A case study on Life Cycle Cost Analysis of a green building
Praveen Raj Patro1, K. Nabeen Kumar2
1ITD Cementation India Limited, Kolkata
2L&T Construction, Bhubaneswar
*Corresponding Author Email: patro.praveenraj@gmail.com, nabeenkumar@gmail.com
ABSTRACT:
Modern building practices show little regard for energy efficiency, environmental or social impact of the built environment over their entire life cycle. Resources such as ground cover, forests, water and energy are depleted to give way to buildings. The indiscriminate use of natural resources puts pressure on the ecosystem. During building construction, vast quantities of waste material is created, and during building operations, large amount of energy is consumed, contributing extensively to environmental pollution. This paper presents the various aspects and benefits of green buildings along with building environment assessment tools and rating systems followed worldwide. Life cycle cost analysis is performed to prove the economics of green buildings vis-à-vis ordinary buildings. By considering only the initial cost; economic viability of green building cannot be admissible. This paper includes life cycle cost assessment of some of green building of India and some other countries to show the economic viability of green building. The economic feasibility of these studies are justified by considering cost of whole life period of building. Life period have taken in these study usually from 20 to 25 years. The whole life period of building includes the planning, design, construction, operation and maintenance phase. This study includes results in term of SIR value, NPV and the payback period of green buildings to show the feasibility of those buildings as compared to conventional buildings. From the perspective of the entire lifecycle of the building, this data was analysed to identify green design and construction practices that not only provide a green, luxurious environment but also enhance the building’s financial strength.
KEYWORDS: Life Cycle Costing, Green Building, SIR value, NPV.
INTRODUCTION:
The tremendous growth in economic activity across the globe is placing pressure on natural and environmental resources. The construction industry in India is growing rapidly at a rate of 10% compared with the world average of 5.2%. It is observed that buildings in India consume about 20% of the total electricity in the country. Hence, real estate activity in India has a significant impact on the environment and resources. This indicates that there is a real opportunity to develop green buildings in the country.
However, developers face a major challenge in the development of green buildings as in some cases this increases construction costs. Developers find it difficult to opt for green buildings due to price constraints difficulty in sourcing green building materials, technologies and service providers or facilitators in India. This paper attempts to understand and find solutions to these problems. It investigates the cost efficiency of green buildings through Lowest life-cycle cost (LCC) which is the most straightforward and easy-to-interpret measure of economic evaluation. Some other commonly used measures are Net Savings (or Net Benefits), Savings-to-Investment Ratio (or Savings Benefit-to-Cost Ratio), Internal Rate of Return, and Payback Period.
Financial Benefits
1. Green buildings reduce capital costs
2. High performance buildings reduce operating and maintenance costs
3. Sustainable buildings result in lower risks and liabilities
There is evidence that building green is getting less expensive day by day because of more and more work is underway on developing better green technology and cheap green material in developing countries. People are also becoming more and more aware and getting experience in constructing the green facilities. Some findings of financial benefits of green building tabulated below1;
Table 1: Financial benefits of green buildings (per sq. ft.)
|
Category |
20 yr. NPV(in US$) |
|
Energy value |
5.79 |
|
Emission value |
1.19 |
|
Water value |
0.51 |
|
Waste value |
0.03 |
|
Commissioning O&M value |
8.47 |
|
Productivity and health value (Certified & Silver) |
36.89 |
|
Productivity and health value (Gold & Platinum) |
55.33 |
|
Less green cost premium |
(4.00) |
|
Total 20 yr. NPV (Certified & Silver) |
48.87 |
|
Total 20 yr. NPV (Gold & Platinum) |
67.31 |
Recent studies indicate that the economic benefits have been substantiated; more and more the focus is on demonstrating the financial benefits of these products and practices as well as highlighting the environmental benefits.
Stages and Cost Components for LCCA:
Costs:
There are numerous costs associated with acquiring, operating, maintaining, and disposing of a building or building system. Building-related costs usually fall into the following categories:
a) Initial Costs—Purchase, Acquisition, Construction Costs
b) Fuel Costs
c) Operation, Maintenance, and Repair Costs
d) Replacement Costs
e) Residual Values—Resale or Salvage Values or Disposal Costs
f) Finance Charges—Loan Interest Payments
g) Non-Monetary Benefits or Costs
Parameters for Present-Value Analysis:
1. Discount Rate: In order to be able to add and compare cash flows that are incurred at different times during the life cycle of a project, they have to be made time-equivalent. LCC method converts them to present value by discounting them to a common point in time, usually the base date. The interest rate used for discounting is a rate that reflects an investor's opportunity cost of money over time, meaning that an investor wants to achieve a return at least as high as that of her next best investment. Hence, the discount rate represents the investor's minimum acceptable rate of return.
