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A wide range of alternatives was considered for meeting Spokane County’s
wastewater management requirements. This chapter describes the evaluation
process used and identifies the alternatives considered. A detailed
discussion and comparison of the most feasible alternatives is presented
in Chapters 4 through 7. A summary of the preferred wastewater management
concept is presented in Chapter 9.
Alternatives were identified and evaluated through an interactive process
involving County staff, consultant staff, representatives from resource
and regulatory agencies, City of Spokane staff, the Spokane County Water
Quality Advisory Committee (WQAC), the Spokane County Board of County
Commissioners and the general public. Major elements of the evaluation
process are described below. More detailed discussion of the public
involvement process is presented in Chapter 8, and further discussion of
the Environmental Impact Statement (EIS) process is presented in the
separately bound EIS report. Error!
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identifies discussion topics at key review meetings during the course of
the study.
Define Process Methodology. To provide a consistent planning basis
and to gain timely input from stakeholders, HDR and County staff developed
an evaluation methodology for the wastewater management concepts. This
resulted in an integrated decision-making/public involvement process.
Initial Inter-Agency Symposium. In August 2000, a workshop was
held with regulatory and resource agencies concerned with regional water
quality and wastewater management issues. This meeting also included a
number of municipal and industrial dischargers to the Spokane River. The
workshop focused on the Basis of Planning findings and identified the
range of alternatives likely to be evaluated. Participants were invited
to suggest additional alternatives for consideration.
Initial WQAC Meeting. In August 2000, an introductory meeting was
held with WQAC members to summarize the Basis of Planning study and to
solicit input on the types of alternatives that should be considered.
Initial Public Meeting, EIS Scoping Session. In September 2000, a
public meeting was held to present key findings of the Basis of Planning
effort. This meeting also identified the types of wastewater management
concepts that were likely to be evaluated. A question/answer session and
a written questionnaire solicited the public’s input on their initial
reaction to the concepts and their recommendations for additional
alternatives to consider. This initial public meeting also served as the
formal Scoping Session for the EIS.
Evaluation Criteria. Based on input from County staff, Ecology
staff, consultant staff, stakeholder interviews and the public meetings
held to date, a set of criteria was developed for use in evaluating
alternatives. These are listed in Table 3‑1. Except for cost,
these criteria were applied on a non-weighted, qualitative basis.
Table
3‑1. Evaluation
Criteria
|
Capacity |
Regulatory
Compliance |
|
Meets near-term requirements (Year 2007) |
Meets anticipated effluent or biosolids quality requirements |
|
Meets Year 2025 requirements |
|
Expandable to meet 50-year needs |
Ease of permit compliance |
|
Technical |
Water Resource Enhancement |
|
Proven performance |
Increases direct reuse opportunities |
|
Low operational complexity |
Enhances conservation and use of regional water resources |
|
Low operational & maintenance intensity |
Environmental Impact 2 |
|
Reliability & longevity |
Surface water |
|
Conveyance |
Groundwater |
|
Low construction requirements |
Fisheries |
|
Low complexity |
Bird and wildlife habitat |
|
Reduces CSO problem |
Air quality |
|
Implementation |
Soil |
|
Permitting/approval requirements |
Non-point water quality |
|
Property/ROW acquisition |
Community Impact 2 |
|
Ease of siting |
Construction activities |
|
Ability to logically phase expansion |
Public health and safety |
|
County Control |
Land use |
|
Ability of County to implement independent of other agencies |
Odor |
|
Noise |
|
County’s long-term control over wastewater management |
Vectors |
|
Traffic |
|
Risk 1 |
Open space |
|
Potential for practice to fail due to changes in future regulation,
public perception, land use |
Recreation/resource awareness |
|
Economics |
|
Reliance on private entity that may relocate, change operation or
greatly increase cost |
Construction cost/cash flow |
|
Operations cost |
|
|
Land acquisition cost |
|
Life cycle cost |
1.
For treatment location alternatives, the risk criterion was
replaced by a “financial risk” criterion. This is explained in Chapter 6.
2.
For treatment location alternatives, the environmental impact and
community impact criteria were combined into a single “impact” criterion.
