cover the entire building as BEMS typically monitor and
control buildings as a whole. The advantages of adopting this system boundary include
potentially larger reduction in emissions and efficient MRV. Large reductions resulting from
operational improvements and synergies achieved from the automatic control of multiple
devices, and some spillover effects (e.g. reduction in air-conditioning costs following
renovation of illumination and upgrading of heat insulation) are captured with the whole
building approach. Additionally, the approach cuts down on the cost of monitoring and
verification by collectively measuring the consumption of electric power and fuel in the
whole building.
The target greenhouse gas is CO2 generated from energy consumption. The reason for this is
that most greenhouse gas emitted from the facilities in the commercial sector in Thailand is
energy-originated CO2. Buildings in Bangkok (Thailand) meet 90% of required energy
consumption from electricity. Therefore, it is important to place the emphasis on electric
emission sources. Electric usage is measured with meters controlled by the Metropolitan
Electricity Authority in Bangkok and the Provincial Electricity Authority in other areas.
(7) Monitoring Methods:
The table below shows the results of monitoring that was planned based on the calculation
method options in 4 (3).
The facility manager confirmed that it is possible to monitor the items listed in the table below.
This is because the items listed are the same as those in the Energy Saving Promotion Law in
Thailand and the facility manager was familiar with data summarization and calculation.
Notification under the Law is required two times per year meaning that monitoring is
conducted at the same period and intervals, which can reduce the burden of the person in
charge of monitoring.
For the purpose of reducing monitoring cost, use of actual measurement data with BEMS was
considered. TIS is a standard on the accuracy of measuring instruments in Thailand, which is
equivalent to JIS in Japan. TIS defines the accuracy of measuring instruments and criteria for
inspection. TIS 1030 specifies the inspection standard for measuring instruments. TIS 2336
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provides the specifications for accuracy and classes of measuring instruments. TIS 1030 is
based on international standards such as IEC, and revised in 2008. TIS 2026 was revised in
2009. If measuring instruments such as power meters used for BEMS are procured from local
Japanese manufacturers, the instruments conform to these standards and generally no problem
occurs. If there is a problem, this could be due to measuring instruments supplied from
non-Japanese manufacturers and use of old measuring instruments for maintenance purposes
in existing buildings connected to BEMS. However, considering the necessity of transmitting
measurement data to BEMS, measuring instruments will need to be upgraded or new
equipment installed, so this should not be a problem. However, use of existing instruments or
simple and cheap instruments from local manufacturers may result in inaccurate data. It is a
basic principle that when configuring BEMS, the measuring instruments should be replaced
with high-precision models.
Items Monitored Monitoring
Frequency
Notification
Requested by
the Energy
Saving
Promotion
Law
Feasibility
PECy: Electric Power Usage of the Target Facility
during the Project (MWh/y)
Once/6 months ○ According to the Thai
Accountants Law, heating and
lighting bills must be stored for
five years.
Many facility management
divisions store and manage those
bills to conform to the Energy
Saving Promotion Law.
For total floor area, there is a
building certificate application to
Bangkok Metropolitan
Government Office. Therefore,
the information on relatively
many facilities is stored in the
management division.
