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DUBLIN RANCH
REGIONAL WATER QUALITY CONTROL BASIN
STAGE 2 DEVELOPMENT PLAN / SITE DEVELOPMENT REVIEW
RE-SUBMITTAL
ATTACHMENT 3
Dublin California, July 2005
Dublin Ranch Area H Water Oualitv Control Basin -Januarv 2005
TABLE OF CONTENTS
1. APPLICATION FORMS
Planning Application Form
2. PROJECT REFERENCE
Vicinity Map
Context Plan
3. STAGE 2 DEVELOPMENT PLAN - PROJECT DESCRIPTION
Introduction
Background
Existing Land Use and Site Conditions
Design Concept / Theme
Proposed Uses
Site Areas/Setbacks
Water Quality Treatment Parameters
Basin Features
Maintenance and Emergency Access
Pedestrian Paths
Fencing
Lighting/Power Service
Public Art Component
Landscape and Planting Design
Irrigation System
Ownership and Maintenance
Vector Control - Mosquito Abatement
Project Phasing
4. STAGE 2 DEVELOPMENT PLAN - FINDINGS STATEMENT
5. SITE DEVELOPMENT REVIEW
Project Description
Drawing Reductions
Water Quality Control Basin - Table of Contents ·Page I of 2
Dublin Ranch Area H Water Qualitv Control Basin -January 2005
SHEET INDEX
L 0.01 COVER SHEET
L 1.00 ILLUSTRATIVE PLAN
L 1.10 SITE PLAN
L 1.20 STREETSCAPE CONCEPT PLAN
L 2.00 GRADING / DRAINAGE PLAN
L 3.00 PLANTING SCHEDULES
L 3.10 TREE PLANTING PLAN
L 3.20 GROUNCOVER AND SEEDING PLAN
L 3.30 IRRIGATION PLAN
L 4.00 SITE SECTIONS
L 5.00 SITE RENDERING KEY
L 5.10 SITE PERSPECTIVE VIEW 1
L 5.20 SITE PERSPECTIVE VIEW 2
L 5.30 SITE PERSPECTIVE VIEW 3
L 5.40 SITE PERSPECTIVE VIEW 4
L 5.50 SITE PERSPECTIVE VIEW 5
L 6.00 SITE DETAILS
L 6.]0 SITE FURNITURE AND LANDSCAPE PRECEDENTS
L 6.20 STREETSCAPE DETIALS
6. PRELIMINARY TITLE REPORT (previously submitted)
7. PUBLIC NOTICE MATERIALS (previously submitted)
Appendix A: Detailed Planting Design Description
Appendix B:Email Correspondence from Keith H. Lichten, P.E. , Acting Section
Leader San Francisco Bay Regional Water Quality Control Board, regarding
general approval of revised basin design.
Appendix C: Alameda County Mosquito Abatement District Review Letter.
Appendix D: Maintenance and Operations Program
Water Quality Control Basin - Table of Contents ·Page 2of2
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Dublin Ranch Area H Water Oualitv Control Basin -January 2005
PROJECT DESCRIPTION
for
DUBLIN RANCH - REGIONAL WATER QUALITY CONTROL BASIN
Stage 2 Development Plan/Site Design Review
Introduction
The Regional Water Quality Control Basin (WQCB) is required by the California Regional Water
Quality Control Board (RWQCB), according to the terms of Transmittal of Order No. R2-2003-
0032, Water Quality Certification and Waste Discharge Requirements, Dublin Ranch Project,
dated April 22, 2003. The WQCB is the primary storm water treatment feature identified in the
Storm Water Management Plan (SWMP) for the Dublin Ranch Project.
Approval of a Stage 2 PD rezone application for the WQCB project is required by Section
8.32.030B of the Dublin Zoning Ordinance. The WQCB is located in Area H of Dublin Ranch
between Tassajara Road to the west, Fallon Road to the east, 1-580 to the south, and Dublin
Boulevard to the north. The Eastern Dublin General Plan, Specific Plan, and PD designate the
proposed site area as "Campus Office," The area directly to the west of the planned development
is designated as General Commercial. The Stage 2 Planned Development Rezone covers 11.13
acres.
This submittal includes a listing of proposed uses, data on site area, and textual information
sufficient to establish consistency with the Eastern Dublin General Plan and Specific Plan.
Background
Subsequent to the development of the SWMP, schematic plans for the WQCB were developed
and reviewed by the RWQCB. The schematic plans serve as the functional basis of the proposed
development plan. The location and landscape design of the WQCB have been further refined
based upon existing storm water infrastructure, site characteristics, water quality treatment
parameters, and compatibility with potential development of adjacent areas. The revised plans
were submitted to the RWQCB staff in September 2004, to confirm ongoing compliance with the
permit. The WQCB design has been further refined as part of an integrated planning effort for
adjacent parts of Area H, to ensure compatibility with access, circulation and site design.
Existing Land Use and Site Conditions
The Stage 2 PD area is currently vacant land. No residences or other structures exist within the
boundaries of the Stage 2 PD area. The existing topography across the site is very flat, sloping
from south to north at approximately 0.5%. Elevations range between elevation 343.00 and
340.00, with exception of a low landform at elevation 347.00, created above the recently
completed G3 box culvert on the southern edge of the site. The adjacent grades in the
development area will be raised to elevation 347.00 as part of the grading of the basin. 1-580
forms the southern edge of the area.
A Phase I and 2 Environmental Site Assessment of the Stage 2 PD area and surrounding areas
has been conducted by Berlogar Geotechnical Consultants to determine the presence of any
hazardous waste and substance sites. The findings of these studies indicated that no problem sites
Water Quali(v Control Basin ~ Stage 2 Planned Development Project Description .Page I of 7
Dublin Ranch Area H Water Oualitv Control Basin -January 2005
were found. Geotechnical investigations of the Project Area and surrounding areas have been
conducted by Berlogar Geotechnical consultants to determine the soil condition and stability; the
studies indicated no areas of concern within the project area. The recommendations and
conclusions of the study are referenced in the Geotechnical Report: Dublin Ranch - Pao - Y eh Lin
Property dated August 30, 1999,
Design Concept/Theme
The beauty of the existing rolling topography and natural countryside is the basis for the Dublin
Ranch landscape concept and planting theme. The primary goal of the WQCB design concept is
to integrate the basin into the surrounding area as an open space amenity.
The design concept is to create a park like environment based upon the picturesque qualities of
the regional California landscape, combined with ecological and naturalistic aesthetics. The
water quality functions and infrastructure are integrated into a picturesque landscape with rolling,
sculptural landforms and distinct groupings of trees, which create a sense of depth and enable
distinct views. Site improvements will have a contemporary but rustic quality. The design
concept anticipates public access associated with future Area H uses, by including walking paths,
overlooks and seating areas in the design. The overlook areas are framed by rustic, dry laid
boulder walls, which create a sense of place and contrast with the rolling topography. The north
edge of the basin has been developed as a pedestrian promenade with a more urban park character
compatible with future adjacent streetscape and uses. The basin is largely screened by low
landforms and tree planting on the east, west and south edge, while a frontage landscape has been
developed along the 1-580 corridor. The frontage landscape provides visual relief and continues
the picturesque theme with low sweeping landforms and rows of trees.
By treating the basin as a designed landscape, and considering its location, layout, and visual
qualities, the proposed design successfully integrates water quality function, public open space,
and ecological value.
Proposed Uses
The Development Plan covered by this Stage 2 PD proposes 2.34 acres of open space with public
access, 7.16 acres of open space for stonn water treatment, and 1.18 acres of open space
associated with the 1-580 frontage. The project will provide for maintenance access associated
with ongoing landscape maintenance, vector control, and stonn water facilities. The project
includes a below grade pump station, accessed by a manhole.
Open space/recreational areas are provided in anticipation of the future adjacent development.
Open Space areas with public access include designated paths and overlook seating areas along
the upper edges of the basin. These areas will enable passive recreational uses such as walking,
jogging, picnicking, cycling, and dog walking. A public access easement will not be placed
over the property but the public will be allowed to use the perimeter trail system subject to
certain restrictions. Public use will be restricted between dusk and dawn.
Water Qualitv Control Basin - Stage 2 Planned Development Project Description -Page 2 of 7
Dublin Ranch Area H Water Qualitv Control Basin -Januarv 2005
Site Area
Open space - Public Access:
Open space - Storm water Area:
Open space - 1-580 Frontage landscape
Total Site Area:
2.34 Acres
7.16 Acres
1.18 Acres
10.17 Acres
Percent Landscaping:
80%
Site Area Dia2ram
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Setbacks:
The top slope of the basin is set back a minimum of approximately 20' from the proposed
parcel boundary. The open space area at the top of the basin creates a buffer zone, which
will be planted with trees.
Water Quality Control Basin - Stage 2 Planned Development Project Description -Page 3 of 7
Dublin Ranch Area H Water Oualitv Control Basin -Januarv 2005
Water Quality Treatment Parameters
Water Quality Treatment Volume: In accordance with the Storm Water Management Plan
(SMWP), the proposed design meets the water-quality treatment volume of 19.5 acre-feet, with a
target holding time of 48 hours,
Required Surface Area: As per the SMWP, the minimum surface area set aside for the water
quality treatment portions of the basin will be approximately 4.0 acres at an elevation of 333.00
feet. The proposed development plan provides a water quality surface area of 4.0 acres.
Operating Depth: As per the SMWP and schematic plans, the average lowest elevation of the
basin floor (outside the permanent pools) will be approximately 328.00 feet. This will give an
average water quality depth of 5.0 feet at elevation 333.00. For the large and/or closely spaced
storms that completely fill the water quality volume. Once the water quality volume has been
reached, the depth of the basin will continue to increase at a reduced rate to a maximum elevation
of 344.00, associated with the 100-year storm event. The average depth at this point will be 16
feet, with deeper areas associated with the forebays, low flow channel, and permanent pool.
