An economic technique applied to public decision−making that attempts to quantify the advantages (benefits) and disadvantages (costs) associated with a particular project or policy.
ReSAKSS-AfricaLead Workshop on Strengthening Capacity for Strategic Agricultural Policy and Investment Planning and Implementation in Africa Safari Park Hotel, Nairobi, June 25th‐ 26th 2012
ost-benefit analysis provides an organizational framework for identifying, quantifying, and comparing the costs and benefits (measured in dollars) of a proposed policy action. The final decision is informed (though not necessarily determined) by a comparison of the total costs and benefits.
ReSAKSS-AfricaLead Workshop on Strengthening Capacity for Strategic Agricultural Policy and Investment Planning and Implementation in Africa Safari Park Hotel, Nairobi, June 25th‐ 26th 2012
ost-benefit analysis provides an organizational framework for identifying, quantifying, and comparing the costs and benefits (measured in dollars) of a proposed policy action. The final decision is informed (though not necessarily determined) by a comparison of the total costs and benefits.
This report focuses on the Cost-Benefit Analysis which is effective tool and a rational technique for economic valuation where market information is either non-existent or deficient is.
Garrett Hardin discusses the role of open access resources that lead to their over use and exploitation. Environmental goods are in the nature of open access, common property resources so that there is no limit to their use. This results in over exploitation and destruction.
Monitoring is an activity undertaken to provide specific information on the characteristics and functioning of environmental and social variables in space and time. Environmental monitoring compares impacts predicted in environmental impact assessment with those which actually occur during and after implementation, in order to assess whether the impact prediction process performs satisfactorily. In Kenya communities are encouraged take a leading role and responsibility to monitor project activities at all stages to ensure that the measures stipulated in the environmental management plan are adequate to mitigate adverse impacts or are attaining or fulfilling the anticipated benefits from the project
Monitoring is therefore undertaken after the project has begun to check the initial EIA predictions and determine whether further action is needed to abate or avoid pollution or environmental harm. It can also be done for purposes of conducting research or identifying patterns or trends which reflect the state of the environment. It can also be described measurement of the quality of the environment and each of its components, activities or natural and anthropogenic inputs which may affect the quality of the environment and the effects of such activities.
All monitoring strategies and programmes have reasons and justifications. The aim is to actually establish the current state of or trends in certain environmental parameters. In all cases the results of a monitoring process will be reviewed, analyzed statistically and published. The design of a monitoring program must therefore have regard to the final use of the data before monitoring actually starts.
The frequency of monitoring will vary from project to project. This depends on the nature of the project and severity of the environmental impacts.
NAP Training Viet Nam - Session 7 Appraising Adaptation OptionsUNDP Climate
This two-day workshop supported the Government of Viet Nam in building the necessary capacity to advance its National Adaptation Plan (NAP) process. The workshop closely focused on building National Adaptation Plans in the agricultural sector through multi-stakeholder collaboration, and increased knowledge and capacity on a number of topics including: prioritization of adaptation options, cost-benefit analysis, overview of the broad-based nature of climate change adaption impacts, analysis of challenges, and creation of an open discussion with key stakeholders on defining a road-map for the NAP process. The workshop was delivered using discussions and case studies to enhance interactive learning for participants, with supporting presentations by GiZ and SNV.
This report focuses on the Cost-Benefit Analysis which is effective tool and a rational technique for economic valuation where market information is either non-existent or deficient is.
Garrett Hardin discusses the role of open access resources that lead to their over use and exploitation. Environmental goods are in the nature of open access, common property resources so that there is no limit to their use. This results in over exploitation and destruction.