PFCi,y: Fossil Fuel Usage of the Target Facility during
the Project (kl, t, 1000Nm3/y)
Once/6 months ○
REC3y: Average Electric Power Usage of the Target
Facility in the Past 3 Years (MWh/y)
Only at project
planning
RFCi,3y: Fossil Fuel Usage of the Target Facility in the
Past 3 Years (kl, t, 1000Nm3/y)
Only at project
planning
RAG3y: Average Floor Area of the Building in the Past
3 Years (m2)
Only at project
planning ○
ROR3y: Percentage Operational Area in the reference
(%)
Only at project
planning
PAGy: Total Floor Space of the Building during the
Project (m2)
Once/year ○
PORy: Percentage Operational Area of the Building
during the Project (%)
Once/year
EERk: Percentage Energy Usage Efficiency
Improvement after the Introduction of an Individual
Piece of Equipment k Independent from Building Type
(%)
Once/year - (default)
EERi: Percentage Energy Usage Efficiency
Improvement by EMS of Building Type j (%)
Once/year
EFe,y: Electric Power CO2 Emission Factor
(tCO2/MWh)
Once/year
NCVi,y: Net Calorific Value of Fossil Fuel i (GJ/Nm3, t,
etc)
Once/year
EFf,i,y: Fossil Fuel CO2 Emission Factor (tCO2/GJ) Once/year
(8) Quantification of GHG Emissions and its Reductions:
The table below shows the reference emission and emission reduction calculated based on the
MRV methodology from the CO2 emissions at each MRV demonstration site. The emission
reduction is as of the preparation of the first monitoring report. The verification process
checks the emission reduction achieved to determine whether the calculation is appropriate.
The CO2 emission factors used were based on the Energy Saving Promotion Law data by
DEDE. It does not link with the emission factor obtained from the reference emission
calculated based on the MRV methodology of this study, and total floor area.
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The percentage emission reduction after BEMS introduction is from the early stage
implementation of verification on percentage reduction using the values under study, which is
usually done with the default assumed to be available according to the JCM/BOCM system.
The current defaults are tentative values.
MRV Demonstration Sites Building Total Floor
Area (m2)
Reference
Emissions
(t-CO2/y)
Emission
Reduction
(t-CO2/y)
Percentage
Emission
Reduction after
BEMS
Introduction
Monitoring Period
Building A 67,562 4,995 524 Implemented at
10.5%
April 1, 2012 to October 31, 2012 (7
months)
Building B 213,311 27,917 6,554 Implemented at
10.5%
May 1, 2011 to December 31, 2011 (8
months)
Building C 9,952 1,693 18 Implemented at
1.1%
January 31, 2010 to January 31, 2011
(12 months)
Building
D
27,886 49,349 5,335 Implemented at
10.8%
January 1, 2009 to November 31,
2011 (23 months)
For the emissions and reduction of greenhouse effect gas, reference emissions are set based on
the emissions during the project, with actual differences during the project considered as
emission reductions. (See the attached methodology proposal). Emissions that may result
from “leakage” are not taken into consideration because of the whole building system
approach which includes all energy-consuming equipment controlled by the BEMS falls in
the boundary.
(9) Verification of GHG Emission Reductions:
The table below is a summary of trial MRV verification. The verification entity was
requested to conduct on-site reviews and desk-top reviews. Two types of calculation methods
can be executed for the MRV methodology depending on the provision of monitoring data
from the project participants. Since there are few cases where BEMS have been introduced in
Thailand and it is impossible to obtain actual values, Calculation Method 2 was not selected.
However, the basic concept of calculation is similar to Calculation Method 1. Therefore, it is
possible to conduct evaluation by verification of Calculation Method 1.
Trial Verification Building Verification Type Date of Execution
(Date of Submitting the Monitoring
Report)
Date of Submitting the
Verification Report
Building A On site review
Calculation Method 1
November 26, 2012 December 7, 2012
Building B Desk-top review
Calculation Method 1
1st Verification: November 30, 2012
2nd Verification: December 12, 2012
December 17, 2012
Building C Desk-top review
Calculation Method 3
1st Verification: December 3, 2012
2nd Verification: December 12, 2012
December 17, 2012
Building D Desk-top review
Calculation Method 1
1st Verification: December 4, 2012
2nd Verification: December 12, 2012
December 17, 2012
For the on-site review of Building A, the verification entity confirmed the monitoring report
was created based on the evidences of electric, LPG, and light oil usage, and checked the
equipment. It was also confirmed that the calculation was appropriate without any problem.
However, they pointed out that the source document for the optimal control of heat sources by
the BEMS introduced was not clearly written.
