CHAPTER 6

 

PUBLIC INFRASTRUCTURE

 

 

6.1 PUBLIC INFRASTRUCTURE IMPACTED BY ILLAHEE CREEK

 

The primary public infrastructure systems in Illahee are sewer, water, and storm water and each of these systems is impacted in a significant way by Illahee Creek.  As stated in the transportation chapter, Illahee Creek essentially forces the roadway system to detour one and a half miles around the creek.  This impacts the water distribution system and especially impacts the sewer systems in the area as Illahee Creek also provides the general separation boundary between the city of BremertonÕs sewer basin area and the Kitsap County sewer basin area.  The storm water impact is one of trying to minimize or mitigate the effects of storm water on Illahee Creek as a salmon bearing stream.

 

Because the area is at near build out conditions no major capital improvement systems are currently planned for this area for sewers, water, or stormwater.  There are nevertheless, some major issues with sewers, water, and stormwater that need to be resolved by the community and other governmental bodies.

 

 

6.2   SEWER

 

Kitsap County provides the sewer infrastructure currently existing in Illahee.  Sewer service is provided along the Wheaton Way corridor and east along McWilliams Road where it serves developments primarily to the north.  See Figure 6.1.  Kitsap County notes the sewer system has been sized to accommodate growth in the basin area.

 

The City of Bremerton would be the logical provider of future sewer service to the area south of Illahee State Park and south of Sylvan Way due to formidable barrier of the canyons of Illahee Creek and the distance and cost to run the sewer connector lines.  This area is covered by the City of Bremerton in the Trenton Avenue Basin as noted in its 2005 Comprehensive Plan Update.

 

Because of the delicate ground water balance situation in this area and the necessity of groundwater to support baseflows in Illahee Creek, the advisability of sewers for the area around Illahee Creek is being questioned by the community.  Sewers diminish the water recharge of the basin area and can thereby diminish stream flow.  Recent studies note that one proposed development in the area will decrease the baseflow in Illahee Creek by a minimum of 15 percent.  Additionally, when sewer systems are provided the zoning density increases as does the commensurate impermeable surfaces, which also diminish groundwater recharge.  Other hydrological studies of this area point to the fact that this area is a recharge sensitive area, and sewers and stormwater runoff are not supportive of salmon in Illahee Creek.

 

Goals and Policies

 

Goal S-1         Provide the availability of sewer service to residents within the Illahee Community boundary where sewer systems already exist and where they are outside critical aquifer recharge areas.

 

 

Policy S-1        Require all new construction and remodel projects involving an increase in sewage beyond the existing capacity of the septic system to connect to sewer if within 200 feet of an existing line.

 

Policy S-2        Encourage property owners on shorelines or near other critical areas to maintain their septic systems in good operating condition or connect to an available sewer system

 

Goal S-2         Conduct additional hydrological studies of the critical aquifer recharge areas around Illahee Creek to determine the appropriate boundaries around the creek and the recommended policies and procedures necessary to ensure baseflow levels are maintained.

 

Policy S-3        Prohibit, under this Plan, the introduction of sewers into the critical aquifer recharge regions of Illahee Creek, until the necessary hydrological studies are completed.

 

Policy S-4        Require all newly installed septic systems within the critical aquifer recharge area be capable of returning essentially nitrate free effluent to drain fields.

 

 

6.3 WATER

 

General

 

The Illahee Community is served by only one water purveyor, North Perry Avenue Water District.  The Water System Plan (WSP) for the North Perry Avenue Water District has been prepared in accordance with Washington State Administrative Code 246-290-100 and the Department of Health ÒWater System Planning Handbook, April 1997Ó.  The WSP is on file at the District office located at 2921 Perry Ave NE, Bremerton WA 98310. 

