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The probable OpInIOn of capital costs for the upgrading the City' s WWTP by
11 incorporating an oxidation ditch process is summarized on Table 4- 3. As with the
other reviewed alternatives, these costs were based on unit prices obtained from
j recent bid experience with upgrades to similar wastewater treatment facilities, as well
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as infonnation obtained from manufacturers of the equipment to be supplied. As
indicated on Table 4- 3 the total probable opinion of cost for the upgrades to the City' s
WWTP is estimated to be approximately $4, 262, 500.
4. 2.3.2 Scheduling and Sequencing
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Based on the proposed plan described above it is anticipated that the overall program
can also be completed within 2 years from inception, with no downtime of the
facilities required. It is anticipated that final design and permitting associated with
this alternative would take approximately 4- to 6- months to complete, including
review periods. Similar to the other alternatives considered, bidding, review and
recommendation for award will require 2- months to complete. Construction of the
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improvements would take approximately 16- months to reach substantial completion.
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During the last 2- months start- up and operational modifications to bring the system
ill on line would take place. Based on our experience construction can proceed on the
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new facilities without impacting the operation of the existing RBC system.
Once the construction of the recommended improvements is completed, the necessary
r yard piping to connect the new process structures would be connected, the equipment
tested and certified, and the aeration basin seeded. A portion ofthe influent flow will
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1 then be diverted to new process tankage to acclimate the biomass in the unit. Once
the new process is acclimated, the existing RBC facilities will then be
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decommissioned and equipment removed, and all influent wastewater will flow
through the new process tankage, for treatment.
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TABLE 4- 3
lilt CITY OF FORT WALTON BEACH
II WASTEWATER TREATMENT PLANT
PROBABLE OPINION OF CAPITAL COSTS
OXIDATION DITCH
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Description of Work Cost
I RBC Equipment Removal and Disposal 20, 000
Flow EQ Mixers/Rails/ Supports 150, 000
I Oxidation Ditch Structure
Additional Excavation to Maintain Hydraulic Profile
1, 600, 000
250, 000
Mechanical Aerators ( 2 - 150 HP) 500, 000
I Electrical Modifications 250,000
110, 000
Recycle Wetwell
Recycle Pumps 115, 000
I Yard Piping
Influent & Effluent Weir Gates ( includes recycle wetwell)
350,000
25, 000
Generator ( supplemental capacity) 40. 000
I SUB- TOTAL 3, 410,000
I Engineering, Contingency, Permitting @ 25% 852. 500
TOTAL 4. 262. 500
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i. 4.3 PRESENT VALUE ANALYSIS
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The proposed alternatives that were evaluated to upgrade the City' s WWTP facilities will
improve the level of service presently provided to the City's wastewater customers, as well as
I meet the rules and regulations, which govern the treatment of wastewater.
information researched for the improvements, modifications, and/or upgrades that are required
Based on the cost
for the existing wastewater facilities, a 30- year present value analysis was performed.
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To accurately weigh the financial components of each alternative, the historical operating
I expenses, projected operating expenses, and projected capital costs were utilized to determine a
present value. The present value analysis for each wastewater treatment facility alternative was
I for a 30- year service life utilizing data provided by the City and several other considerations and
assumptions which are summarized below:
I 1. Operating and maintenance ( O& M) expenses remained constant for the purpose of
comparing the various wastewater treatment alternatives.
I 2. The operating and maintenance expenses were estimated from the City' s Wastewater
Utilities Fund, power costs were projected, and labor expenses were estimated.
I 3. Capital costs were projected utilizing actual component replacement costs from City
records as well as unit costs obtained from bid experiences of similar wastewater
I facilities and cost estimates from equipment suppliers.
4. An analysis period of 30- years was used, together with an assumption of a discount
r rate of 5- percent.
5. An average capital inflation rate of 2. 72- percent was assumed as reported in the
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Engineering News Record ( ENR) and Handy- Whitman Index ( HWI).
6. An average operating inflation rate of2.5- percent was assumed.
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7. Average service lives were assumed for each process component based on industry
standard values.
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The present value analysis performed for each of the treatment alternatives included the
estimated construction cost and the present worth of O& M costs. Construction costs were
f, estimated based upon vendor' s quotations, estimated installation costs, cost data for similar
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projects, and published cost data, as previously discussed.
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The O& M costs utilized for this analysis included the cost of labor, power, and normal
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replacement parts. Inflated component replacement costs are added to the present value analysis
at the end of each components average service life ( ASL). A residual value was added back to
the present value for components with a useful life remaining after the 30- year analysis. These
Un residual values were based on an assumed ASL and straight- line depreciation over the ASL for
each component. The estimated capital costs and component residual values for each alternative
are shown in Tables A-4, A-5, and A-6.
4.4 CONCLUSIONS
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The purpose of this section of the report was to evaluate several wastewater treatment
I alternatives utilizing a present value analysis. As described previously, a 30- year proforma
analysis was based on projected capital and O& M costs for each of the three alternatives. In
Iii!! summary, the following conclusions were developed:
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1. The resulting present value of Alternative 1 was $ 5, 887, 585. A residual value of
I 950, 000 was assumed for equipment with a remaining service life and this value
was applied to the present value. The total present value of Alternative 1 is
I 4, 937, 585 as shown in Table A- 7.
2. The resulting present value of Alternative 2 was $ 5, 298, 999. A residual value of
I 656, 250 was assumed for equipment with a remaining service life and this value
was applied to the present value. The total present value of Alternative 2 is
I 3.
4, 642, 749 as shown in Table A- 8.
The resulting present value of Alternative 3 was $ 6, 715, 312. A residual value of
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I' 925, 000 was assumed for equipment with a remaining service life and this value
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was applied to the present value. A total present value of Alternative 3 is $ 5, 790,312
as shown in Table A- 9.
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The present value analysis for each of the wastewater treatment alternatives is summarized in
Table 4- 4. The results of the present value analysis are included in Section 5 as a part of a
weighted analysis and is relative only in conjunction with the circumstances presented herein and
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made part of such projections, and no assurances are