Basin Features
Inlet Design: Two diversion structures direct gravity flow through 48" pipes to the basin. The
design of the diversion structures allows the required treatment volume to enter the basin until the
basin fills to the flowline of the main storm drain line. At that point, the majority of runoff flows
directly into the G3 channel bypassing the basin. For large and/or closely spaced storms, storm
flow will continue to flow into the basin after the water quality volume and elevation are reached,
however most of the water will flow directly to the G3 channel. The inlets will be surrounded by
concrete headwalls as needed.
Basin Side Slopes and Grading: The grading design creates a sinuous landform. A variety of
side slopes are created with maximum slopes of 3H: 1 V, with exception to a stabilized 1.5H: 1 V
slope adjacent to the permanent pool to allow for the outfall structure. The shape of the basin
landforms creates visual interest while being efficient and maintainable.
Sedimentation Forebavs: Storm water will enter the basin at two inlet points and discharge into
the forebays, The sedimentation forebays will be permanent pools ringed by native plants. The
forebays are approximately 150 feet in length and have a bottom width of 50 feet. The forebay
water surface is determined by a weir at elevation 324.00. The side slopes ofthe forebay are
2V: 1 H and the depth is set at 5 feet to minimize invasi ve emergent growth and allow for sediment
deposition. The forebays are separated from the main basin by a 6 to 8 foot berm which is
rimmed by a 3'x3' gabion structures or rip rap to provide long term stability, Water flows to the
low flow channel from the forebays over a reinforced 6-foot wide weir. Gravel access roads with
a maximum slope of 15% provide direct maintenance access. The access road is edged by a
gabion retaining structure to prevent the gravel surface on the inside slope ofthe forebay from
eroding.
Pem1anent Pool and Channels: The permanent pool and channels promote a variety of oxidation
zones shown to enhance pollutant removal. The pool will have a minimum surface area of
approximately 11,000 square feet. Water enters the permanent pool from the low-flow channel
and flows over a series of low weirs. The weirs will provide continuous movement and aeration
Water Quality Control Basin- Stage 2 Planned Development Project Description ·Page 4 of7
Dublin Ranch Area H Water Ouality Control Basin -Januarv 2005
of the pool, helping to prevent algal blooms and invasive emergents. The weir also serves as an
economical, low-maintenance, water feature adding visual interest to the basin. The forebays are
connected to the permanent pool by low flow channels. The low flow channels have a minimum
depth of 4 feet and a maximum of 8 feet. The bottom width of the channels varies between 4 to 8
feet; the top width of the channel varies between 16 and 30 feet. Side slopes will vary. The final
elevation and depth of the permanent pool will be adjusted based upon groundwater levels.
Pump Controlled Outlet Structure: Outflow from the basin will be controlled by a pump station,
which will include more than one pump to provide redundancy as necessary. The outfall
structure is set into a stabilized rip-rap slope 1.5V: 1 H on the southern edge of the permanent pool.
From the permanent pool, water flows by gravity through the outfall structure to the pump
station. Final design details will be updated as the design proceeds and will naturally be subject
to review and approval by the City of Dublin and the RWQCB.
Main Basin Area: A diversity of elevations is maintained in the main basin area to provide
filtration through vegetation as well as biochemical processes. The basin floor is graded to create
a series of islands four to eight feet above the minimum pool elevations so that the highest points
are inundated at the water quality elevation of 333.00. This will significantly increase the littoral
(edge) area, thereby increasing the filtration zone of the basin, A divider ridge, between forebay
1 and the permanent pool, prevents water from flowing directly from the forebay to the outfall
structure. The divider ridge and islands are planted with a mix of native trees to create groves
and reduce the visual scale of the basin area, so that it does not appear as a single large
depression.
Maintenance and Emergency Access
An existing gated entry at the existing frontage road cuI de sac provides access to the
maintenance and emergency access loop around to the basin area. This access point may be
moved to the NW corner of the site if the cuI de sac is removed in the future as a result of
widening 1-580. The maintenance access loop around the top of the basin is 15 feet wide and
will also serve pedestrian circulation. The existing G3 maintenance access road on the south
edge of the basin will be retained and resurfaced with stabilized crushed stone paving as part of
the loop. The basin floor is accessible from the maintenance roads at three gated locations.
Knox box hardware will be installed at all maintenance access gates for emergency access.
A 15- foot wide path provides access to two sides of the penn anent pool to provide access for
maintenance and vector controL A turn around area is provided for maintenance vehicles at the
end of the pool maintenance road. In addition, maintenance access ramps with a maximum slope
of 15% are provided for maintenance access to the pennanent pool and forebays. All road/path
will have a standard 2% cross slope for drainage. All access roads and pedestrian paths will be
designed to carry light truck access for maintenance and emergency purposes. In addition,
emergency access to the site will be available from streets on the north, east, and west edges
of the basin when the adjacent development is complete and people are using the area. Class
2 base rock will be used for the access roads and paths. The maintenance access roads will
not accommodate H-20 loading.
Pedestrian Paths
Pedestrian access will be provided at the NW and NE comers of the site and integrated with
future development of adjacent areas. The pedestrian paths will be paved with an ADA-
compliant, stabilized crushed stone surface amenable to walking and jogging. The crushed stone
Water Quality Control Basin - Stage 2 Planned Development Project Description -Page 5 of7
Dublin Ranch Area H Water Qualitv Control Basin -Januarv 2005
surface will be placed over the Class 2 aggregate base. The grades on the path vary from 0% to a
maximum of 5% to allow for pedestrian use. Several, smaller, 8' wide, stabilized crushed stone
pedestrian paths are also provided for general use and access to overlook seating areas.
Fencing
A 5-foot fence will limit access to the interior of the basin. The intent of the fence is to clearly
identify public open space areas and preclude access to the interior of the basin. Signage will be
posted to indicate that the basin is "offlimits." Access gates will be provided at each entry point
to the interior of the basin. The fence layout is varied in plan and elevation to create an effect
similar to stone fann walls or horse fences. The proposed fence layout moves gently up and
down the basin side slopes to meet the vehicle access gates where required and stay below sight
lines where possible. Because the fence changes elevation it is important to select a fence system
that can follow the slopes smoothly without abrupt level changes between panels. The fence
also needs to be non-climbable according to city requirements. Based on these considerations as
well as initial and long-term costs we are proposing a green vinyl coated chain link fence with I"
openings and a top wire to reduce climbing and visibility. The existing 6-foot chain link fence
will be maintained on the current Caltrans right of way.
The fence layout insures that inundation levels above the fence will not exceed 18 inches, The
maximum water surface for the 100-year storm event is elevation 344; therefore the lowest fence
elevation is 342.50. The top edge of the basin ranges in elevation from 347,00 to 351.00. The
fence is set 5' below path grades where possible to minimize visual impact of the fence from
adjacent areas and pathways.
Lighting
The Water Quality Basin is most similar to natural park areas, greenways, and stream corridors.
Good precedents include the stream corridors managed by homeowner's associations at Dublin
Ranch and the golf paths managed by the golf club. These areas are accessible but are not
illuminated because they are not intended for nighttime use. The basin will be located in an
isolated field with no direct public access until adjacent areas are developed. The basin has been
designed to allow limited public access around the upper perimeter. However, this access should
be deterred until adjacent development is completed and adjacent property owners, the police
department, and the public can monitor the area. Lighting the basin area prior to completion of
adjacent development will draw unnecessary attention to the basin and could draw unwanted
visitors,
We propose adding lighting along the north edge of the basin as part of future streetscape
improvements associated with Area H. Final selection of fixtures and layout will be developed
as part of the planning review process for that area. Refer to the Phasing description and
streetscape improvement concept plans. The basin is not a residential area and therefore the I fc
level required by the residential security code should not apply. The proposed lighting would
meet IESNA standard of 0.5 fc for pedestrian park paths. This lighting would supplement
required street lighting and create a pedestrian scale along the edge of the basin. In order to deter
night use of the east, west and south edges these areas would not be illuminated.
Water Quality Control Basin - Stage 2 Planned Development Project Description ·Page 6 of 7
Dublin Ranch Area H Water Qualitv Control Basin -Januarv 2005
Power Source
Final power service connections will depend on construction sequence. Two options are
being considered. The fITst option is a connection to existing power service on the Caltrans 1-
580 frontage, the second option is to provide service from Dublin Boulevard. The optimum
connection will depend on further coordination with PG&E and sequencing of Area H
construction.
Public Art Component
The applicant will develop a public art component for the project. Artist selection, type, and
funding will be further coordinated with the Dublin Fine Arts Foundation.
Landscape and Planting Design
In keeping with the SMWP, the design will include a variety of native emergent species,
grasses/forbs, woody shrubs, and trees, as well as selected non-native species in distinct areas at
the top of the basin.
The following section provides the rationale behind the plant associations and plant species
palettes for the Water Quality Treatment Basin planting zones. The planting design aims to
maximize water treatment functions and aesthetics while maximizing natural wetland, riparian,
woodland and grassland habitats.
The overall objectives of the planting design are:
· to facilitate contaminant filtration of local runoff water
· to provide aesthetic value and outdoor open space for adjacent business, office, and
residential centers
· to minimize maintenance requirements to sustain the vegetation
· to promote vector control
· to provide wildlife habitat
These objectives will be achieved through the establishment of a self-sustaining riparian habitat
along the low-flow channel on the basin floor and managed upland plant communities around the
area's perimeter. Top of slope areas will be planted with more formal and uniform planting's
compatible with future development streetscapes and open space areas in Area H. This will
create a cohesive park like environment around the more natural areas that fall within the basin.