2. Cost Period(s): Length of study period: The study period begins with the base date, the date to which all cash flows are discounted. The study period includes any planning/construction/implementation period and the service or occupancy period. The study period has to be the same for all alternatives considered.
3. Service period: The service period begins when the completed building is occupied or when a system is taken into service. This is the period over which operational costs and benefits are evaluated.
4. Contract period: It starts when the project is formally accepted, energy savings begin to accrue, and contract payments begin to be due. The contract period generally ends when the loan is paid off.
5. Discounting Convention: In OMB and FEMP studies, all annually recurring cash flows (e.g., operational costs) are discounted from the end of the year in which they are incurred; in MILCON studies they are discounted from the middle of the year. All single amounts (e.g., replacement costs, residual values) are discounted from their dates of occurrence.
6. Treatment of Inflation: An LCCA can be performed in constant dollars or current dollars. Constant-dollar analyses exclude the rate of general inflation, and current-dollar analyses include the rate of general inflation in all dollar amounts, discount rates, and price escalation rates. Both types of calculation result in identical present-value life-cycle costs. The constant-dollar method has the advantage of not requiring an estimate of the rate of inflation for the years in the study period. Alternative financing studies are usually performed in current dollars if the analyst wants to compare contract payments with actual operational or energy cost savings from year to year.
Life-Cycle Cost Calculation:
After identifying all costs by year and amount and discounting them to present value, they are added to arrive at total life-cycle costs for each alternative2:
LCC = I + Repl - Res + E + W + OM&R + O
Where
LCC = Total LCC in present-value (PV) dollars of a given alternative
I = PV investment costs (if incurred at base date, they need not be discounted)
Repl = PV capital replacement costs
Res = PV residual value (resale value, salvage value) less disposal costs
E = PV of energy costs
W = PV of water costs
OM&R = PV of non-fuel operating, maintenance and repair costs
O = PV of other costs (e.g., contract costs for ESPCs or UESCs)
E. Supplementary Measures
Supplementary Measures:
All supplementary measures are relative measures, i.e., they are computed for an alternative relative to a base case.
NS = Net Savings: operational savings less difference in capital investment costs
SIR = Savings-to-Investment Ratio: ratio of operational savings to difference in capital investment costs
AIRR = Adjusted Internal Rate of Return: annual yield from an alternative over the study period, taking into account reinvestment of interim returns at the discount rate
SPB = Simple Payback: time required for the cumulative savings from an alternative to recover its initial investment cost and other accrued costs, without taking into account the time value of money
DPB = Discounted Payback: time required for the cumulative savings from an alternative to recover its initial investment cost and other accrued costs, taking into account the time value of money
Evaluation Criteria:
Followings are the evaluation criteria to make decision about whether Green Building is a viable option or not.
Lowest LCC (for determining cost-effectiveness)
NS > 0 (for determining cost-effectiveness)
SIR > 1 (for ranking projects)
AIRR > discount rate (for ranking projects)
SPB, DPB < than study period (for screening projects)
Sensitivity Analysis:
Sensitivity analysis is the technique recommended for energy and water conservation projects by FEMP. Sensitivity analysis is useful for:
1. Identifying which of a number of uncertain input values has the greatest impact on a specific measure of economic evaluation,
2. Determining how variability in the input value affects the range of a measure of economic evaluation, and
3. Testing different scenarios to answer "what if" questions.
4. Break-Even Analysis
Decision-makers sometimes want to know the maximum cost of an input that will allow the project to still break even, or conversely, what minimum benefit a project can produce and still cover the cost of the investment.
A Case Study Analysis- Godrej & Boyce, Mumbai:
Life Cycle Cost Analysis Example:
This deals with the actual computation of cost and benefit associated with various credits of IGBC Green Homes rating system. A hypothetical residential multi dwelling project is taken to perform cost benefit analysis. This project is assumed to aim for gold rating level. 20 years of period has been considered for cost and benefit analysis.