 

History

 

The North Perry Avenue Water District was formed on November 24, 1942.  The original project consisted of construction of approximately 6.6 miles of water mains along North Perry Avenue from Riddell Road to Stoneway and adjacent streets.  Water supply was purchased from the City of Bremerton, and a 50,000 gallon tank on a 70 foot tower was constructed for storage near the corner of Olympus Drive and Sylvan Way.  Significant additions to the water system were made in the 1950s, including additional mains, new wells, booster station, and storage tank.  The District was expanded to two pressure zones.  The Illahee Water District, which operated a small system in the Illahee area, merged with North Perry in the 1960s, as well as the merger of a small, private system in the Gilberton area.  Negotiations between the District and the City of Bremerton in the 1970s resulted in an agreement on a joint service area boundary.  The agreement was signed in 1976, which resulted in transferring some customers to establish the current boundary between the two systems.  The present service area boundary was further defined in 1989 by agreement between the District and Silverdale Water District No. 16 and with Kitsap County PUD NO. 1.  The District service area currently covers approximately 12 square miles and has 12 wells in service, seven storage reservoirs, and more than 82 miles of water main.  Figure 6.2 denotes the boundaries of the service area.

 

 

Geography

 

Most of the service area is rolling with a ridge running north and south through the approximate center of the District.  A creek valley cuts through the District in an east-west direction near Brownsville.  The ground elevation varies from near sea-level at the eastern side of the District to approximately 460 feet at the highest point.  Steep slopes exist in some areas, and several small streams with steep side slopes intercept the service area.  The occasional occurrence of wetlands restricts building in some areas.  These topographic features affect the locations of water facilities and the method of serving the District.

 

Description of Facilities/Components

 

The District service area contains five pressure zones, ten source wells, two backup wells, and one well that is drilled but not yet in service.  The total sustainable capacity of the District is 3680 gpm.  Because the raw water quality is so high, the District does not perform water treatment, but does add chlorine to the water for the purpose of taste and odor control.  There are seven storage reservoirs, with a current total capacity of 4.75 MG, with 1.898 MG of standby/fire suppression storage.  There are more than 82 miles of water mains.  Much of the older pipe in the District is constructed of asbestos cement, and recent installations have used ductile iron pipe, with a typical diameters of 6 or 8 inches.  There are three pump stations.  One inter-tie exists between the District system and adjacent (Bremerton) systems, used only for emergencies.  A significant distance between the District system and other adjacent systems and the topography of the service area typically makes inter-ties infeasible.

 

Related Plans

 

Land use planning and coordination of capital facility planning on a regional basis is the responsibility of Kitsap County.  Water facilities are planned to accommodate and provide for the level of zoning and density included in the following related plans:

 

 

Zoning and Land Use

 

The Land use planning for the service area is controlled by Kitsap County.  The northwest part of the District is zoned for rural medium density, which provides for relatively large lots for residential use.  Regulations generally prohibit utility service for development in rural areas.  Most of the remaining portion of the District is zoned for low-to Ðmedium density residential use, with some commercial areas along H303 and other selected locations.  Past water system planning has been based on serving the use as it has developed.  Land use is generally consistent with zoning. 

 

 

Future Service Area

 

As part of its Capital Improvement Program, the District plans to construct new distribution piping in portions of its service area not currently served by water mains.  These service areas are undeveloped property within the current District boundaries.  Water service to these areas will generally be provided through developer extension agreements.

 

Design and Performance Standards

 

Any property owner developing a new plat of commercial property not served by existing water mains is required to design and construct a water main extension in accordance with the DistrictÕs current developerÕs standards and transfer title of the facilities to the District upon completion of the construction as a condition of acceptance.  Costs associated with the design and construction of these water main extensions are the responsibility of the developer.

 

Population Projections and Demand Forecasting

 

The Kitsap County Comprehensive Plan projects an average annual growth rate of 1.0% from 1997 to 2012 in unincorporated areas, however the historical average annual growth rate within the District has been higher.  A more conservative growth rate of 2.5% is being used for demand forecasting.  A second factor affecting demand is the overall weather condition and the weather pattern during the summer.  A third condition is the success of a conservation program. 