Brainstorm and Screen Ideas. In October 2000, a three-day workshop
was conducted to identify potential alternatives for managing wastewater
generated in the Spokane County Service Area. Following the brainstorm
session, an initial screening step was conducted to eliminate ideas that
were fatally flawed, technically unproven, excessively expensive or
otherwise unworthy of detailed evaluation.
Detailed Development and Evaluation. Alternatives surviving the
initial screening step were evaluated in detail. Facility sizing and cost
estimating were based on a 25-year planning horizon, although
consideration was given to expanding the concepts to meet 50-year growth
projections. Alternatives were compared based on cost and non-economic
criteria. Results were summarized in draft report chapters.
Second Round of Public, Inter-Agency and WQAC Meetings. In January
2001, during development of the alternatives, a second round of
workshops was held with regulatory and resource agencies, Spokane River
dischargers, WQAC members and the general public. These meetings
identified the alternatives being evaluated in detail and presented
initial observations on the advantages and disadvantages of the concepts,
but did not present information on cost or results of the comprehensive
evaluation. The intent was to inform stakeholders as to the final
alternatives being considered and to gain input as to whether the study
was properly focused.
Review Workshops. During the alternatives development process,
meetings were conducted with County staff to review interim findings and
refine the alternatives being evaluated. As part of this process,
participants compared the alternatives against the evaluation criteria.
Preliminary Preferred Wastewater Management Concept. Following
review of the various alternatives, the project team developed preliminary
recommendations for the preferred wastewater management concept. These
recommendations are summarized in Chapter 9.
Review Workshops with City of Spokane, Ecology and WQAC. In April
2001, individual meetings were held with City of Spokane wastewater
management staff, representatives from the Department of Ecology and the
WQAC to review the evaluation process, discuss the preliminary
recommendations for the preferred wastewater management concept and
solicit comments on how to improve the preliminary recommendations.
Briefing Workshop with Spokane County Board of County Commissioners (BOCC).
In early May 2001, the Spokane County BOCC was briefed on the status
of the facilities planning effort, and provided an overview of the
preliminary recommendations for the preferred wastewater management
concept.
Third Round of Public and Inter-Agency Meetings. In late May 2001,
a third round of public and agency meetings was held to present the
results of the evaluation and to identify preliminary recommendations. A
meeting was also held with the SCWQAC at this time. Each group was asked
to comment on the findings.
Decision Workshop. Following the meetings with the City of Spokane,
Ecology, WQAC, BOCC, the public and agencies, the project team met to
consider the comments received and to adjust the recommended plan in
response to accepted comments. Since each of the groups was generally
supportive of the recommendations presented, only minor revisions were
needed to produce a final plan.
Refinement of Preferred Wastewater Management Concept. A plan was
developed to guide implementation of the recommended wastewater management
concept. This effort included evaluation of financing methods, facility
siting requirements, permitting and environmental documentation
requirements, and public and private approaches for construction and
operation.
During the brainstorming session, more than 80 ideas for wastewater
management were identified. During a subsequent screening session, the
each idea received one of the following designations:
·
Retain. Carry idea forward into detailed analysis.
·
Retain, merge with similar idea. Valid idea, combine
with one of the retained ideas carried forward into detailed analysis.
·
Retain, evaluate later. Valid idea, evaluate during
development of the implementation phase of the facility plan once a
preferred wastewater management concept has been identified.
·
Retain, not in scope. Valid idea, but outside of the
scope for this study. Address in concurrent or future studies.
·
Fail. Idea is fatally flawed. Do not carry forward
to detailed analysis.
A full listing of the ideas identified is presented in
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Table 3‑2 summarizes the number of ideas generated and the initial
screening results.