Benefit Calculations3:
Occupants will get something and even when there will be installed win technologies, once they occupy the building. This annual benefit gets infected by 5 % in the end of 20th year.
Present Value (PV):
PV is calculated by discounting the future cash flows. Following equation is used for calculation of PV.
PV= {Cn/ (I+R) n} =1042.39 Lacs
Where,
n=year number (i.e. 1, 2, 3 …20)
Cn= net cash flow at the end of year n (in our case it is annual benefit), R = Discount rate (in our case R= 12%)
Net Present Value (NPV):
NPV is calculated as follows,
· NPV= PV-Initial Cost=1042.39-205=837.38
· Hence NPV of entire project is Rs.837.38 Lacs.
· Total Built up area of project=3, 55,072 sq.ft.
· Hence NPV per sq.ft. = RS. 235.88
Sensitivity Analysis
Table 2: Sensitivity Analysis
|
|
Values Of Variables |
||
|
Most pessimistic |
Normal |
Most optimistic |
|
|
Initial cost |
|||
|
Change in percentage |
10% |
0% |
-10% |
|
Initial cost (in lacs) |
225.50 |
205 |
184.50 |
|
Net NPV (in lacs) |
816.88 |
837.38 |
857.88 |
|
NPV per Sq. Ft (in Rs) |
230.11 |
235.88 |
241.66 |
|
Operating cost |
|||
|
Change in percentage |
10% |
0% |
-10% |
|
Operating cost (in lacs) |
11.24 |
10.21 |
9.19 |
|
Net NPV (in lacs) |
941.62 |
837.38 |
836.46 |
|
NPV per Sq. Ft(in Rs) |
265.25 |
235.88 |
235.62 |
|
Benefits |
|||
|
Change in percentage |
-10% |
0% |
+10% |
|
Benefits (in lacs) |
121.95 |
110.87 |
99.781 |
|
Net NPV (in lacs) |
825.19 |
837.38 |
849.58 |
|
NPV per Sq. Ft(in Rs) |
232.45 |
235.88 |
239.32 |
Scenario Analysis
Table 3: Scenario Analysis
|
Scenario |
Initial Cost |
Operating Cost |
Benefits |
NPV (in Lacs) |
NPV/sq.ft (in Rs.) |
|
1 |
12% |
15% |
-10% |
682.10 |
192.14 |
|
2 |
10% |
10% |
-7% |
715.63 |
201.59 |
|
3 |
7% |
5% |
-5% |
760.33 |
214.18 |
|
4 |
3% |
2% |
0 |
829.12 |
233.55 |
|
5 |
-2% |
-3% |
3% |
879.10 |
247.63 |
|
6 |
-5% |
-5% |
8% |
944.77 |
266.13 |
Distribution of Benefits
Table 4: Outcomes of cost & benefit of the project
|
|
Total in |
Costs/sq.ft |
|
Additional cost for green building |
205 |
57.75 |
|
Gross benefits from green building(Total PV) |
1042.39 |
293.63 |
|
Net benefits (NPV)=Total PV- Additional cost |
837.38 |
235.88 |
Developer’s Benefits
Table 5 shows that developer can earn additional profit of rupees 316. 19 lakhs by providing green technologies or by constructing a green building.
Table 5: Developers Benefit
|
|
Rs. In Lacs |
|
Share of benefit from green features |
521.19 |
|
Initial cost incurred by developer |
205 |
|
Additional profit=shared benefit-initial cost |
316.19 |
Customer’s Benefit4
Benefit for customers can be a reduction in per sq.ft price. Besides this, customer will be getting reduced operating cost.
Customers benefit per sq.ft. = Total shared benefit * Total built up area
= Rs 146.81
Table 6: shows that customer gets benefits of Rs. 146.81 per sq.ft. In the price.