Monitoring is an activity undertaken to provide specific information on the characteristics and functioning of environmental and social variables in space and time. Environmental monitoring compares impacts predicted in environmental impact assessment with those which actually occur during and after implementation, in order to assess whether the impact prediction process performs satisfactorily. In Kenya communities are encouraged take a leading role and responsibility to monitor project activities at all stages to ensure that the measures stipulated in the environmental management plan are adequate to mitigate adverse impacts or are attaining or fulfilling the anticipated benefits from the project
Monitoring is therefore undertaken after the project has begun to check the initial EIA predictions and determine whether further action is needed to abate or avoid pollution or environmental harm. It can also be done for purposes of conducting research or identifying patterns or trends which reflect the state of the environment. It can also be described measurement of the quality of the environment and each of its components, activities or natural and anthropogenic inputs which may affect the quality of the environment and the effects of such activities.
All monitoring strategies and programmes have reasons and justifications. The aim is to actually establish the current state of or trends in certain environmental parameters. In all cases the results of a monitoring process will be reviewed, analyzed statistically and published. The design of a monitoring program must therefore have regard to the final use of the data before monitoring actually starts.
The frequency of monitoring will vary from project to project. This depends on the nature of the project and severity of the environmental impacts.
NAP Training Viet Nam - Session 7 Appraising Adaptation OptionsUNDP Climate
This two-day workshop supported the Government of Viet Nam in building the necessary capacity to advance its National Adaptation Plan (NAP) process. The workshop closely focused on building National Adaptation Plans in the agricultural sector through multi-stakeholder collaboration, and increased knowledge and capacity on a number of topics including: prioritization of adaptation options, cost-benefit analysis, overview of the broad-based nature of climate change adaption impacts, analysis of challenges, and creation of an open discussion with key stakeholders on defining a road-map for the NAP process. The workshop was delivered using discussions and case studies to enhance interactive learning for participants, with supporting presentations by GiZ and SNV.
Social Cost Benefit Analysis: Concept of social cost benefit, significance of SCBA, Approach to SCBA,
UNIDO approach to SCBA, Shadow pricing of resource, the little miracle approach,
Project Implementation: Schedule of project implementation, Project Planning, Project Control, Human
aspects of project management, team building, high performance team.
Taking Stock – 40 years of Industrial Energy AuditsLeonardo ENERGY
Industrial energy audits were amongst the first energy efficiency policy measures developed in response to the oil shocks of the 1970s. Since then they have become enormously popular in industrialised economies. In the EU they are mandatory for large organisations under the EU Energy Efficiency Directive. Developing countries are considering them as they scale up their own climate programmes.
So interest in audits can only grow. But, from a policy-maker’s perspective, do they work? How do they work? How could they work for me? Certainly, in principle, audits are extremely important because they get to the heart of how a company uses energy. But after 40 years, the scientific literature on audits is large and complex and difficult for the non-specialist policy-maker to wade though.
This webinar tell the story of audits in a way designed to cut through this complexity. It recounts the history of audits and sets out why they are important. It sets out some of the main features of successful audit programmes, and, from the practical experience of the speaker, how to go about putting one together. It then considers the main problems with audits and how these can be addressed. Finally the talk will look ahead to see how audits might evolve in the near future.
Taking Stock – 40 years of Industrial Energy Audits Leonardo ENERGY
Industrial energy audits were amongst the first energy efficiency policy measures developed in response to the oil shocks of the 1970s. Since then they have become enormously popular in industrialised economies. In the EU they are mandatory for large organisations under the EU Energy Efficiency Directive. Developing countries are considering them as they scale up their own climate programmes.
So interest in audits can only grow. But, from a policy-maker’s perspective, do they work? How do they work? How could they work for me? Certainly, in principle, audits are extremely important because they get to the heart of how a company uses energy. But after 40 years, the scientific literature on audits is large and complex and difficult for the non-specialist policy-maker to wade though.
This webinar tell the story of audits in a way designed to cut through this complexity. It recounts the history of audits and sets out why they are important. It sets out some of the main features of successful audit programmes, and, from the practical experience of the speaker, how to go about putting one together. It then considers the main problems with audits and how these can be addressed. Finally the talk will look ahead to see how audits might evolve in the near future.