The side slopes of the basin will be planted with a mixture of native meadow grasses, shrubs and
trees, to create an environment similar to the regional hills. The lower parts of the basin will be
planted with a variety of native plant communities and will evolve into a naturalistic environment
similar to a stream corridor. The level and type of maintenance will be managed by zone
accordingly to achieve a combination of picturesque and naturalistic areas.
Nine planting zones are proposed based on elevation, hydrology, and aesthetic considerations.
PI: Perennial Emergent Wetland, low flow channel and pool edge
P2: Willow Riparian, low flow channel
P3: Seasonal Wetland, upper channel slopes and pool edges
(elevation 320 ~ 324)
(elevation 320 - 328)
(elevation 324 - 348)
Water Quality Control Basin - Stage 2 Planned Development Project Description ·Page 7 of 7
Dublin Ranch Area H Water Oualitv Control Basin -Januarv 2005
P4: Faucultive Wetland, Basin Floor
P5: Mixed Riparian, Basin Islands
P6: Slope and Upland Grassland, Basin Slopes
P7: Oak Woodland, Selected areas of basin slope
P8: Valley Oak Savanna - managed grassland, Top of Basin
P9: Upland Slope, side slopes of park landforms
(elevation 338 - 330)
(elevation 330 - 334)
(elevation 330 - 347)
(elevation 330 - 347)
(elevation 345 - 352)
(elevation 345 - 352)
Refer to appendix A for a detailed description of each planting zone.
Irrigation System
A permanent automatic irrigation system will be installed in areas above the typical storm water
detention surface elevation of 333.00. In addition, temporary irrigation will provided as needed
to establish plant material in areas below elevation 333.00. Refer to the irrigation system notes
and the Irrigation exhibit L 3.30 in this submittal for system zones and parameters.
Ownership and Maintenance
A property owners' association(s) comprised of owners of the Area H General Commercial and
Campus Office parcels will be created for the Project Area and surrounding areas, and a
Declaration of Covenants, Conditions, and Restrictions (Declaration) will be prepared and
recorded. The Declaration will establish easements and other rights necessary for the
association(s) to fulfill their responsibilities. The Declaration will require the association( s) to
own and/or maintain the lands in accordance with the maintenance and operations plan
required by the Regional Water Quality Control Board order, and the Storm Water
Management Plan. The maintenance will be the responsibility ofthe current landowner prior
to the creation of the POA. For a detailed outline of monitoring and maintenance activities
refer to the attached maintenance summary documents,
Vector Control- Mosquito Abatement
Storm water detention facilities can become mosquito sources if they are not properly designed
and maintained. The basin has been designed to prevent mosquito source development and allow
for both maintenance and abatement procedures. In addition the design team has consulted with
the Alameda County Mosquito Abatement District to discuss the design and address these
concerns. The abatement district addresses vector control issues through source reduction, source
prevention, larvaciding, mosquito fish, and monitoring.
Mosquito breeding requires still, standing water for more than a few days. Balance Hydrologies
Inc. has measured low flows for storm drain pipes flowing to the basin and has estimated that the
basin will have a significant low flow through out the year. This low flow is the result of
groundwater seepage into the storm drain system as well as irrigation runoff. The low flows will
provide a continuous stream of moving water through the permanent pool and pump system. The
slope of the low flow channels has been maximized to increase flow velocity and minimize the
risk of standing water. The pem1anent pool will also support mosquito fish habitat and a food
chain to prevent mosquito breeding. To avoid mosquito breeding associated with detention of
water for treatment purposes the basin will be drawn down over a maximum of 72 hours.
Water Quality Control Basin - Stage 2 Planned Development Project Description .Page 8 of 7
Dublin Ranch Area H Water Ouality Control Basin -Januarv 2005
In addition the maintenance access roads provide access to all areas of the basin floor to provide
for ongoing vegetation maintenance to reduce breeding habitat and allow for larvaciding if
required.
The Design team met with John Rusmisel of the Alameda County Mosquito Abatement District
on 5/1 9/2005 to review the basin plan. See the attached letter outlining his review and approval
of the plan.
Project Phasing
Implementation of the Water Quality Basin will occur in three phases of construction. The
phasing plan has been developed to address overall grading operations, regulatory requirements,
technical issues, and adjacent development. The first phase is scheduled for completion in
summer - fall of 2005.
Phase 1 Rough Grading and Infrastructure: The first phase of Basin construction will include
rough grading and installation of primary storm drainage infrastructure. The basin side slopes
and access roads will be graded to contour. The bottom of the basin will be graded flat with even
cross slopes to drain. The site will be hydro seeded with an erosion control seed mix.
Construction documents for phase I basin construction will be submitted to the City as part of the
Grading Permit application. Outfall pipes will be capped at the diversions structures and the
Basin will not be operational at this stage.
Phase 2 Finish Grading, Site Improvements and Landscaping: The second phase of
construction will include remaining basin drainage infrastructure; site improvements including
the basin overlook walls, fencing, site furniture, access roads and paths; as well as, finish grading,
soil preparation, irrigation and planting. The sediment forebays, low flow channels, gabion
structures, and permanent pool will also be completed in this phase. With completion of this
phase the basin will be connected to the storm drain system. The connection of the basin will be
coordinated with upstream earthwork operations to avoid heavy sedimentation of the basin and to
meet R WQCB permit requirements.
Phase 3 North Edge Streets cape Improvements: The third phase of construction will be
competed in accordance with future Area H improvements and will include construction of the
landscaped pedestrian promenade, overlook grove, additional site furniture, comer plazas, and
pedestrian path lighting. The proposed design will be refined in sequence with Area H
development plans and submitted to the City for review as part of the planning review process. A
streetscape improvement easement has been included on the parcel map to accommodate
construction of future improvements, Refer to sheet L 1.20 in this submittal for the concept plan.
Water Quality Control Basin - Stage 2 Planned Development Project Description ·Page 9 of 7
Dublin Ranch Area H Water Oualitv Control Basin -Januarv 2005
FINDINGS STATEMENT
for
DUBLIN RANCH - REGIONAL WATER QUALITY CONTROL BASIN
Stage 2 Development Plan/Site Design Review
The following findings relate directly to the specific questions listed under the written statement
section of the City's application submittal requirements for a Stage 2 Development Plan.
A. Describe how the proposal will be harmonious and compatible with existing and future
development in the surrounding area?
The WQCB has been designed to create a park-like environment similar to the larger
open space preserves in the Dublin Ranch area. Each edge of the basin has been
designed to address current and future development in the surrounding area. To the
south, 1-580 frontage has been designed to screen the basin from view and provide
passing vehicles with an attractive but subtle frontage landscape, which are intended to
create a foreground for distant views to surrounding hillsides. The north edge of the
basin has been configured to create a pedestrian promenade fronting future development.
The east and west edges are partially screened by low landforms and oak plantings to
create a park environment and to screen potential parking areas on either side. The
sculpted side slopes within the basin create a graceful transition from the upper area to
the more natural area in the bottom of the basin.
B. Is the site physically suitable for the type and intensity of the zoning district being
proposed?
The hydrologic requirements and existing storm water infrastructure dictate the location
and size of the proposed WQCB. The existing topography, soils and adjacent uses are
physically suitable for the proposed zoning district. Geotechnical investigations of the
Project Area and surrounding areas have been conducted by BerIogar Geotechnical
consultants to determine the soil condition and stability; the studies indicated no areas of
concern within the project area. The recommendations and conclusions of the study are
referenced in the Geotechnical Report: Dublin Ranch - Pao - Y eh Lin Property dated
August 30, 1999.
C. Will the proposal adversely affect the health or safety of persons residing or working in
the vicinity, or be detrimental to the public health, safety and welfare?
The proposal will not adversely affect the health, safety, or welfare of persons residing or
working in the vicinity. Measures have been incorporated in the proposal to address
public safety issues associated with visibility, access, nuisance behavior, and mosquito
abatement and vector control concerns. The public access area will be clearly delimited
and signed to deter nuisance activity in the basin and ensure public safety. Mosquito
abatement and vector control issues have been addressed in the proposal and coordinated
with appropriate agencies.
The proposed project is consistent with the Eastern Dublin Specific Plan and any related
municipal ordinances addressing public health, safety and welfare. Additionally, no
noxious odors, hazardous materials or excessive noises will be produced by the project.
Water Quality Control Basin ~ Stage 2 Planned Development Findings Statement .Page I of2
Dublin Ranch Area H Water Oualitv Control Ba.çin -Januarv 2005
With respect to areas subject to flooding, FEMA has issued a Letter of Map Revision
(Number 0607050002B dated August 27,2004), which indicates that no developable
areas of the project site are within a 100-year flood hazard area.
D. Is the proposal consistent with all elements of the General Plan and any applicable
Specific Plans of the City of Dublin?
The proposed regional water quality basin is consistent with the policies of the
Dublin General Plan and Eastern Dublin Specific Plan with respect to water
quality treatment practices as well as location of public infrastructure elements.
In particular, it is consistent with Specific Plan Policy 9-9, which requires that
the project "plan facilities and select management practices in the Eastern Dublin
Specific Plan area that protect and enhance water quality". The proposed facility
is intended to provide treatment for surface water runoff for a significant portion
of Dublin Ranch.
In addition, the proposed facility is consistent with Specific Plan policies pertaining to
open space by providing a significant open space area that has both visual and physical
access. More specifically, the project complies with Specific Plan Policy 6-3 by
providing "convenient access from developed areas to designated open space area and
trails"; Policy 6-4 by preserving "views of designated open space areas" and Policy 6-5
by ensuring "adequate access to open space areas for maintenance and management
purposes."