Table
3‑2. Summary of
Initial Brainstorm and Screening Session
|
Wastewater Management Area |
Number of Ideas by Screening Designation |
|
Retain |
Retain, merge with similar idea |
Retain, evaluate later |
Retain, not in scope |
Fail |
Total |
|
Demand Management |
9 |
8 |
0 |
1 |
10 |
28 |
|
Effluent Management, Disposal & Reuse |
11 |
3 |
0 |
0 |
3 |
17 |
|
Biosolids Management |
7 |
2 |
0 |
1 |
6 |
16 |
|
Treatment Plant Location |
5 |
0 |
0 |
0 |
2 |
7 |
|
River Management |
0 |
0 |
0 |
2 |
1 |
3 |
|
Institutional Arrangements |
0 |
0 |
11 |
0 |
0 |
11 |
|
Total |
32 |
13 |
11 |
4 |
22 |
82 |

Figure 3‑1.
Components of the Overall Wastewater Management Concept
|
Development of a preferred wastewater management concept requires
determination of the four components shown in Figure 3‑1.
Following the initial brainstorming and screening steps, the alternatives
remaining in these management areas were developed in detail, and compared
against evaluation criteria. This section identifies the alternatives
evaluated, presents major design criteria used in development of the
alternatives, and describes the cost estimating methodology.
Table 3‑3. lists the
alternatives considered for the four major components comprising the
overall wastewater management program.
An array of design criteria was established to guide development of the
wastewater management alternatives.
Planning Horizon
Generally, the alternatives were developed and compared based on flow and
loading projections for the year 2025. This would allow nearly 20 years
of operation following implementation. Consideration was also given to
the ability of the alternatives to handle projected flows and loadings in
the year 2050. This long-term view allows the alternatives to be compared
with respect to expandability, and flexibility to meet future changes in
land use, regulation and public perception.
Flows and Loadings
Flow and loading projections are summarized in Chapter 2, and are
discussed in detail in the Basis of Planning Report.
Effluent Quality Requirements
The effluent quality requirements will vary for the range of effluent end
use alternatives being considered. Specific requirements are presented in
Chapter 5 for each alternative.
Table 3‑3.
Alternatives Subjected to Detailed Analysis
|
Component |
Alternatives |
|
Demand Management |
Water conservation |
|
|
Public education
Economic incentives
Increased metering
Fixture replacement |
|
|
Infiltration and inflow control
Sewer rehabilitation
Removal of sump connections
Improvements to codes and procedures |
|
|
Industrial and commercial load reduction
Pretreatment limits or prohibitions on selected wastewater
constituents
Surcharges on high strength wastes
Industrial and commercial recycling |
|
Effluent End Use |
Discharge to Spokane River
Discharge to Little Spokane River
Flow augmentation in small tributary streams
Irrigation of agricultural land
Irrigation of poplar farms1
Irrigation of urban green spaces
Wetlands creation or enhancement
Industrial reuse
Groundwater recharge |
|
Treatment and Conveyance |
Send all flow to SAWTP |
|
|
Distribute flow between SAWTP, new In-City Plant and new North Spokane
Plant
SAWTP at 10 mgd; No Plant in North Spokane
SAWTP at 10 mgd with North Spokane Plant
Increased Flow to SAWTP
North Spokane Only to SAWTP
No Flow to SAWTP |
|
|
Distribute flow between SAWTP, new Mid-Valley Plant and new North
Spokane Plant
SAWTP at 10 mgd; No Plant in North Spokane
SAWTP at 10 mgd with North Spokane Plant
Increased Flow to SAWTP
North Spokane Only to SAWTP
No Flow to SAWTP |
|
|
Distribute flow between SAWTP, multiple Mid-Valley Plants and new
North Spokane Plant
Two Mid-Valley Plants; No Plant in North Spokane
Two Mid-Valley Plants with North Spokane Plant |
|
Biosolids Management |
Class B Biosolids and Land Application
Class A Treatment (Thermal Treatment) and Land Application
Composting
Treatment at SAWTP
Privatized Management
Co-Incineration with Solid Waste |
1. Added during planning process
in response to public comment.
Process Sizing Criteria
These criteria specify design loading rates and operating parameters for
critical unit treatment processes. Examples include clarifier overflow
rates, aeration basin mixed liquor concentrations, and filter loading
rates. Where applicable, the Washington State Department of Ecology’s
Criteria for Sewage Works Design
[i] were used.
Otherwise, conventional design methodologies were used.
