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DISCOUNTING
The benefits received by the public or by an individual from government and
private expenditures often are experienced at approximately the same time that
the costs are incurred. This, however, is not always true. In the case of the
Environmental Management program, 90 percent of costs will be incurred over the
next 45 years; however, many of the benefits will be experienced far after this
period. Therefore, in programs such as the Environmental Management program,
the time at which benefits and costs are experienced becomes an important
consideration.
For example, a dollar spent in ten years is worth less than a dollar spent today
because today's dollar could be invested in a savings account or another
investment and be worth more than a dollar in ten years. For this reason,
policy analysts "discount" future costs and benefits so that all costs and
benefits are evaluated at their worth in terms of today's dollars. Intuitively,
"discounting" implies that future costs and benefits are worth less than costs
and benefits received today. To determine how much less future costs and
benefits are worth, analysts typically apply a discount rate. For example, a
five percent discount rate implies that $1.05 received in one year is worth a
dollar today.
CHOOSING A DISCOUNT RATE
A major issue in discounting future costs and benefits is selecting the
appropriate discount rate. This choice often has a major effect on policy
analysis results (as discussed in the next section). Analysts emphasize the use
of two major variables to determine the proper discount rate. The first
variable is the rate at which people are willing to sacrifice present
consumption for future consumption. This is often called the time preference
rate or the social rate of time preference. Second, public projects use
resources that can be employed in private investment projects. Thus, if private
investment projects yield 15 percent, diverting resources from private
investment to public projects entails an opportunity cost of 15 percent or an
opportunity cost rate of 15 percent. The return on private investment is often
called the opportunity cost rate. The discount rate is usually approximated as
one of these two rates. Using an appropriate discount rate, policy analysts can
calculate the "present value"of streams of costs and benefits.
Based on analysis of the social rate of time preference and the opportunity cost
rate, the U.S. Environmental Protection Agency and the Office of Management and
Budget suggest using real discount rates (above inflation) of approximately
three percent to seven percent.
EFFECT OF DISCOUNTING ON BASE CASE AND ALTERNATIVE CASE COST ESTIMATES
Table E.1 displays life-cycle costs in constant 1996 dollars and present value
costs for the Base Case and nine alternative cases. The present value cost for
each case was calculated separately using a three percent and a seven percent
discount rate. Table E.1 also ranks the cases from least expensive (1) to most
expensive (10). As is evident from this presentation, discounting results in a
different relative ranking of the cases based upon cost. This is most evident
in the funding reduction case. In constant 1996 dollars, the funding reduction
case is the second most expensive case. In contrast, the present value cost of
the funding reduction case is the second least costly alternative. The major
reason for this difference is that the funding reduction case shifts costs
farther into the future. Shifting costs farther into the future translates into
a lower present value. To a lesser extent, costs for the delaying waste
disposal case are higher than those for the Base Case in constant 1996 dollars,
but have a lower present value cost than the Base Case. Discounting has little
effect on the relative cost ranking of the other cases because the time profile
of costs is similar for these cases.
Table E.1. Life-Cycle Costs for Base Case and Alternative Cases
| Base Case
|
$160 billion (5)
|
$96 billion (7)
|
$59 billion (6)
|
| Accelerating Stabilization and Deactivation
|
$159 billion (4)
|
$94 billion (6)
|
$59 billion (6)
|
| Delaying Waste Disposal
|
$161 billion (8)
|
$93 billion (4)
|
$58 billion (4)
|
| Funding Reduction
|
$199 billion (9)
|
$89 billion (2)
|
$48 billion (2)
|
| Iron Fence
|
$150 billion (2)
|
$90 billion (3)
|
$56 billion (3)
|
| Industrial
|
$155 billion (3)
|
$93 billion (4)
|
$58 billion (4)
|
| Recreational
|
$162 billion (6)
|
$96 billion (7)
|
$60 billion (8)
|
| Modified Green Fields
|
$166 billion (7)
|
$99 billion (9)
|
$61 billion (9)
|
| Maximum Feasible Green Fields
|
$272 billion (10)
|
$141 billion (10)
|
$80 billion (10)
|
| Minimal Action
|
$90 billion (1)
|
$51 billion (1)
|
$33 billion (1)
|
Chapter -1- / -2-
/ -3- / -4-
/ -5- / -6-
/ -7- / -8-
Appendix -A2- / -B-
/ -C- / -D-
/ -E1- / -E2-
/ -F- / -G-
/ -H- / Glossary
|