E. How does this project satisfY the purpose and intent of Chapter 8.32 "Planned
Development" of the Municipal Code?
The project is required by the California Regional Water Quality Control Board
(RWQCB), according to the terms of Transmittal of Order No. R2-2003-0032, Water
Quality Certification and Waste Discharge Requirements, Dublin Ranch Project, dated
April 22, 2003. This requirement is consistent with the provisions described in the East
Dublin General and Specific Plans. The project provides for effective development of
facilities and services serving the entire Dublin Ranch project area. The project includes
creative and imaginative design, which promotes amenities beyond those expected in
conventional developments and utilizes design features to achieve development that is
compatible with the surrounding area,
F. How does this project satisfY the purpose and intent of Chapter 8.104 ((Site
Development Review" of the Municipal Code?
The project satisfies the purpose and intent of the Site Development Review by
creating an orderly, attractive and harmonious site development compatible with
the facility program and individual environmental constraints. The landscape
design and theme, pedestrian and maintenance access, and visual impacts have
been effectively addressed. As a regional, water quality facility the project
promotes the general welfare.
Water Quality Control Basin - Stage 2 Planned Development Findings Statement ·Page 2 of2
Dublin Ranch Area H Water Oualitv Control Basin -January 2005
PROJECT DESCRIPTION
for
DUBLIN RANCH - REGIONAL WATER QUALITY CONTROL BASIN
Site Design Review
The following findings relate directly to the specific questions listed under the written statement
section of the City's application submittal requirements for Site Development Review (SDR). For
more information on the area covered here, see SDR drawing reductions in this section.
A. What type of business, activity or use are you proposing?
The Development Plan covered by this Stage 2 PD proposes 2.34 acres of open space for
public access, 7.16 acres of open space for storm water treatment, and 1.18 acres of open
space associated with the 1-580 frontage. The project will include storm water
infrastructure associated with the water quality function including an underground pump
station.
B. How many employees will you have or propose to have?
Not applicable.
C. What are the proposed hours and days of operation?
Public access will be allowed by the P.O.A from dawn to dusk. Commercial-type uses will
not be permitted within the project area.
D. Are there any ways in which your business, activity or use have a negative effect on the
health or safety of persons residing or working in the vicinity, or be detrimental to the
public health, safety or general welfare?
The planned activities and uses will not have a negative effect on the health or safety of
persons residing or working in the vicinity, nor are they detrimental to the public health,
safety or general welfare.
E. Describe how the design of the project including site layout, structures, vehicular access,
circulation and parking, etc. will provide a desirable environment for the future
development?
The WQCB has been designed to create a park-like environment similar to the larger open
space preserves in the Dublin Ranch area. Each edge of the basin has been designed to
address current and future development in the surrounding area. To the south, the 1-580
frontage has been designed to screen the basin from view and provide passing vehicles with
an attractive but subtle frontage landscape, which is intended to create a foreground for
distant views to surrounding hil1sides. The north edge of the basin has been configured to
create a pedestrian promenade fronting future development. The east and west edges have
been partially screened by low landforms and oak plantings to create a park environment
Water Quality Control Basin - Site Development Review, Project Description· Page I of 3
Dublin Ranch Area H Water QuaUtv Control Basin -January 2005
and screen potential parking areas to either side. The sculpted side slopes create a graceful
transition from the upper area to the more natural area in the bottom of the basin.
F. Is the site physically suitable for the type and intensity of development proposed?
The hydrologic requirements and existing storm water infrastructure dictate the location
and size of the proposed WQCB. The existing topography, soils and adjacent uses are
physically suitable for the proposed zoning district.
G. Describe how the proposed development may impact views?
The Project Area does not contain any of the City's designated visually sensitive ridge
lands as outlined in the Eastern Dublin Specific Plan. Therefore, development will not be
visually obtrusive to those views of the Tassajara Hills. The Project Area is situated in the
flat low lying area along 1-580 and is designed to create a landscaped foreground with view
corridors to the Tassajara Hills beyond. Views from adjacent edges and 1-580 have been
addressed with gentle landforms and tree plantings unique to each edge of the basin. Views
into the basin are designed in a controlled manner to create a picturesque effect.
H. Describe the physical characteristics of the site including existing slopes and topographic
features and any proposed changes to these features?
The Project Area is currently vacant land. The existing topography across the site is very
flat, sloping from south to north at approximately 0.5%. Elevations range between 343.00
and 340.00, with exception to a low landform at elevation 347.00 created above the
recently completed G3 box culvert on the southern edge of the site. The adjacent grades in
the development area will be raised to elevation 347.00 as part of the basin grading
operations. 1-580 forms the southern edge of the area. The WQCB will be excavated to
create sculpted landforms from approximately elevation 347.00 to a low point of elevation
318.5. The final elevation and depth of the permanent pool will be adjusted based upon
groundwater levels, Low landforms will also be created above the G3 box culvert from
elevation 347.00 - 352.00.
L Describe the architectural design/theme of the development including character, scale
and quality of the design, and explain how the project will relate to and be compatible
with the existing site and the character of adjacent buildings, neighborhoods and uses?
Not applicable.
1. Describe how the landscape features have been designed so as to insure visual relief and
an attractive environment for the public?
The beauty of the existing rolling topography and natural countryside is the basis for the
Dublin Ranch landscape concept and planting theme. The primary goal of the WQCB
design concept is to integrate the basin into the surrounding area as an open space amenity.
The design concept is to create a park like environment based upon the picturesque
qualities of the regional California landscape, combined with ecological and naturalistic
aesthetics. The water quality functions and infrastructure are integrated into a picturesque
Water Quality Control Basin - Site Development Review, Project Description -Page 2 of 3
Dublin Ranch Area H Water Oualitv Control Basin - Januarv 2005
landscape with rolling, sculptural landforms and distinct groupings of trees, which create a
sense of depth and enable distinct views. Site improvements will have a contemporary but
rustic quality. The design concept anticipates public access associated with future Area H
uses, by including walking paths, overlooks and seating areas in the design. The overlook
areas are framed by rustic, dry laid boulder walls, which create a sense of place and contrast
with the rolling topography. The north edge of the basin has been developed as a
pedestrian promenade with a more urban park character compatible with future adjacent
streetscape and uses. The' Art fence' proposed for this edge of the project will add a layer
of visual interest. The remainder of the fencing will be an open mesh fence system to create
a continuous and transparent ribbon, moving through oak woodland groves along the basin
slopes. The basin is largely screened by low landforms and tree planting on the east, west
and south edge; while a frontage landscape has been developed along the 1-580 corridor.
The frontage landscape provides visual relief and continues the picturesque theme with low
sweeping landforms and rows of trees.
By treating the basin as a designed landscape, and considering its location, layout, and
visual qualities, the proposed design successfully integrates water quality function, public
open space, and ecological value.
Water Quality Control Basin - Site Development Review, Project Description -Page 3 of 3
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PRO.JECT TEAM
CHANG SU-O UN, HONG YAO UN & HONG LIEN UN
JAMES TOHG, AUTHORIZED REPRESENTlTIVE
7707 KOLL CENTER PAAI<mAY
SUITE 120 PLEASANTON, CA 9.54566
(925) 485-1060
BAlANCE HYDORLOGtCS INC.
841 Folger Avenue
Berkeley, CA 94710
(510) 704-1000
CONTACT: ED BAl.LMAN
ECOLOGICAL CONSULTANTS: H.T, HARVEY & ASSOCIATES
3150 AlMADEN EXPRESSWAY, SUITE
SAN JOSE,CA 95118
(408) "'ð-9<50
CONTACT: MAX BUSNARDQ
45
CMG LANDSCAPE ARCHITECTURE
589 HOWARD STREET, SUITE 5
SAN FRANCISCO, CA 94105
(415) 495-3070
CONTACT: CHRIS GUllLARD
MACKAY & SOMPS
5142 FRANKLIN DRIVE, SUITE B
PLEASANTON, CA, 94588
(925) 225-0090
CONTACT: DAVE CHADBOURNE
LANDSCAPE ARCHITECT:
OWNER/APPLICANT
CIVIL ENGINEER!
lAND PLANNER:
HYDROLOGY:
SHEET INDEX
COVER SHEET
ILLUSTRATIVE PLAN
SITE PLAN
STREETSCAPE CONCEPT PLAN
GRADING AND DRAINAGE PLAN
PLANTING SCHEDULES
GROUND PLANTING PLAN
TREE PLANTING PLAN
IRRIGATION PLAN
SITE SECTIONS
PERSPECTIVE RENDERINGS
SITE DETAILS
SITE SPECS AND PRECEDENTS
STREETSCAPE DETAILS
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L 2,00
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Holdings L.L.C.
4690 Chabot Drive, Suite 1 (
Pleasanton, CA 94558
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STAGE 2 PD/SDR
Jo"No: DUB 0401.1
0.,.; 0512005
ShHrT1t1e:
SITE PLAN
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Holdings L.L.C.
4690 Chabot Drive, Suite 1(
Ple858nlon. CA 94558
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STAGE 2 PD/SDR
GRADING NOTES
EXlSTIN6 ~ INDICATED ON fJ..!jS F\.AN HAVE BEEN Ha)IFIED fJ'( 63 GLL'ÆRT
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GRADING PLAN
Job No
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Stamp:
Consultant:
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Dublin Ranch
Holdings L.L.C.