Conceptual framework for evaluating multiple benefits from energy efficiencyLeonardo ENERGY
The International Energy Agency (IEA) launched their recent publication, “Capturing the Multiple Benefits of Energy Efficiency,” at IEPPEC in Berlin (September 2014). Following the launch of the publication, the IEA and IEPPEC have collaborated to explore and address the evaluation process relating to these multiple impacts/ benefits. This webinar will cover one focus area of that collaboration – i.e., the development of a conceptual framework aimed to provide some guidance regarding the evaluation process of these multiple benefits/impacts within the scope of an energy efficiency programme or policy. This webinar will provide an overview of the draft framework as well as an early opportunity for researchers and evaluators to offer feedback prior to more in-depth discussion with a panel at this year’s IEPPEC June 7-9 in Amsterdam.
A VRC™ is the monetized cost of the estimated impact of climate change, adjusted for the income level of the community, that will be avoided as a result of the project. In brief, it is a credit for work done to avoid damages or losses owing to climate change - a vulnerability reduction credit.
This tutorial discusses why, what and how VRCs came to be and may benefit those interested in impactful climate adaptation.
Workplace wellbeing relates to all aspects of working life, from the quality and safety of the physical environment, to how workers feel about their work, their working environment, the climate at work and work organization.
Workers wellbeing is a key factor in determining an organization’s longterm effectiveness
law is a body of norms
(or rules of conduct) of binding force and effect, specified
and enforced by a recognised authority. Law is used to
create rights and duties, which should be applied fairly
and consistently throughout society
PUBLIC HEALTH POLICY & LEGISLATIONS Health is the right of all persons and the duty of the State and is guaranteed by means of social and economic policies aimed at reducing the risk of illness and other hazards and at universal and equal access to all actions and services for the promotion, protection and recovery of health.
After completing this module you will able to..
1. Describe the access tools available to you for finding information
2. Identify effective search techniques
3. Describe the characteristics of Internet search engines , subject directory and databases.
4. Identify a range of information sources
5. Consider which sources are most likely to be useful for your search question
6. Understand why some information sources may be more helpful than others in the context of a particular information need.
After completing this module you will able to..
1. Analyze a research topic
2. Develop appropriate search strategies and conduct a search
3. Refine search results
Micro RNA genes and their likely influence in rice (Oryza sativa L.) dynamic ...Open Access Research Paper
Micro RNAs (miRNAs) are small non-coding RNAs molecules having approximately 18-25 nucleotides, they are present in both plants and animals genomes. MiRNAs have diverse spatial expression patterns and regulate various developmental metabolisms, stress responses and other physiological processes. The dynamic gene expression playing major roles in phenotypic differences in organisms are believed to be controlled by miRNAs. Mutations in regions of regulatory factors, such as miRNA genes or transcription factors (TF) necessitated by dynamic environmental factors or pathogen infections, have tremendous effects on structure and expression of genes. The resultant novel gene products presents potential explanations for constant evolving desirable traits that have long been bred using conventional means, biotechnology or genetic engineering. Rice grain quality, yield, disease tolerance, climate-resilience and palatability properties are not exceptional to miRN Asmutations effects. There are new insights courtesy of high-throughput sequencing and improved proteomic techniques that organisms’ complexity and adaptations are highly contributed by miRNAs containing regulatory networks. This article aims to expound on how rice miRNAs could be driving evolution of traits and highlight the latest miRNA research progress. Moreover, the review accentuates miRNAs grey areas to be addressed and gives recommendations for further studies.
"Understanding the Carbon Cycle: Processes, Human Impacts, and Strategies for...MMariSelvam4
The carbon cycle is a critical component of Earth's environmental system, governing the movement and transformation of carbon through various reservoirs, including the atmosphere, oceans, soil, and living organisms. This complex cycle involves several key processes such as photosynthesis, respiration, decomposition, and carbon sequestration, each contributing to the regulation of carbon levels on the planet.