For Building B, data was entered into the monitoring report based on the evidences of electric
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and LPG usage. During the first verification, the receiving power meter failed after the
introduction of BEMS, and needed to be replaced. However, the electric usage including the
period of meter failure was entered in the monitoring report, which was found by the
verification entity. The entity pointed out that the period after the meter was replace during
which monitoring was reliable should be taken as the monitoring period after BEMS
introduction and it should be the target of calculation. The staff followed this instruction
because emission reduction is small and conservative calculation was made. In the 2nd
verification, the calculation was confirmed to be appropriate.
Electric bills and actual LPG measurement data were provided in Building C. They were
entered in the monitoring report and verified. In the 1st verification, modification of the
monitoring period was requested. A point in time where individual technology was introduced
was taken as the introduction of BEMS. At the point where BEMS was introduced
(monitoring started), all individual technology must have been introduced. This was fixed
before the 2nd verification and the calculation was confirmed to be appropriate. They pointed
out that there is not enough documentation for the introduction of individual technology and
to determine the accuracy of LPG measurement.
For Building D, the monitoring report was created based on the evidence of electric usage and
verified. During the 1st verification, the power consumption of the pumps used for the
cafeteria and temporarily used pumps outside the area of BEMS control was entered as the
power usage after BEMS introduction and used for calculation. In the 2nd verification, the
monitoring report was fixed and the calculation was confirmed to be appropriate.
The issues revealed by the verifications include: 1) Clarification of the ranges of management
and measurement by BEMS, 2) Setting the BEMS project start date, 3) Monitoring assistance
tools, 4) Creation of a verification check list, and 5) Need for on-site reviews.
For 1), it is necessary to classify the energy usage for each purpose in case of composite
facilities (e.g. commercial facilities and a hotel in a single building) and clarify the scope of
management by BEMS. However, this requires a large number of source documents and time
for site checking. Regarding the second point, this is explained by the need for “system tuning” following introduction of BEMS to reach the optimal operating conditions. When installing
BEMS, several pieces of technology are generally introduced in stages, not as a single batch.
Therefore, it is necessary to define the actual date when BEMS was introduced. Data should
be presented to support selection of the actual date e.g. work reports created on the date of
tuning. For 3), creating and distributing tools to support monitoring report preparation by
project participants may reduce the likelihood of errors in data entry and summation. For 4), it
is important to create a checklist summarizing the points of verification before hand so that
the verification entity can efficiently conduct verification based on the BEMS methodology.
The checklist is effective for keeping quality. With reference to 5) on-site review should be
conducted by default as this allows a better understanding of energy consumption, and checks
on the accuracy and location of individual meters.
(10) Ensuring Environmental Integrity:
It is thought that the environmental risks that occur during the production of BEMS products,
in other words, the environmental impacts due to the dissemination of BEMS, are not high
compared to other products. Similarly, the general life cycle of BEMS from introduction, to
installation and operation does not cause result in significant environmental issues.
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Thailand enacted the Enhancement and Conservation of National Environment Quality Act in
1992. Environmental assessment must be conducted for the target projects. There are 23 target
projects including the construction of dams, reservoirs, and airports for civil uses.
Introduction of BEMS during the stage of construction or renewal is no the target of
environmental impact evaluation.
(11) How to Promote the Dissemination of Japanese Technologies:
Comments from local real-estate agents and construction companies identified three key
points that Japanese companies and the government should take into consideration when
introducing and disseminating Japanese BEMS technology.
The first point to consider is the "retention of local users." As a characteristic of the social
infrastructure market, Large scale equipment and device including BEMS are difficult to
replace. (Once a supplier acquires clients, other companies cannot supply to those clients.)
For the market of existing buildings, equipment, and devices, Japanese electrical
manufacturers in Thailand pointed out "it is not easy to enter the market occupied by leading
European companies."
For Japanese companies, which are new entries, to acquire users in such a situation, they
should: 1) develop "new business" and "new markets," 2) demonstrate the superiority of their
equipment and devices to clients and let them experience them, and 3) design products and
services whose prices and performance are targeted to the needs of local clients.