4690 Chabot Drive. Suite 1(
Pleasanton. CA 94558
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2 STAGE '2 PDlSDR: 0112005
No: Revision Date:
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DeSCription:
STAGE 2 PD/SDR
Job No: DUB 0401.1
Oar.: 0112005
Sheet Tltl.:
PLANTING
SCHEDULE
- -
Sh.., No:
L 3.00
PLANTING SCHEDULES
SEED MIXES
Two seed mixes tut: described The fucultall\'c wetlund seed mix can be used in PI though P4. The upland seed mix ç!1J1 be used in P4 through P9 Each ot these seed mixes can be u!>Cd at 'I, the lIPplicatíon rate in P4 We
recommend that seed be installed \'Ùt hydrosccding or drill seeding We will need to assess the relative feasibility :md cost of these two optj,
T
ContainerS~s~
lrecband
treeband
treeband ~
treeband
trceband ----==-.==-
SPECIES PALETTES
ent Wetla_~
Scientific Name
AflemQtJsis ca/i(017lica
Epi/obium dUatlun _
ScifJ'us aClltus '"
___,---.!'i£~rpuscali(a17/icll~ ~
Scirpus robllsflls
- "'~ with Seed Mix Species A: Facultative Wetland Mix
===l
I
- I
------=:J
witb location ) ~-Tvpe
¡ native tree
Contllin~rle
Trecpot - 24" Box
Treepot'-IS ital
Trec:pot - 24" Box
~.-36"Bm:
Treepol - 24" Box
Trec:pot - 36" Box
[rcepo! - 24" Box
T reepot - 36" Box
.-----,
T
Container Size (vuies witb location
S=!
S=!
S=!
S=!
S=!
se;¡---
S=!
~--
S<ed
S=!
se;¡--.~
B: Slope and Uplund Mix
,-cali/liS
......Also
P4 - Fauculative Wetland & Slo
Common Name
, annual hainuass
IMolate~fescue
meadow barley
creepina wild rye .__
wwecup clarkia _._
, slenderwheatwass _
: California poppv_ _
PurshinR's lotus
arrovolupine _
, coast rMae melic
three week fescue
"'dominant plant sped, ~
Emer
Perennial
herb
tw.ia! wetJand forb
miaJ wetland forb
!fìial wetland forb
,
nnial wetíand forb
Mial wetland forb
nnial wetland forb
Mia! wetland forb
nnial wetland forb
;mial wetland ~
e:mial wetland ¡¡;rass
ial wetland forb
'-
nallvc
Seed Mix Species A:
Common Name
I annual hairwass
Malate red fescue
; meadow barlev --
I creepinR wild rye
"'dominant species.
Seed Mix Species B: Slope and UJI!1
Common Name
winecup clarida --
slender wheatwass
California POppy
Purshin¡r's lotus
arroyo lupine
caut ranll:e mehc
three week fescue
"'dominW1t species
TREE SPECIES PALLET
Tree Schedule
Common Name --
Tl - Fremont cottonwood
T2 - Box Eldcr -
T3 - California Sycamore '--
'-
H - Valley Oak --
T!'i - California buckeye
T6 - Cout live oak
1'7 - Little-Leaf Linden
T8 - Chinese Hackbem:
PLANT
PI
Co,
mba mansa
fr'Ìnll:cdwillo\\
common rule
-
crennial shrub
~
!Ii!<
nau,:!
native
SclenlincName. ContuInerSize (~Iocatlon)
~ígala'" - .._---====- tree:pot
I SalixlasiQ/epis'" 'treepot __
with Seed Mix Species A: Facultative Wetland Mix.
with location
i Container Size (\-·ane
, trecband
~
I trecband
I treeband
I treeband
: trceband
I=~:~
Scientific Namf
__.Ele(Jch(Jri.rmacrostac/~
Jtl/lCIIS ba/ticu.r '"
JlmcuseffuslIS
~ :Jlmclism~_
JllnCIIS xipl1iaides
Levmlis lriticoides.
Muhlenbel'"J!ia riR/!/1.';
R/lm/!:~ salici(olius
seeded wilh S~ Mix Species A: Facultative Wctland Mix
~rian
"Also seeded
Wetland
Ri
spec!
alkali bulrush
"'dominant plant sped
P2 - Willow
Common Name
~-
arroyo willow
·döminant plant
--
Typ<
~d annU;¡~ wass
--- -- i wetlandperennill.lwass
- --_ ! wetland perennial wass
- wetland perennial wa.<IS
--
~
I upland annual forb
, upland perennial ¡;¡rass
i upland perennial forb
I upland annual JeRUme
upland annual ICRUme
i upland perennial lD'ass
, up!and annual II:ra~s
",",b
T
nali
~
~
depot ~ 36" Box
treeband - 24" 80x_
~--
. deepot
Wetland Mix & Seed Mix Spec¡
arian
Arttf'mi$io dOIlI(/asia'lo
___!l.!!EE_haris dOllillosi;
Rosa cali(017lÌca
RubuslIrsim
i Sambucus m,
_~a
d Mix SpecIes B. Slope and Upland Mix
Mixed Ri
mu¡r.vort
marsh bacchans
P5
~
T'
~~
uplnnd perennial ¡;¡rass_
upland perennial forb
!!f!!.lÐd annuallcllWTle
upland annual lep;um.e
upland perennial wass
upland annual wass
with locatloQ
,·ar:!,
~ize
Contain
Seed
S=!
S=!
S=!
S=!
S=!
S=!
Scientific Name
C/arkiaPtl~_
E¡'".ml/S fradrvcaullls ssp, traÔrvcm,lrls
Esducholzia ca/i/o""ka
LOflls purshianlls
Llfpim/$SI/cCI//enIIlS
JIe/ica imper(ecfa ~
VII/pia mlcrosfaclrvs '"
common snowbem'
...... Also seeded with
P6 ' Slope l Upland Grass
CommOn Name
winecup darkia
slender wheallUass
California POPPy
Purshin¡¡;'S lotus
arroyo lupine
I coast ranl!e mdic
three wcck fescue
"'dominant plant spccíCI
Oak Woodland
P7
erenmalshrub
ial shrub
!.
nati
~
,
,
De
8acchans dOtlldasl/
Rhamnus cali(of7lica
and Upland Mix
WIth Seed Mix SpeclCS B: Slop'
.. Also seeded
1:;
native tree
~
upland
",,·¡tb locatioQ
':!"'
Container Size
treepot
treeband
treebMd-
P8 - VaUey Oak SavaDnal Native Grasslsnd
Common Name Scientific Name
Sambucus mexica'la
Feshlca robra
LeV/nus trilicoide.
Slope and Upland Mix
~
u.
ial
nn¡;¡-
~fescue
~iJdrve
··Also seeded \\1m Seed Mix Species 8
itaOfiginlllgiZII_
ercnníal shrub
If \hill d~'1g is not 30"'142', (till" th._dr.wing hII" been ,eviMd from
NotllKl s~14ts must m. 8dJusttod Th." hne sh~1d b. .quel to one inch
!!J
nati
Container Size
dccpol
~;~í=~~o~~.~~~~~t::n:ps:~~.':t~~~~·JI~~t~~~~~'1 =~~:~,'1r~ItC~M~¡"""
Oak Savanna/ Shrub
Scientific Name
I BacchariJ dOl/Ida.
Seed Mix Species B: Slope and ~
P9, VaDe'
~
~
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CMG
CON6El1ll0SS (;UILLA'D
¡"ROIfAWO 5rUErJUf7£S
UK flAlle/SCIl" 14115
"ELUNDlfE: 4151415-J(110
-Ar;SllIfLlE: ffS/U5-JOU
Stamp:
Consult.nt:
Dublin Ranch
Holdings L.L.C.
4690 Chabot Drive, Suite 1(
P1easanton, CA 94558
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2 STA.GE 2 PDlSDA 12121104
No: Revision Date:
D.
D.
D.
D.
D.
D.
DucrlptJon:
STAGE 2 PD/SDR
Job No: DUB 0401.1
0...: 12/21/04
Sh..r Title:
GROUND
PLANTING PLAN
- -
Sheet No:
.~ in
SCHEDULE
P1 WITH SEED I.!IX
P2 WITH SEED MIX
PJ WITH SEED ~IX A
P4 WITH SEED MIX A &
P5 WITH SEED MIX
P6 WITH SEED ~IX
P7 WITH SEED MIx
PB
P9
ELEVATION
320-326
320-.328
322-328
328-330
330-334
330-.347
330-347
340 +
34D +
ELEV,
ELEV,
ELEV,
ELEV,
ELEY.
ELEV,
ELEV,
ELEV,
ELEV,
LOCATION
CHANNEL 80TTO~ I POOL EDGE
CHANNEL BOTTOM / SLOPES
CHANNEL / POOL SLOPES
BASIN FLoOR
BASIN MOUND / LOWER SLOPES
BASIN SLOPES
BASIN COVES
PERIMffiR
PERIMETER
PLANTING ZONES I ASSOCIATIONS
PERENNIAL EMERGENT WETlAND
WIU.OW RIPARIAN
SEASONAL WETLAND
FAUCULATIVE WETLAND &: UPLAND GRASSLAND
MIXED RIPARIAN
SLOPE &: UPLAND GRASS
OAK WOODLAND
VALlEY OAK SAVANNAH / NATNE
UPLAND SLOPE
GRASSLAND
KEY
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®
®
®
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0' 15' 30' 80'
-----
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------ FUTURE CALTRANSRow 'LlMITOFGRÃÕiÑG- ~'- - - \-) ---"-----,"'"",,, --''""',,-..Õ~~ -'-'--~---'-'-'--="---"_~_:: -S _ _ ,______
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EXISTING CAL
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- Ð:ISTiNG CALTRANS ROW, & L.O,W:---
- -
I -580 WEST
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FRONTAGE ROAD
ClA. DE SAC
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CONQU MOSS aU/lLANO
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lA, FlANCISCD r;A u/øJ
TlLlfllOlfE' .U/4U·,,'/1
FIUI.fLll: "'/fU'JØU
8åmp:
Con.ult.lnl:
r- Dublin R.nch
Holdings L.L.C.