Table 6: Customer Benefits
|
|
Rs/sq.ft. |
|
Cost to customer |
5000 |
|
Benefits |
146.81 |
|
Net Cost |
4853.19 |
Case Studies and Various Findings for Green Buildings in India
LCCA of Green Buildings in India and Various Findings5
Table 7: Performance of Green Building in India
|
Name of the Project |
Location |
Built-up-area (Sq. ft.) |
Rating achieved |
Increase in cost (%) |
Payback period (years) |
|
CII-Sorabji Godrej GBC |
Hyderabad |
20,000 |
Platinum |
18 |
7 |
|
ITC Green Centre |
Gurgaon |
170,000 |
Platinum |
15 |
6 |
|
Wipro |
Gurgaon |
175,000 |
Platinum |
8 |
5 |
|
Technopolis |
Kolkata |
72,000 |
Gold |
6 |
3 |
|
Spectral services consultants office |
Noida |
15,000 |
Platinum |
8 |
4 |
|
HITAM |
Hyderabad |
78,000 |
Silver |
2 |
3 |
|
Grundfos Pump |
Chennai |
40,000 |
Gold |
6 |
3 |
Source: CII
Table 8: Cost Premiums on Green Materials, Equipment and Techniques
|
Green materials, equipment and techniques |
Cost premiums Unit |
Cost Premium Value |
|
High-quality steel with recycled metal content |
INR per tonne |
5,000 |
|
Fly ash content in cement |
% |
22 |
|
Aerated blocks for solid masonry |
INR psf |
37.16 |
|
Double-glazed glass |
INR psf |
10 |
|
Ultra-low plumbing fixtures |
% |
3 |
|
Strom water management system |
INR million |
30 |
|
Special chillers COP-6.5 |
% |
15 |
|
Low side HVAC |
% |
10 |
|
Rooftop garden |
INR psf |
250 |
|
Energy modelling consultant |
INR million |
1.2 |
Source: India bull Real-estate Ltd, Jones Lang LaSalle, Meghraj Project Management and Research
Table 9 depicts the Revenue outflows due to incorporation of green features.
Table 9: Revenue outflows
|
Cost Savings |
Units |
Value |
|
Electricity cost savings |
% |
25 |
|
Water cost savings |
% |
30 |
|
Revenue generation |
||
|
Rental premium (non-sustainability discount) |
% |
1-2 |
|
Carbon credits in ten years |
INR million |
90 |
Source: India bull Real-estate Ltd, Jones Lang LaSalle, Meghraj Project Management and Research
Graph 1: Comparison of initial investment cost (per Sqm.) Green Vs. conventional Building
Table 10: Calculating % increment in cost due to Green features
|
Typology |
Location |
Climate |
AC/Non AC |
Year |
Increment in total civil works cost (in %) |
|
Institute of liver & Biliary Sciences |
|||||
|
Hospital |
Delhi |
Composite |
AC |
2004 |
1.2 |
|
Dental college at Jamia Millia Islamia |
|||||
|
College |
Delhi |
Composite |
AC |
2007 |
2.1 |
|
Kendriya Vidyalaya |
|||||
|
School |
Delhi |
Composite |
Non AC |
2008 |
3.9 |
|
Residential quarters |
|||||
|
Residential |
Ahmedabad |
Hot & Dry |
Non AC |
2005 |
2.3 |
|
Super Speciality Hospital |
|||||
|
Hospital |
Jammu |
Composite |
AC |
2007 |
5.9 |
|
IISER Hostel |
|||||
|
Hostel |
Pune |
Moderate |
Non AC |
2007 |
5.8 |
|
Census Office |
|||||
|
Office |
Gandhinagar |
Hot & Dry |
Non AC |
2005 |
4.3 |
|
Centre for Distance education bldg., Nagarjuna University |
|||||
|
College/office |
Vijayawada |
Warm & Humid |
Non AC |
2006 |
7.0 |
|
Residential Quarters |
|||||
|
Residential |
Bikaner |
Hot & Dry |
Non AC |
2006 |
6.6 |
|
NSSO Office |
|||||
|
Office |
Lucknow |
Composite |
Non AC |
2005 |
5.5 |
|
RTI & Hostel Bldg. for CAG |
|||||
|
Hostel/Training Institute |
Mumbai |
Warm & Humid |
AC |
2011 |
3.5 |
Increment was in the range of 1.2 to 7%, and an average of 4.4%
Life Cycle Energy Analysis of Multifamily Residential House: A Case Study6
Table 11: Life cycle energy comparison
|
Case |
Features |
Embodied |
Operating |
Life cycle |
Life cycle savings (%) |
|
Base case (AS Built) |
Envelope: burnt clay brick masonry roof RCC |
8.07 |
66.85 |
75.07 |
|
|
Case A |
Envelope: aerated concrete block masonry |
7.04 |
60.58 |
67.76 |
9.7 |
|
Case B |
Envelope: aerated concrete block masonry(PV panels) |
9.68 |
37.3 |
47 |
37.4 |
Graph 2: Variation of LCE of the building with change in span
Conclusion of the case study7:
Multi storey houses can be preferred over single storey houses as LCE of single storey houses (300 - 330 kWh/m2 year) is higher than multi storey houses (270 - 280 kWh/m2 year). Electricity consumption during operation phase of the building is to be reduced to lower its life cycle energy demand and make it sustainable. Use of aerated concrete blocks in the construction of walls and for covering roof reduces building’s life cycle energy demand by 9.7%. Building integrated photo voltaic panels are found most promising for reduction in life cycle energy use of the building as it decreases 37% when part of electrical energy demand (75 MWh per annum) of the building is met through PV panels.