Human activities, particularly fossil fuel combustion and deforestation, have significantly altered the natural carbon cycle, leading to increased atmospheric carbon dioxide concentrations and driving climate change. Understanding the intricacies of the carbon cycle is essential for assessing the impacts of these changes and developing effective mitigation strategies.
By studying the carbon cycle, scientists can identify carbon sources and sinks, measure carbon fluxes, and predict future trends. This knowledge is crucial for crafting policies aimed at reducing carbon emissions, enhancing carbon storage, and promoting sustainable practices. The carbon cycle's interplay with climate systems, ecosystems, and human activities underscores its importance in maintaining a stable and healthy planet.
In-depth exploration of the carbon cycle reveals the delicate balance required to sustain life and the urgent need to address anthropogenic influences. Through research, education, and policy, we can work towards restoring equilibrium in the carbon cycle and ensuring a sustainable future for generations to come.
Characterization and the Kinetics of drying at the drying oven and with micro...Open Access Research Paper
The objective of this work is to contribute to valorization de Nephelium lappaceum by the characterization of kinetics of drying of seeds of Nephelium lappaceum. The seeds were dehydrated until a constant mass respectively in a drying oven and a microwawe oven. The temperatures and the powers of drying are respectively: 50, 60 and 70°C and 140, 280 and 420 W. The results show that the curves of drying of seeds of Nephelium lappaceum do not present a phase of constant kinetics. The coefficients of diffusion vary between 2.09.10-8 to 2.98. 10-8m-2/s in the interval of 50°C at 70°C and between 4.83×10-07 at 9.04×10-07 m-8/s for the powers going of 140 W with 420 W the relation between Arrhenius and a value of energy of activation of 16.49 kJ. mol-1 expressed the effect of the temperature on effective diffusivity.
Natural farming @ Dr. Siddhartha S. Jena.pptxsidjena70
A brief about organic farming/ Natural farming/ Zero budget natural farming/ Subash Palekar Natural farming which keeps us and environment safe and healthy. Next gen Agricultural practices of chemical free farming.
Artificial Reefs by Kuddle Life Foundation - May 2024punit537210
Situated in Pondicherry, India, Kuddle Life Foundation is a charitable, non-profit and non-governmental organization (NGO) dedicated to improving the living standards of coastal communities and simultaneously placing a strong emphasis on the protection of marine ecosystems.
One of the key areas we work in is Artificial Reefs. This presentation captures our journey so far and our learnings. We hope you get as excited about marine conservation and artificial reefs as we are.
Please visit our website: https://kuddlelife.org
Our Instagram channel:
@kuddlelifefoundation
Our Linkedin Page:
https://www.linkedin.com/company/kuddlelifefoundation/
and write to us if you have any questions:
info@kuddlelife.org
WRI’s brand new “Food Service Playbook for Promoting Sustainable Food Choices” gives food service operators the very latest strategies for creating dining environments that empower consumers to choose sustainable, plant-rich dishes. This research builds off our first guide for food service, now with industry experience and insights from nearly 350 academic trials.
UNDERSTANDING WHAT GREEN WASHING IS!.pdfJulietMogola
Many companies today use green washing to lure the public into thinking they are conserving the environment but in real sense they are doing more harm. There have been such several cases from very big companies here in Kenya and also globally. This ranges from various sectors from manufacturing and goes to consumer products. Educating people on greenwashing will enable people to make better choices based on their analysis and not on what they see on marketing sites.
1. Dr. Ahmed-Refat AG Refat
Cost Benefit
Analysis CBA
SBCM-MCC 22/02/2015 1Dr.Ahmed-Refat 2015
2. DEFINITION
An economic technique
applied to public
decision−making that
attempts to quantify the
advantages (benefits) and
disadvantages (costs)
associated with a particular
project or policy. 2Dr.Ahmed-Refat 2015
3. Private vs Social cost and benefit
• it is important to correctly measure
costs and benefits.