4690 Chabot Drive, Suite 1C
Pleasanton, CA 94558
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2 STAGe2POiS~ 12121/G1
No: R.vl3/on D.t.:
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6
6
6
6
6
DøcrlpUon:
STAGE 2 PD/SDR
Job No: DUB 0401,1
o.m: 12/21/04
S,,"' Tltl.:
TREE PLANTING
PLAN
- -
Shør No:
L 3.20
TREE PLANTING ZONES (SEE SHEET L 3,00 FOR SCHEDULES)
~-'¡ OAK SAVANNA MIX OF T 4 VALLEY OAK & T6 COAST LIVE OAK
~ "
i~'~, OAK WOODLAND M IX OF T5 CALFORNlA BUCKEYE & T6 COAST LIVE OAK
,t..!¡'i ..~
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"X' RIPARIAN WOODLAND MIX OF T1 FREMONT COTTONWOOD, T2 BOX ELDER, T3 CALIFORNIA SYCAMORE, & T4 VALLEY OAK
'r)¡ ....
, :v, ,
PROMENADE T7 LITTLE LEAF LINDEN
INSTALL!:DWITH FUTURE STREETSCAPE IMPROV£MENTS
OVERLOOK GROVE T8 CHINESE HACKBERRY
INSTALLE:D WITH ~UTUAE STFlEETSCAPE IMFROVEMENTS
FRONTAGE TREE TS, CA::~~~~:R~o~~~;:E \ __~~.!:~§~~~~:~~-!,e-"::~:~~~~~~____
FUTURE PROMENADE TREE ---, _--ì'----- / ________
\ ---...--- '\ / --------
--------1- / -------!.!!.~~RE PARCEL UN. ¡ L
--- \ -_ ,Q,W,
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OM SAVANNA
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- "-- EXISTING (;ALI KAN¡,j K,U,,y, ~ Lu,vv, \- --
N
,580 WEST ~EB
r--I-.I
SCAlE: 1",.30'-0" . ,. '"
AU draw11"o1U 11M ""1111" materlallCOOll11"Q IIo!'e!n CONlltullt OIiQlnaJ 1Ir'd u/'lpubllshed w()r1( 01 \t1s 11th), drawlnq I' nol 3Q"~T, In.n Ilia dtawlr'O:l nu !)oon fOVlsod 110"' Ilt Of~j'" .uD
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OAK WOOD~D -
OAK SAV~~
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FRONTAGE ROAO
I:UI.DeSAC
EXISTING CAL TRANS R.OW, & L,OW,
-580 WEST
ut.IT OF PIJoNTIHG
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CONSeR MDSS ¡U1LUßD
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8U ''''tIICD CJ UfO'
rfLE1RUI; 4IS/4U·J010
<leI/JIll/I: 411/41"3110
Stamp:
Con~ullllnt:
r Dublin Ranch
Holdings L.L.C.
4690 Chabot Drive, Suite i(
Pleasanlon. CA 94558
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No: R.,,sJon Dare:
6
6
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6
6
6
Dqcrlption:
STAGE 2 PD/SDR
Job No: DUB 0401.1
0.,.: 0512005
ShfttTltle:
ZONE PLAN
PLANTING PLAN
- -
ShøINo:
L 3.30
12- PCP-UP SPR9iKl.ER ~ A VAAET't' Of NOZZLE OO/fl:uAATIONS ~ REG'.RD 10 SPAA'1'
p~ RADIUS AND TAAJ£troRY. SPRAy /(IZZD.S 'Mu. fJÁVE co\¡pAlØ£ PftECPITA"I'IOtf PAm. AT
SPRitKl£R lDC.\lK)IS.... zoNE _ PRESSIA£ CI!EA1IS N01ZLE \IS11NG,
PR£SSIJRE-œL/PENSArot«: t«Jm.E AMPTERS OR PIÐSU~ ~ VÞLVfS SHALl BE INSTALLED.
TO BE IIiSPti.ED AT 5IRJB At{D GROliÐ COYER L.DCATKiIS IN ORDER ro PROVIDE Df!ECTID IRIOOATION
oon.m AT SHRUB OR GROOt«> CXM:R ROOT ZOI£ WJ..
SPRAY HEADS AT
SHRUB oS GROUND
COVER AREAS
SHRUB & G,C
DRIP BUBBLERS
TREE BUBBLERS
IRRIGATION NOTES
rHE WjDSC'JÆ lRRX:A,ootI smÐ, SHi.U.. lIE FUllY .wTr:ij~:rm ""Ð DESK;NED TO ~Pl'r WITH All
ÞPPlCABl.EcoœsN«l~ OfTHECnYOF~ I./Àrm. rrWti IlEA IIIATER £FF1C1ENT
S"r'STÐ.I ~T C:OtftIRi.ts TO mE STATE \L.ijþ,m WA~ coNsEJM.1ION POlJC'r.
T1iElRRIG,i.,noIiDESlGNSHALitf:;tl.Œ8IJTNcTBEUUlTEoTOniEFOIloWlNcI
'"",",TIC
IRRIGATION
CONTROtiER.$
GENERAL SYSTEM DESCRIPTION
PERMANOO ..imOMAnc SYSTEM 'NrrH FUlL COVERAGE. Cl1T Off AT PATHS, AND auB!URS AT
1RE5. tJEDlUI. WATER USE AAEA.
P£RIoIANENT AUTOIjATlC smEll wm< "'" ŒMRAGE, LOW WATER USE ARfA
TEMPORAKY smEll FOR ESTABUSIIENT NEEDS, SYSTE~ CO~PONoo; m BE RE\I<wED,
EL 347 AND ABOVE
IRRIGATION ZONES
BASIN EDGE AREAS TOP OF SLOPE AREAS,
UPPER BASIN SLOPE EL .335 - EL 351
SLOPE EL 32B - EL 335
SLOPE EL 328 l 333
IRRIGA~ TOrnE ROOT ZeNt: Of' EoICH SI-WlBEPRCMiED IJI'I.IULl1PlEoonn DRIP Ðirn£R THAT
~~~~~~~~:~~~s::1 G~
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IRRIGA1!Ct1CON'1RCx.lERSStW.l.B(HOlJS[I)~Asa:lRiYÐIf;t.OSI..Æ THE~SlW.LHAVE
I.Itl.m.E PROOR.AM REPE4TCYCUÞ$ F1.£XII..E~ CAPA8I.JT1ES"MTH THE REQUIRED tWUBER
Of S1'A~ 10 oPEPJ.1E AU. CONTRa. WiVES '/I'm1t1 A H ~ IRIOOATIOli nUt FJI..I.\¡E 1\t!1I.£ ~OT
EXCEEDt«i HYDRAl.l.K: OR El..EC1RICALCAPAanES orT1£lJESIGI.m ~1'KIH S"I'STElL
SCHEDUlE !!O f"IC 'lHREADED ~ RISER WI\l BE INstItim I~ cotWC11OH 'fImi T1ftÀDfD F11X81:
:S'D~:m~=~9E~~~_O~~~
1<1''''''''' m _ UHE """"'" FRaU LDII EU.VA~ ounm
6" POfI-tlP Sl'UK!R~A\lAA£lYOFNOZZl.£ cotfl(;ijRAT!ONS WTTM REGAADTO SPRAY
PATTERN. R'aus ..I.'Ð TPJ.£C1'ORY. SPRAY ~ZZElS WIU ~VE COUPÅt1BlE PRECFlTAmN RATES. AT
SPRtIKl£R I.OCÁ~ WHERE zol£ OPERATING m:ssuRE CRfATES I«IZZL! ~.
PR£SSUR£--coI.IPЬfG Irom.E ~ OR PRE5SUR£ REOtX:ItiG vN.'ÆS SWL.l æ 1~Ufi).
SPRAYSPRmKL,
RISERS
NO IRRlGA.TlON. THIS ARtA WIll BE FREQUEHl1.Y FLOODED AND CLOSE TO GROUti:JWAITR. PLANT
YAltRW. I~STAlLAllON WILl. BE TIMED WITH PLANTlNG SEASONS FUR W,T1VE PI..NfT ESTABUSH~ENT.
PERl.l\NENT AUTOIjATlC smEll \\'JTH fUll GOVERAGE, CUT OFF AT PATHS, ANa BUBBLERS AT
ìREES. tJEDIUM WATER USE MEA.
PERMANOO AUTDYAOC S'r'STS.I WITH BOX COVERAGE, LOW WATER USE AREA.
LOWER BASIN
FRONTAGE LANDSCAPE
ROW L...A.NDSCAPE
KEY
([)
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®
®
®
<D
METERING &
aACKFLOW
PREVENTION
OOCUMENTATION
SPRAv/£ADS
TURF AREAS
ctlUPI.m CONS1RUCTION DOCUWENTS 'MLL BE PREPARED FOR: AlL PI.JHTm NÐs. P~ WILL
tcwœ WATER USE CAlctlA110tiS Nf) I OR ~1ERHG S01EIXl.ES AS REQlII!ED BY 11iE em
00: SAVANNA.
OAK SAVANNA
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EXISTING CALTRANS Raw. & LO,W, -----------, - ----- _________________1
N
-580 WEST lEB
~
SCAlE,1·.3O'.()" . ",' '"
~~~~~~~~=::Ji:d..~~=e:::a~u,;~ Itlhll ~ng I' r.oI JO'x-4r, LMrIIhe drwwInghu bMn twIUd frunilS 0IIginaJ 15i:z.
NOU!d lei," 1I1USI!:If ad~. n.- line shoUd be equ-' Þ one InctI ---.:..