 

Recent Hydrologic Studies

 

Kitsap County has noted Category 1 and Category 2 Critical Aquifer Recharge areas next to Illahee Creek.  Additionally, recent hydrologic studies in the area have noted low baseflows in Illahee Creek and the discovery of a relatively porous separation layer between the shallow aquifer supplying the creek and the deeper aquifers that supply local wells.  This means that the use of wells within the hydraulic drawdown vicinity of Illahee Creek can result a decrease in the baseflow of the creek.

 

Goals and Policies

 

Goal W-1        Conduct hydrological studies of the well systems around Illahee Creek to determine the appropriate boundaries around the creek to ensure baseflow levels in the creek are maintained.

 

Policy W-1       Prohibit, under this Plan, the introduction of new wells in the regions of Illahee Creek, until the necessary hydrological studies are completed.

 

Policy W-2       Begin a water balance monitoring system comparing baseflows in Illahee Creek with drawdown rates of local wells.

 

 

6.4 STORM WATER

 

Historic Conditions

 

The Illahee Community is comprised of plateau areas and steep slopes and is primarily located on the east facing slope of a ridge that reaches approximately 500 feet above Port Orchard Channel.  The plateaus and hillsides were originally covered with forests and a variety of vegetation typically found in the Puget Sound.  The limited amount of surface water runoff generated in the forested environment was carried to small streams by many shallow swales and larger ravines. 

 

Existing Conditions

 

The existing stormwater conditions vary considerably from historic conditions according to long time residents.  Probably the greatest impact has been on Illahee Creek where local fishermen note the devastating effects of increased stormwater discharges on local trout and salmon fishing.

 

The storm water problems in Illahee are significant.  They mostly result from natural topography of steep and unstable slopes that cannot handle either a major single event storm, or a series of smaller storms in rapid succession.  These have been documented since the late 1960s and early 1970Õs when there were no stormwater mitigation requirements.  As storm water flushes through ravines during these storm events they create problems for the streams and ravines as well as the downstream property owners.  There are no easy fixes for these problems so they have existed for nearly 40 years.  The most recent acknowledgement of the problem with Illahee Creek occurred in the mid 1990Õs when a new culvert was being planned.  It was noted in the report for the culvert that a complete basin study was required to best understand how to deal with controlling the storm water in Illahee Creek.  To our recollection, no other studies have been undertaken since then.

 

More recently two significant stormwater related items have surfaced.  The first was a report entitled ÒIllahee Creek, A Stream Destined for DisasterÓ which highlighted problems with various issues, including stormwater surge problems.  The second was a statement of area stormwater problems via a Department of Ecology grant application submitted by the Port of Illahee.  The PortÕs grant scored high in the State of WashingtonÕs rating system and is likely to be funded.  This will allow the necessary studies to be conducted to determine how to resolve the areas storm water problems.

 

Goals and Policies  

 

Goal SW-1  Support development of a comprehensive approach to storm water management.

 

Policy SW-1     Review all new developments to ensure coordination with regional                         storm water system planning.

 

      Policy SW-2     Use environmentally proven methods to enhance runoff                                                 quality and control runoff rates.

 

      Policy SW-3     Involve the Illahee Community in the assessment and prioritization                      of storm water capital facility projects.

 

      Policy SW-4     Identify areas needing improved storm water infrastructure within                               the Illahee Community.

 

Goal SW-2  Encourage storm water management systems that preserve natural drainage systems such as streams and construct facilities that complement these systems by taking advantage of opportunities for filtration , infiltration, and flow control where feasible and reasonable.

 

      Policy SW-5     Preserve stream and natural drainage systems.

 

      Policy SW-6     Identify the remaining areas of the natural drainage system in the                                  CountyÕs Geographical Information System as critical drainage                                       areas.

 

Goal SW-3  Limit the amount of impervious surface that can be created on individual residential lots to reduce future increases in storm water runoff.

 

      Policy SW-7     Limit impervious surface for each residentially zoned lot to a                                          maximum of 50% on lots less than .50 acre and 40% on lots more                                 than .50 Acre.

 

      Policy SW-8     Encourage the use of permeable surfaces and other new                                             technologies in building construction and property development.

 

 

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