• We must identify the private
costs and benefits versus the
social costs and benefits
3Dr.Ahmed-Refat 2015
4. • The social costs and benefits are often
spread out across society, rather than
being paid directly to the organization
that is undertaking a project/service
Private vs Social cost and benefit
4Dr.Ahmed-Refat 2015
5. Externalities
• When non-market impacts do not occur in the
transactions between the producer and the
direct users of the services but fall on third
parties, these impacts are defined as
externalities.
• The social costs are therefore externalities;
they must be included in the decision-making
process to ensure greatest efficiency.
5Dr.Ahmed-Refat 2015
6. A procedure for comparing
alternative courses of
action by reference to the
net social benefits that they
produce for the community
as a whole.
DEFINITION
6Dr.Ahmed-Refat 2015
7. ‘Net Social Benefit’
• = difference between social
benefits and social costs.
• Cost-benefit analysis
proceeds by estimating
hypothetical dollar amounts
that reflect real economic
values. 7Dr.Ahmed-Refat 2015
8. Intangibles
• Inevitably, some costs and benefits
resist the assignment of dollar values.
• These costs and benefits, known as
‘intangibles’, are separately presented
to the decision-maker for assessment
in conjunction with the quantified
estimate of the net social benefit of the
activity.
8Dr.Ahmed-Refat 2015
9. CBA- Aim
• The aim of an CBA is to estimate
the benefits, in monetary terms, of
proposed policy changes in order to
inform decision making.
• Estimating benefits in monetary
terms allows the comparison of
different types of benefits in the
same units, 9Dr.Ahmed-Refat 2015
10. USES
• CBA is most commonly used
for public decisions– policy
proposals, programs, and
projects, e.g., dams, bridges,
traffic circles, and anything
else the government might
fund.
10Dr.Ahmed-Refat 2015
11. •Accepting or rejecting a single project;
•Choosing the appropriate scale and/or timing
for a project;
•Choosing one of a number of mutually
exclusive projects;
•Choosing a number of discrete alternative
projects from a larger number of discrete
alternative projects;
•Evaluating government policies, notably
though not only related to government
regulations; and
•Evaluating projects or policies post- rather
than pre-
USES
11Dr.Ahmed-Refat 2015
12. CBA –strengths
• Systematic way of thinking and
analysis
• Focus on use of scarce
resources
• Strong methodological basis
• Monetary measurement provides
comparison
• Appeal to policy makers 12Dr.Ahmed-Refat 2015
13. Limitations
One approach to assess the
efficiency of policy/program
Uncertainty of all parameters
used
Estimated values of objects at
risk
Probabilities of the hazard
13Dr.Ahmed-Refat 2015
14. Benefit-Cost Analysis (BCA)
• Benefits and costs measured in a
common unit, typically monetary .
• Some benefits & costs may be
difficult to measure in monetary
units.
•
14Dr.Ahmed-Refat 2015
15. Cost-Effectiveness Analysis
(CEA)
• Benefits measured in “natural” (non-monetary)
units
• – Health effect (e.g., "lives saved," asthma
cases averted
• (QALYs, DALYs)
• – Exposure (e.g., peak ozone concentration(
• – Emissions (e.g., tons of CO2)
• Allows comparison of costs per unit benefit
(efficiency).
• Judgment of whether benefits justify costs (and
optimal level of control) is external to analysis.
15Dr.Ahmed-Refat 2015
16. Cost Effectiveness Analysis:
• CEA does not require the monetization of
either the benefits or the costs (usually the
benefits).
• CEA does not show whether the benefits
outweigh the costs, but shows which
alternative has the lowest costs (with the
same level of benefits).
• CEA is often applied when the norm for a
certain level of safety has been set.
• CEA analyzes which types of solution is
the ‘cheapest’ given a certain level of
safety standard.
16Dr.Ahmed-Refat 2015
17. CEA
• What is the cost per unit of
output/impact that can be bought by
intervention A?