®:
--'-----
FUTURE CAL TRANS ROW, , LIMIT OF GRADING
<D
'-- EXISTING GAL TRANS ROW, & LOW,
I -580 WEST
EX1S11NG
FRONTAGERQ.ID
Cll. CE SAC
No; (ssue Dato.
f.IV.r.r..;~ "'t.. ,.... I....~-':I.J :,,~~
~"'J.(".:, ~r.::.;:If-;
Ooscr/ptlon:
STAGE 2 PD/SDR
ShO"! Tit/a:
SITE SECTIONS
- -
ShCC'fNo.
L 4.00
D,u(\'
Dublin Ranch
Holdings L.L.C.
@ :0
;>;')
CMG
COMGER MOSS tiUll.LAffD
,
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Job No:
OJ-Ie;
No:
6
6
6
6
6
6
FUTURE PARCElllNEJL.O.W.
rr"':~__t.....
FUTURE PARCH
,~~;:.~ '?;.~:.""!T.:'~~~:':"'¡ """"T;.::_~~:.~'~',.~;;::.~~ :~':'
SECTION
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PEDESTR!AN
~ATH
~
ART
FENCE
ART
FENCE
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MAIN'JENANCE
ACCESS ROAD
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MAINTENANCE
ACCESS ROAD
P6: SLOPE/uP'LAND GRASS
/ /
?::t;;;;P~1·.:::'..~~,~T-~~·~~\!.~::-;~~~::~;;r~=~:;'~~;~.~..~'r~ ..,....
FENCE
-/
h
MAINTENANCE
ACCESS ROAD
.,
/--/
--/
CHANNEL
;,
LOWER P'ERMANENT POOL
/
EL
'~-J4
PJ. OAK WOODLAND .3 .3
~ / / /
U:t RIPRAP SLOP
I ~l /-/
:RGENT WETLAND D' p,
-/ -r~/
FENCE
/ /
PEOESTRLAN PATH
f'OREBAY DIVIDER RIDGE
.
-
-
,
.'. "., '~ .'
.
I .
/ ~/
LOW·FLOW
CHANNEL
- --
WMER QUALITY BASIN
ACCESS ROAD
FI:NCE
I
I
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:;' - .-&~. CL¡
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,
/
/
DRAINAGE EASEMENT
FRONTAGE LANDSCAPE
CULVERT
E
ULT.
CAL TRAN S
R.O.W.
El'," EL
346.50 3-42.00
I I
(E) GJ CULVER
/ /
I· 510 DRAINAGE EASEMENT
weST BOUND FRONTAGE LANDSCAPE
SITE SECTION 2 . - -
SCAlE: 1" = 30'.0"
C:AL TRANS
R.O_W.
El
3.41.00
/~ '/
1-580
WEST BOUND
- - . -
SITE SECTION SCALE 1" = 30',0"
UL
I
CMG
ClJNGE!l ,V(JSS GU!aHO
H~ ~:rI't;.~~ H'IU 5~i'l ~
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Darer:
U1.·'co~
D.1fr.:
Dublin Ranch
Holdings L.L.C.
·1(¡~J C~a:Jcl D·I'It.> Sl.l:e ':)
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6
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-----~- - ....--
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".....~1 ", /:;:>.,- " >'.... / /' ';', >,' ". 0 ·1
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Dublin Ranch Area H Water Ouality Control Basin - Januarv 2005
APPENDIX A
DETAILED PLANTING DESIGN DESCRIPTION
for
DUBLIN RANCH - REGIONAL WATER QUALITY CONTROL BASIN
Site Design Review
PLANTING ZONE PI: Perennial Emergent Wetland Association
The PI planting zone includes the bottom and slope of the low-flow channel along the bottom of
the basin. The low-flow channel is expected to have perennial flow due to "nuisance"
summertime runoff from the development and due to groundwater that may be intercepted by the
channel. Therefore, the channel hydrology will support the establishment of wetland and obligate
riparian plant species known to improve the removal efficiency of nutrients (nitrogen and
phosphorus), heavy metals and petroleum hydrocarbons associated with storm water. In addition,
vegetation planted immediately adjacent to the channel will enhance the aquatic habitat value of
the channel by providing shade and detritus for the aquatic food chain. The channel will then be
valuable to wildlife species associated with local wetlands and riparian forests. The riparian
wetland vegetation will also reduce channel bank erosion, while improving channel water quality
(e.g. lower water temperatures, lower turbidity, higher dissolved oxygen levels). To accomplish
these goals a mosaic of riparian, perennial emergent and seasonal wetland associations will be
planted in designated areas based on exposure to light and shade tolerance.
The perennial emergent wetland plants will be interspersed with the riparian association plants,
along edges of the southern channel bends, in order not to be over shaded. Plant species in the
perennial emergent wetland association tolerate frequent flooding, provide habitat for riparian
bird species, and filter contaminants in the channel water.
PLANTING ZONE P2: Willow Riparian Association
A wooded riparian habitat will be established along edges of the low-flow channel at the bottom
of the basin, specifically along northern bends in the channel. Plant species in the riparian
association tolerate frequent flooding, provide shelter for riparian bird species and create aesthetic
structure within the basin as well as contributing to water quality improvement and erosion
control.
PLANTING ZONE P3: Seasonal Wetland Association
The seasonal wetland association will be located at a slightly higher elevation than the riparian
and perennial emergent wetland associations. Plant species in the seasonal wetland association
tolerate flooding and also survive when the water table elevation recedes. Plant species in the
seasonal wetland association provide habitat for riparian bird species and increase sediment
deposition and contaminant filtration as water in the channel rises and recedes.
IV ater Quality Control Basin - Appendix A - Page I of 3
Dublin Ranch Area H Water Ouality Control Basin -Januarv 2005
PLANTING ZONE P4: Faucultive Wetland
The P4 planting zone is located along the basin floor, at elevations above planting zones P3. This
zone includes higher elevation mounds that will be planted with the woody mixed riparian
association plants. Areas surrounding the raised mounds will consist of seasonal wetland
herbaceous and grass species that will be established from seed. A seed mixture of facultative
wetland and upland grass and forb species will be sown between the wooded mounds. The
wetland and upland herbaceous species will establish along the environmental gradients in the
basin floor. These species have been selected to control erosion in the area, enhance contaminant
and nutrient removal, and will provide seasonal aesthetics during blooming times as well as
wildlife habitat.
PLANTING ZONE P5: Mixed Riparian Association
The mosaic of wooded and herbaceous areas will create an aesthetic feature along the basin floor.
The mixed riparian association will be planted on the higher elevation mounds. These mounds
will be flooded during winter rainfall events, and will be dry as the water table recedes in the
summer. The species selected for this association tolerate flooding. In addition, the Fremont
cottonwood (Populus fremontii) has been selected for this association because it survives when
the water table has receded below ground surface elevation (during summer months). The tree
and shrub species within this association provide food and cover for wildlife species as well as
stabilizing soils along the basin floor.
PLANTING ZONE P6: Upland Grass Association
Planting zone P6 occurs on the basin slopes. This zone traverses the lower limits of the normal
flood zone to the upper slopes of the basin. Plant associations in zone P6 will integrate with
those in P7 to form a continuum of wooded and grassland areas, A seed mixture of upland
grasses and forbs will be planted between the Oak Woodland association, These species have
been selected to tolerate infrequent flooding as well as drought conditions between flood events.
These open areas will provide a scenic vista across the basin increasing the aesthetic value of the
area.
PLANTING ZONE P7: Oak Woodland Association
The Oak Woodland association in P7 consists primarily of Valley Oak (Quercus lobata)
intermixed with other native species. Valley Oak are adapted to flooding, and have been selected
as a dominant species on the lower slopes of the basin where winter flooding will regularly occur.
Other flood tolerant shrubs will add to the structure of the woodland. These native species
provide food and cover for wildlife species. A seed mixture of upland grasses and forbs similar
to the Oak Woodland seed mix will be planted on slope areas between the oak groves.
PLANTING ZONE P8: Valley Oak Savanna/Native Grassland Association
Planting zone P8 is a continuation of zone P7, the primary difference being that the plantings in
zone P4 will be on a wider spacing to create a savanna, rather than a wooded, landscape. The
Valley Oak of zone P3 will be partially replaced by the less flood tolerant Coast Live Oak (Q.
agrifolia) species in zone P7, The savanna consists of native oak trees planted in small groups, or
Water Quality Control Basin - Appendix A ,Page 20f3
Dublin Ranch Area H Water Ouality Control Basin -January 2005
individually, separated by open spaces of native grasses. The oak and associated shrub species
have been selected to optimize the aesthetic value by providing shade and architectural plant
forms to create an interesting landscape for the people who live and work in the area,
A seed mixture of native grasses has been selected to fill areas between the widely spaced tree
plantings. These grasses have been selected for their ability to compete with weedy species and
thereby mininúze maintenance requirements. Depending on the suite of grasses selected,
maintenance will include either irrigation or weed removal within the grassland areas. Additional
shrubs may be added to this association to provide seasonal interest.
PLANTING ZONE P9: Upland Groundcover
The P9 planting zone is associated with steep side slopes on landforms in the upper areas of the
project including the frontage landscape. These slopes will be planted with a continuous mass of
low growing evergreen groundcover to minimize maintenance requirements and create a visual
contrast with surrounding grasslands,
SOILS
The soils at the site will be vital to meeting the objectives of the water quality basin. The
infiltration of water into the soil is a primary mechanism of contaminant and nutrient filtration in
addition to sedimentation. This is influenced by both soil permeability and the percent of clay
and organic matter in the soils onto which contaminants and nutrients are absorbed. Suitable
topsoil is also critical to the success of establishing the proposed plant associations. On-site soils
have been assessed for suitability of water quality improvement and plant establishment. A soil
preparation plan will be prepared as part of the final construction documentation.