Though embodied energy of the buildings accounts only 11% of the LCE of the building, opportunity for its reduction through low embodied energy materials should also be considered.
Case Studies and Various Findings for Green Buildings Other Than India
Table 12: Basic economic information for life cycle analysis of GOP option
|
Province/territory |
General inflation rate |
Discount rate (excluding inflation) |
Economic life (years) |
Environmental multiplier |
Water cost ($/1000 cum.) |
escalation rate (excluding inflation) |
|
|
Canada |
3.0% |
6.0% |
30 |
1.0 |
1031 |
5.15% |
|
Total life cycle cost (TLCC) = CCI + PCF*(OCI + MCI)
Where
TLCC = total life cycle cost
CCI = capital cost increment
PCF = present cost factor
OCI = operating cost increment
MCI = maintenance cost increment
Table 13: Total life cycle cost parameter analysis
|
General inflation rate |
Discount rate |
Water cost escalation rate |
Effective interest rate |
Project life |
Present cost factor |
|
3% |
6% |
5.15% |
0.93% |
30 |
26.09 |
Table 14 shows Total life cycle cost evaluation of the office building tabulated below.
Table 14: Total life cycle cost evaluation
|
Base case capital cost |
Alternative capital cost |
CCI |
OCI |
MCI |
TLCC |
|
$300 |
$300 |
0 |
$10 |
0 |
$261 |
|
$300 |
$400 |
$100 |
0 |
0 |
$100 |
CASE STUDY: COLORADO COURT
Percentage of Net cost increased due to incorporation of green feature are listed in table 15 as follows:
Table 15: Net cost of Greening
|
|
Cost ($) |
Cost/Sq. ft.($) |
% of total dev. Costs |
|
Green design |
4,700,000 |
157.41 |
|
|
Traditional design |
4,085,778 |
142.98 |
|
|
Green design premium |
614,222 |
3.75 |
13.07 |
|
Net cost of greening |
614,222 |
3.75 |
13.07 |
Saving made by green features included in table 16.
Table 16: Green saving
|
Owner NPV by feature (before demand meter) |
305,956 |
|
Owner NPV by category (before demand meter) |
305,956 |
|
Owner NPV by feature (after demand meter) |
227,513 |
|
Owner NPV by category (after demand meter) |
227,513 |
|
Owner NPV by feature (assuming full buyback of energy) |
88,780 |
|
Owner NPV by feature (assuming full buyback of energy) |
88,780 |
Table 17 shows the operating cost of conventional building and what was the saving made in operating cost due to green features.
Table 17: Operating costs
|
Operating cost category |
Green costs($) |
Traditional costs($) |
Annual saving($) |
|
Electricity |
5,762 |
8,448 |
2,686 |
|
Gas |
412 |
981 |
569 |
|
Water |
183 |
506 |
323 |
|
Total |
6,357 |
9,935 |
3,578 |
Green saving made by the resident as well as the owner by both feature and category tabulated below.