• Cost per youth trained
• Cost per life saved
• Cost per children without nutrition
problems
• Cost per DALY / QALY
17Dr.Ahmed-Refat 2015
18. Theory of Cost-Benefit Analysis
• Choose the level of service to
maximize net social benefits
(NSB)
• NSB = TSB – TSC where
• TSB = total social benefits
• TSC = total social costs
18Dr.Ahmed-Refat 2015
19. Basic Steps CBA
1. Define scope of the project
2. Identify the type of costs and benefits
3. Put monetary values on costs and
benefits
4. Compare costs and benefits
5. Calculate profitability
indicators/decision criteria
6. Sensitivity analysis
7. Make recommendations.
19Dr.Ahmed-Refat 2015
20. Calculating net benefits
The outcomes of NSB depends on :
1. What is included in the categories of
costs and benefits
2. How each of the goods/services are
valued
3. The discount rate(s)
4. Risks and uncertainty
5. Choice of “prices”: current/real/shadow.
20Dr.Ahmed-Refat 2015
21. Categories of Costs
• When economists estimate
the costs of a policy or
project for the purpose of
conducting a CBA, they
refer to the Social Costs
of the Policy.
21Dr.Ahmed-Refat 2015
22. Costs
•The costs of the policy/project falls
into five broad categories:
1. Real−resource costs, Including
compliance costs,
2. Government regulatory costs
3. Social welfare losses
4. Transitional costs
5. Indirect costs. 22Dr.Ahmed-Refat 2015
23. 1-Real−resource cost
• All of the resources that are used up
to implement the program or policy.
• Compliance costs: all of the
resources that must be expended for
complying with the regulatory
aspects of the program.
•
23Dr.Ahmed-Refat 2015
24. 2- Government regulatory
cost
• includes the monitoring,
administrative, and
enforcement costs
associated with the policy,
especially when the latter has
a regulatory aspect
• 24Dr.Ahmed-Refat 2015
25. 3- Social welfare losses
• The consumer and
producer losses
associated with possible
rises in prices or
decreases in output that
occur as a result of the
policy. 25Dr.Ahmed-Refat 2015
26. 4- Transitional social costs
• include the value of all the resources
that are displaced by the policy, and
the private
• costs of reallocating these
resources.
• 5- Indirect costs
26Dr.Ahmed-Refat 2015
27. Estimation of the Benefits
• The correct way to
measure the benefits of a
proposed policy/PROJECT
is to ask the beneficiaries
what is their willingness to
pay (WTP) for it.
27Dr.Ahmed-Refat 2015
28. WTP/WTA
• WTP is one method that we can use to
determine the price of a good.
• This is useful in cases where price is not
known, e.g. noise pollution .
• This method tries to determine the price
that people are willing to pay for the good.
28Dr.Ahmed-Refat 2015
29. A. Market Approaches
• In some cases, it is possible
to determine the WTP for the
proposed policy by using
information available in
regular markets.
29Dr.Ahmed-Refat 2015
30. Non market approaches
• In many cases, WTP
cannot be measured easily
using market prices,
because the impacts of the
policy are not traded in
regular markets.
30Dr.Ahmed-Refat 2015
31. Stated preference methods
• A direct survey approach to
estimating the value placed on
non-market goods or services.
They rely on information
obtained through surveys rather
than on the indirect valuation
through revealed preference
methods. 31Dr.Ahmed-Refat 2015
33. Net present value
• The correct criterion for reducing
benefits and costs to a unique
value is the net present value
(NPV( or “net benefits” criterion.
The correct rule is to adopt any
project with a positive NPV and
to rank projects by their NPVs.
33Dr.Ahmed-Refat 2015
34. Benefit/cost analysis
• If B/C ≥ 1.0, project is economically
justified at discount rate applied
• If B/C < 1.0, project is not
economically acceptable
•
34Dr.Ahmed-Refat 2015
35. Static efficiency is defined as maximization
of net benefits for a single time period.
Many economic decisions that occur over
time are a series of static decisions.