For sewers, year 2050 flow projections were used as the basis for design.
Sizing was based on a maximum water depth of 0.7 times the pipe diameter
under peak flow conditions.
Reliability/Redundancy Criteria
For wastewater treatment and pumping stations, the redundancy criteria
presented in Table 3‑4 were applied.
Table
3‑4. Redundancy
Criteria for Unit Treatment Processes
|
Criteria No. |
Description |
|
Liquid Treatment Systems |
|
1 |
Handle peak instantaneous flow without overflows with all units in
service |
|
2 |
Pumping facilities must handle peak instantaneous flow with largest
unit out of service |
|
3 |
Provide full treatment to maximum-day flow with all units in service |
|
Solids Treatment Systems |
|
4 |
Handle maximum-week solids loading with all units in service |
|
Liquid and Solids Treatment Systems |
|
5 |
Handle maximum-month flow or loading with largest unit out of
service (winter condition) |
|
6 |
No extraordinary manual operation is required if largest unit is out
of service |
For wastewater force mains, redundant pipelines will not be provided;
however, multiple pipelines may be needed to accommodate the range of
flows expected over the life of the facility.
Standby power will be provided for treatment plants and pumping stations.
Treatment plant facilities will meet EPA’s Class I reliability
requirements, with the added demand of keeping the biological process
viable during a prolonged power outage.
Capital Costs
Capital costs are expressed in January 2001 dollars (ENR Cost Index 6281),
and should be viewed as “planning level” estimates. These estimates are
approximations made without detailed engineering or site-specific data.
Estimates of this type can be expected to vary from 50 percent less than
to 30 percent more than actual final project costs.
The sources of construction cost data are:
·
HDR’s ENVision cost-estimating program based on national
cost curves that HDR developed for the U.S. EPA, adjusted to regional
market conditions and 2001 dollars.
·
Recent construction costs for other, similar facilities,
adjusted to regional market conditions and 2001 dollars.
·
Recent construction costs for the County’s pipeline and pump
station projects, adjusted to 2001 dollars.
·
Equipment pricing from manufacturers, including
installation, structure, and housing costs.
All capital costs include allowances for site work and yard piping;
contractor mark-up; contingencies; and engineering, legal and
administration costs. The cost estimating procedure is presented in
Table 3‑5.
Table
3‑5.
Illustration of Capital Cost Estimating Procedure
|
Cost Item |
Cost |
|
Base Construction Cost |
$1,000,000 |
|
Site work |
$100,000 |
|
Electrical and Controls |
$150,000 |
|
Subtotal A |
$1,250,000 |
|
Design Contingency – Misc. Costs Not itemized (20% of A) |
$250,000 |
|
Subtotal B |
$1,500,000 |
|
Mobilization and Bonds (5% of A) |
$75,000 |
|
Contractor’s Overhead and Profit (10% of B) |
$150,000 |
|
Subtotal C |
$1,725,000 |
|
Washington State Sales Tax (8.1% of C) |
$138,000 |
|
Subtotal D (Construction Bid Price) |
$1,863,000 |
|
Construction Contingency - Change Orders (5% of D) |
$93,000 |
|
Subtotal E (Total Construction Cost) |
$1,956,000 |
|
Engineering, Legal, Administration (25% of E) |
$489,000 |
|
Total Capital Cost |
$2,445,000 |
Operating Costs
Operating costs were developed for projected flow and loading conditions
in 2015, the mid-point of the initial 20-year operating period. The
following unit factors were used:
·
Labor - $31.50/hour
·
Maintenance – 5% of installed equipment
·
Electrical power - $0.06/kwh
·
Natural gas - $0.83/therm
·
Aluminum sulfate – $120/ton
·
Polymer - $10/dry ton of dewatered sludge
Land Costs
Property acquisition costs were based on the following estimated land
costs:
·
North County -$20,000/acre
·
Spokane Valley (highly developed areas) - $100,000/acre
·
City of Spokane (highly developed areas) - $140,000/acre
Present Worth Analyses

[i]
Washington Department of Ecology,
Criteria for Sewage Works Design, 1999.
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