For 1), the real-estate agencies in Thailand recommended to approach the developers and
chain operators of major commercial facilities, targeting "newly built commercial facilities"
with understanding of the trend of open air markets converted into shopping malls. For 2) and
3), it was pointed out the need for strengthening sales efforts to local construction consultants
who influences the design stage, as well as the building owners and trustees of management
and operations.
Secondly, the local users should be able to access the low-cost finance schemes. In emerging
countries including Thailand, "price matching" indicated in above 3) is required. However, the
lowest price for maintaining the quality (and profitability of the supplier) for assuring energy
saving can exceed those of the local companies. Therefore, use of 4) fundrasing such as loans
and lease, and 5) subsidy and tax credit and other public programs is preferable.
In case of 4), Japanese and local financial institutions provide products and services that can
be used for BEMS introduction with the help of public fund such as International Finance
Corporation. It is expected that the above products and services are further promoted and
cases are expanded. It is also important to build capacity for Japanese manufacturers to
propose their own finance schemes as European and American manufacturers do.
Thirdly, the opportunities for introducing BEMS and recognizing MRV should be provided by
both Japanese and Thai governments. The degree of recognition of BEMS among building
owners in Thailand is not high. In a DEDE seminar held in Bangkok, many building owners
showed strong interest in BEMS, which suggested market potential.
To exploit market potential and link it to energy saving trends at the national level, activities
by both governments are required. While providing the Thai government with the Japanese
experience of BEMS (dissemination process, construction of MRV methodology, types and
MRV DS Report in 2012
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behaviors of market players, and technological support for dissemination by the government),
a "Japan-Thailand public-private partnership" should be established to disseminate BEMS.
For the dissemination of BEMS, training BEMS engineers is essential. In some buildings the
staff visited in this study, there was no person who can operate a BEMS. It is difficult for
building owners to pay for the training cost. It is requested that the Thai or Japanese
government provide support for human resource development.
(12) Prospects and Challenges for Similar Project/Activity Implementation:
Calculation Method 3 of MRV methodology uses total floor area as key operations data in
emissions calculations. In office and commercial facilities, tenant occupation data is used to
define the operation state to control the effects of factors other than the introduction of BEMS
on energy consumption. However, if the operation rate is not appropriately monitored, or
variations in factors impacting energy consumption other than BEMS introduction are not
captured, significant errors in calculating emission reduction could occur. Therefore, to
improve the accuracy of operating ratio, it is necessary to consider establishing different
operating ratios for different usages of the building.
5. Contribution to Sustainable Development in Host Country Three ways in which introduction of BEMS can contribute to the sustainable development of
Thailand are listed below:
1) Alignment with the development policy and strategy of the host country: use of BEMS
to identify opportunities and measure the results of energy saving are in line with the Thai
government’s mid-term plan to 2015. Government policy aims to support the development of
specialists in energy saving and lower unit energy consumption. Energy saving of individual
facilities resulting from BEMS introduction, and measurement of energy use and operation
not only assist the Thai plan but co-evolve with it.
2) Contribution to Peak Power Reduction: In Thailand, the peak electric power usage in
2010 reached 25,089 MW, 12.6% above 2006 levels. Lowering peak electric power use is an
important issue for the development of Thai electric distribution system. In Japan and other
countries, adoption of BEMS systems has been shown to contribute to a reduction in peak
power usage. Demonstrating the relationship between use of BEMS and potential reductions
in peak power usage in Thailand may act as a driver for the introduction of BEMS removing
some of the issues impacting the development of Thailand’s electric distribution system.
3) Energy Saving Technology Transfer and Human Resource Development: There is a
clear demand for training of staff capable of conducting technical assessments to realize
energy saving opportunities and create financial plans. Introduction of BEMS is an important
tool through which people can be trained about different aspects of energy saving.