Example: Shopping for Food
Choose groceries each week, consume them,
then start over again next week.
Static vs. dynamic
efficiency
35Dr.Ahmed-Refat 2015
36. A dynamic decision is one in which current
decisions have impacts on net benefits
arising in the future.
Many economic decisions with
environmental implications are dynamic.
Example: Forestry
If you choose to harvest trees this year,
harvesting next year is no longer an option.
Static vs. dynamic
efficiency
36Dr.Ahmed-Refat 2015
37. Key Point
Decisions are typically not made on the
basis of BCA alone…
but BCA can be useful for providing
information on economic features of
projects or activities, and can therefore be
useful for informing the debate.
37Dr.Ahmed-Refat 2015
39. Dam construction
Benefits:
Recreation = $400,000
Flood control = $300,000
Electricity = $500,000
Total Benefit =$1,200,000
BCA in a timeless world
39Dr.Ahmed-Refat 2015
40. Dam construction
Total Benefit =$1,200,000
Total Cost = 1,100,000
Net Benefit = 100,000
Benefit exceeds cost, so dam appears to be a good
investment
BCA in a timeless world
40Dr.Ahmed-Refat 2015
41. BCA as “Approach”
To know whether society should build the
dam, other information may be needed:
1. Are there non-economic impacts?
2. What is the opportunity cost of the dam?
.
41Dr.Ahmed-Refat 2015
42. Opportunity costs
• Opportunity cost is the cost of
what has to be given up to gain
some good or service
When choosing one option over
another.
42Dr.Ahmed-Refat 2015
43. Time and
Discounting
Often the benefits and costs of a project accrue
at different times. The technique used to deal
with this issue is discounting.
43Dr.Ahmed-Refat 2015
44. Discounting
Discounting is a technique used to convert all
benefits and costs to a common point in time,
usually the present.
The value of a project, expressed in terms of
the present, is called the Present Value.
44Dr.Ahmed-Refat 2015
45. Discounting
• Discounting is based on the idea that
a dollar of benefit received today is
worth more than a dollar of benefit
received in the future.
• Discounting is the opposite of
compounding.
45Dr.Ahmed-Refat 2015
46. Discounting
The rate at which a current value is
compounded is called the interest rate.
The rate at which a future value is discounted
is called the discount rate.
46Dr.Ahmed-Refat 2015
47. Computing a present
value
PV = Pt / (1 + r)t
PV = present value
Pt = value at time t
r = interest (discount) rate
t = year in which Pt is realized
47Dr.Ahmed-Refat 2015
48. Dam revisited
Total Benefits accrue
when dam is finished
(t = 1)
Total Costs accrue at
start of construction
(t = 0)
Discount rate = 10% Should the dam be built?
BCA with discounting
48Dr.Ahmed-Refat 2015
49. Total Benefits accrue when dam is finished (t = 1), so
Pt = $1,200,000 and PV of benefit is:
$1,200,000 / (1+0.10)1 = $1,090,909
Total Costs accrue at start of construction (t = 0), so
Pt = $1,100,000 and PV of benefit is:
$1,100,000 / (1+0.10)0 = $1,100,000
PV(B) < PV(C) The dam shouldn’t be built.
Dam construction revisited
49Dr.Ahmed-Refat 2015
50. Total Benefits accumulate in the future (i.e. when
dam is finished). The process of discounting
reduces the value of those benefits because they
occur in the future.
Because the merit of a project can hinge on the
choice of discount rate, it can be a source of debate.
There is no simple rule for choosing a discount rate.
Often a “well known” interest rate is used.
?
50Dr.Ahmed-Refat 2015
51. Whenever benefits and costs accumulate at different
points in time, amounts should be converted to
present values for comparison.
BCA is a decision-support tool, not a decision-
making tool.
Discounting can be used regardless of the length of
time under consideration, but discounting has
implications for equity.
Key Points
51Dr.Ahmed-Refat 2015