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ERDC TN-DOER-C27
July 2002
disposal, and quantity suitable for beneficial use. Methods for estimating recoverable and
residual volumes follow in the section titled "Volume Reduction Estimating."
b. Calculate interest during construction (IDC).
IDC must be calculated for each
construction (new work) year using Equation 1.
c. Calculate initial investment. The initial construction cost will equal the sum of all
construction costs and IDC for each construction year.
d. Develop maintenance dredging cycle and associated costs, including mobilization/
demobilization, dredging, dewatering, separation, transportation, and placement.
Sufficient placement capacity (either CDF or offsite) must be available to accommodate
all residual maintenance material for the entire period of analysis. All associated
placement costs for the disposal alternative, such as CDF construction or expansion,
facility maintenance costs, and transportation and unit disposal costs, must be developed
and included. Timing for future costs must be established.
e. Calculate net present value (NPV). Determine NPV of all costs, including construction
costs, IDC, and anticipated future expenditures. These calculations are completed using
Equation 2.
f. Compute the AAEV for each alternative using Equation 3.
g. Select the separation alternative. If more than one separation alternative is being
considered, these steps must be completed for each alternative.  The least costly
alternative that accommodates all future maintenance material, including initial
investment, IDC, and future maintenance costs, is the selected separation option. The
selected plan will have the lowest AAEV.
IV. Calculate Benefits from Separation. The benefit to separation is the savings between the
annualized base condition costs and the annualized selected separation alternative costs. If
separation is not more efficient than the base plan, the benefits from separation will be negative.
Among separation alternatives with comparable benefits, intangible benefits, such as reduced
contaminant emissions or habitat creation, may be factored into the final selection.
VOLUME REDUCTION ESTIMATING: Economic analysis requires estimation of in situ
sediment volumes and relative volumes of recoverable materials and residuals requiring disposal.
Procedures for estimating the percent material by mass meeting BU specifications (recoverable
materials) were presented in Olin-Estes and Palermo (2000a). Mass and volume percentages are
not equivalent, however, and this is central to the concept of volume reduction. The volume
represented by a given mass percent of sand, for example, is a function of the specific gravity of
the relative sediment fractions and the void ratio of the material. The relative proportions and
specific gravity of the principal sediment fractions (sand, fines, organics) and in situ void ratio can
be determined from bench-scale characterization of the material to be processed. Nomographs were
developed for a hypothetical material to illustrate the variation in percent sand by volume versus
percent sand by mass (Figure 5). Similar nomographs can be developed using site-specific
information and the mathematical and geotechnical relationships describing the sediment fractions
for a unit mass of sediment. By bounding the analysis within a range of values representative of
8

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