Table 18: Green saving
|
Resident NPV by feature |
88,921 |
|
Resident NPV by category |
88,921 |
|
Owner NPV by feature |
21,378 |
|
Owner NPV |
21,378 |
Table 19: Case studies5
|
CASE STUDIES |
Implementation |
Impact on productivity |
|
US POST OFFICE, RENO, NV |
Energy efficient lighting and dropped ceiling · Cost = $300,000 · Energy savings $22,400/year, payback 13 years
|
· Sorting errors dropped to 0.1% · 8% increase in mail sorted per hour · Annual productivity gains $400-500K · Payback period < 1 year |
|
HERMAN MILLER SQA BUILDING |
295,000 sf. office & manufacturing centre · Extensive daylighting · Interior “street” with plants · Passive heating & cooling · $35,000+ annual energy savings |
· Increase in worker effectiveness and productivity
|
|
EMERYVILLE, CA AFFORDABLE HOUSING DEVELOPMENT |
Material efficiency · Framing at 24” instead of 16” · Significant saving on volume of wood used · 50,000 sq. ft. school · Costs of carpet vs. durable floor compared · Includes installation, maintenance & replacement costs · Over 40 years, durable flooring saves $5.4 million |
Scope of the Problem · 136 million tons of building-related C&D debris (1996) · 43% from residential sources, 57% non-residential · Demolition = 48%, renovation = 44%, construction = 8% · 20 - 30% recovered for processing & recycling · Most often recycled: concrete, asphalt, metals, wood. “Deconstruction” → highest diversion rates (76%) |
|
SCHOOLS |
Energy cost got reduced due to incorporation of green measures · Spend more than $6 billion annually on energy · DOE estimates possible 25% savings through: o Energy efficiency o Renewable energy technologies o Improved building design |
Daylight schools vs. non-daylight schools: · 2%-64% energy cost reductions · Payback for new daylight schools < 3 years · Increase in student performance |
LCCA for Similar Buildings
In this study, we compares construction costs of buildings where LEED certification was a primary goal to similar buildings where LEED was not considered during design. The building types analysed included the three previously evaluated- academic buildings, laboratories and libraries and two new types- community centres and ambulatory care facilities.
A total of 221 buildings were analysed. Of these, 83 buildings were selected which were designed with a goal of meeting some level of the USGBC’s LEED certification. The other 138 projects were buildings of similar program types which did not have goal of sustainable design.
Followings are the findings made by USGBC figured out below.8
Graph 3
CONCLUSION:
As this article illustrates, LCC provides an opportunity to embed sustainability principles at the design stage of building construction. Lowest life-cycle cost (LCC) is the most straightforward and easy-to-interpret measure of economic evaluation. By taking a holistic approach to the construction of new buildings, and focusing on achieving value for money, the trade-off between time, quality and price can be mitigated. As can be seen with case studies taking a more sustainable approach does indeed increase initial capital expenditure, however significant savings and quicker payback periods are proven. Referring to the graph 3 for the similar buildings by taking integrated approaches during design and construction stage even the initial cost for the green buildings can be lowered than the conventional building.
REFERENCES:
1. N.K. Bansal, “Energy Security, Climate Change and Sustainable Development,” In J. Mathur, H. J. Wagner and N. K. Bansal Ed., Science, Technology and Society: Energy Security for India. Anamaya Publishers, Inc., New Delhi, 2007, pp. 15-23
2. K. Adalberth, “Energy Use during the Life Cycle of Single-Unit Dwellings: Examples,” building and environment, vol 32, No 4, 1997,pp. 321-329
3. B.V.V. Reddy and K.S. Jagadish, “Embodied Energy of Common and Alternative Building Materials and Technologies,” Energy and Buildings, Vol. 35, No.129-137.
4. Kadoshin S., Takashi Nishivama and Toshihide Ito, “The trend in current and near future Energy consumption from the statistical”, Journal of Applied Energy, vol. 67, 2000, pp 407-417.
5. Kate Greg, capital E, “The costs & financial benefits of green building”
6. Green economics- cost efficiency of Green Buildings in India, JLL Meghrah, 2008
7. M. Asif, T. Muneer and R. Kelley, “Life Cycle Assessment: A Case Study of a Dwelling Home in Scotland,” Building and Environment, Vol. 42, No. 3, 2007, pp. 1391-1394.
8. Green Habitat, “A newsletter on green buildings”
|
Received on 15.11.2015 Accepted on 28.12.2015 © EnggResearch.net All Right Reserved Int. J. Tech. 5(2): July-Dec., 2015; Page 322-328 DOI: 10.5958/2231-3915.2015.00042.5 |