Water Quality Control Basin - Appendix A - Page 3 of3
Dublin Ranch Area H Water Oualitv Control Basin -January 2005
APPENDIX B
San Francisco Bay Regional Water Quality Control Board, Preliminary Approval of
revised design, Email Correspondance
for
DUBLIN RANCH - REGIONAL WATER QUALITY CONTROL BASIN
Marty,
Here is an email regarding the proposed Dublin Ranch Water Quality Pond. Thank you for your
patience on it. I understand the City of Dublin is looking for something written--even just
informal, such as this email--toseethatweconcurwiththeconceptualdesignofthepond.So.
this email is intended to provide our conceptual concurrence with the pond's conceptual design, as
presented in CMG Landscape Architecture's submittal of August 10, 2004, which includes a
written narrative ("Dublin Ranch, Regional Water Quality Control Basin, Schematic Design
Update" and set of 11 x 17 plan sheets.
If you would, please forward this to your consultants at HT Harvey and CMG.
Overall, we remain excited to see this proposal and are very hopeful that it will simultaneously
provide a benefit to water quality while also providing an aesthetic and open space benefit to the
surrounding land users, and perhaps even a visual benefit to those driving by on the adjacent
interstate,
Additionally, we have the following questions and comments on the submittal.
(2) Water Quality Treatment Volume
This section indicates that the current treatment volume in the pond's design, 22.42 ac-ft, will be
decreased to the design water quality volume of 19.5 ac-ft as design proceeds. To the extent
possible, please seek to accomplish this by reducing temporary ponding depths, rather than
shrinking the ponding surface area. This will help promote settling of pollutants and reduce
transport of non-settled pollutants to the outflow point.
(5) Inlet Design
This indicates that flows will divert into the basin until the treatment volume has been reached,
and that thereafter, flows will go down the G3 channel. I had recalled (probably incorrectly) that
at some point there was a proposal to also use this basin for flood flow storage. Can you reassure
me that the submittal's statement (which indicates the basin will not be used to detain flood flows
above the WQV) is correct?
(7) Sedimentation forebays
Thank you for the detail on the design of these forebays, Would it make sense to line the bottom
of the forebays to help maintenance? Ordinarily, we would seek to maximize the open earth
area, to assist with infiltration, help vegetation grow, and maximize pollutant removal. However,
some of the presentations we've seen on detention basins in wetter climates ( e.g., Seattle) where
there is year-round rain, have suggested that maintenance may be helped by a somewhat harder
bottom. In this case, since we have a dry summer, during which one would assume maintenance
would typically take place, that may not be such a significant issue. So, we would hope to see the
design remain as proposed, but were just curious whether this issue came up for you during the
design process,
Water Quality Control Basin - Appendix A . Page I of 3
Dublin Ranch Area H Water Oualitv Control Basin -Januarv 2005
(8) Permanent Pool and Channels
Thank you for the description of the proposed permanent pool design. Has the issue been looked
at as to whether this design will provide sufficient aeration of the pond? Is there pumping
proposed to circulate the water over the waterfall/weir?
p,9 (last page) states that H.T. Harvey is developing a soil plan and is taking a look at on-site
soils. Can you let us know if this work has been completed?
Finally, just fyi, I'll forward (via email or regular mail) some pictures of Jens Jensen's lagoon in
Columbus Park, on Chicago's West Side. While I certainly defer to your firm's design
capabilities, this recently restored lagoon design is an example of a native stone design (of course
in a different climate and area) that remains striking and frequently visited more than 100 years
after its original construction. Perhaps it might serve as a point of inspiration for certain aspects
of the design, if they are not already completed.
Regards,
-Keith H. Lichten, P.E.
Acting Section Leader
San Francisco Bay Regional Water Quality Control Board
1515 Clay Street, Suite 1400
Oakland, CA 94612
(510) 622-2380 direct
(510) 622-2460 fax
kl ich ten(cl)waterboards.ca. go v
Marty,
I should have noted in my earlier email that we are commenting on the submittal as a conceptual
submittal that we have received as a part of the basin design process. That is, we would still
expect to receive a finalized submittal, acceptable to the Executive Officer, prior to the beginning
of construction, as required in the Dublin Ranch Order and related submittals.
Regards,
-Keith H. Lichten, r.E.
Acting Section Leader
San Francisco Bay Regional Water Quality Control Board
1515 Clay Street, Suite 1400
Oakland, CA 94612
(510) 622-2380 direct
(510) 622-2460 fax
klichten@waterboards.ca.gov
»> Keith Lichten 12/22/04 03:40PM »>
Water Quality Control Basin - Appendix A - Page 2 of3
Dublin Ranch Area H Water Oualitv Control Basin -Januarv 2005
Response to Keith H. Lichten's comments (12/22/04)
(2) Water Quality Treatment Volume
The Storm water Management Plan and Schematic Design included a 4,1 acre surface area and
19.5 ac-ft of treatment volume, with temporary ponding depths of approximately 5 feet. The
revised design included a 5.6 acre surface area and 22.42 ac-ft of treatment volume with
temporary ponding depths of approximately 5 feet. The difference in volume is related to the
enlarged surface area. The only practical and efficient way of reducing the volume and fitting the
basin within the designated land area is to reduce the surface area to the 4.1 acre minimum
designated in the Storm water Management Plan and schematic plans.
(5) Inlet Design
Your understanding is in fact correct. The design of the diversion structures allows the required
treatment volume to enter the basin until the basin fills to the flowline of the main storm drain
lines. At that point, the majority of runoff flows directly into the G3 channel bypassing the basin.
For large and/or closely spaced storms, storm flows will continue to flow into the basin after the
water quality volume and elevation are reached, however most of the water will flow directly to the
G3 channel. Once the water quality volume has been reached, the depth of the basin will
continue to increase at a reduced rate to a maximum elevation of 344.00, associated with the
1 DO-year storm event.
(7) Sedimentation forebays
The Storm water Management Plan and Schematic Design included a 4,1 acre surface area and
19.5 ac-ft of treatment volume, with temporary ponding depths of approximately 5 feet. The
revised design included a 5.6 acre surface area and 22.42 ac-ft of treatment volume with
temporary ponding depths of approximately 5 feet. The difference in volume is related to the
enlarged surface area. The only practical and efficient way of reducing the volume and fit the
basin within the designated land area is to reduce the surface area to the 4,1 acre minimum
designated in the Storm water Management Plan and schematic plans.
(8) Permanent Pool and Channels
We anticpate a constant low flow through the system from fore bay to permanent pool. The low
flow volume and rate anticipated from irrigation runoff, and groundwater seepage into the storm
drain system is estimated to be adequate to provide constant movement and aeration over the
weirs in the permenant pool, this flow will be pumped out of the permanant pool through the
outfall, providing constant circulation.
The soils work has been completed and incorporated in the soils and planting design. The results
of the soils analysis and recommended soils treatment will be included along with detailed
planting plans and specifications in the package submitted to the RWQCB prior to construction,
Water Quality Control Basin - Appendix A - Page 3 of 3
APPENDIX C
June 14, 2005
Mike Porto, Planning Consultant
Planning Department
City of Dublin
100 Civic Plaza
Dublin, CA 94568
Subject: Dublin Ranch Water Quality Control Basin
Dear Mr. Porto:
I met with Ed Ballman of Balance Hydrologics, Inc. and Chris Guillard of CMG recently to
review plans for the Dublin Ranch Water Quality Control Basin. Overall, I was pleased with the
amount of planning that has gone into the project. There are a number of adaptive management
tools available to manipulate the water level in the lower permanent pool to prevent vegetation
growth that can develop into mosquito sources. Cattails can become a real problem in this type
of basin so the vegetation maintenance called for in the management plan should be followed.
Our District technicians will need access to the basin to inspect and treat any mosquitoes that
develop. There are several locked gates to the access roads; we will need keys to the lock or
permission to add our lock to the gate.
Since the two forebays and permanent pools may have water throughout the year, we will want
to plant mosquitofish, Gambusia afjinis, to provide long term biological control of mosquito
larvae. If the mosquitofish do well in the pools we would harvest fish on occasion to augment
our fish stock which we provide to residents throughout the County. The vector control section
(3.9) of the draft operations and maintenance manual states that the use of chemical control
methods should be avoided to the extent practical and consistent with public health and safety.
We would use two naturally occurring bacteriallarvacides, Bacillus thuringensis var. israelensis
and Bacillus sphaericus as well as Methoprene, an analog of an insect growth regulator as the
pesticides of choice for mosquito control on the basin site, It is important to have a number of
tools available as part of our integrated program to avoid future problems with pesticide
resistance.
The vegetated low flow channels from the forebays to the pennanent pools have the highest
potential for producing mosquito larvae, If the flows are too slow, water may form isolated
pockets that produce mosquitoes. This problem could be reduced during low flow periods by
mowing the vegetation to allow water to dry out quicker and providing our technicians with
better access. This is addressed in the adaptive management plan.
We would like to be supplied with the name and phone number of person (or agency) charged
with managing the basin so that we can alert them of potential problems and request action to
prevent mosquito emergence. If the Basin should become a continuing source of mosquitoes that
requires numerous inspections and treatments during a year, we would seek a service contract to
pay for the treatments or consider legal abatement if a service contract is not secured. The cost
analysis in Table 2 of the draft operations and maintenance manual has funds allotted for
controlling vegetation and rodents, a line for mosquito control should be added to this annual
maintenance budget ($1,000 should be sufficient)
Again, we appreciate the opportunity to review and comment on the plans prior to construction.
The plan developers have added numerous improvements to this water quality control basin
compared to others that we have seen in our County. If you have any questions regarding my
comments, you can contact me at (510) 783-7744 or via email at acmad@mosquitoes.org,
Sincerely,
John R Rusmisel
District Manager
Cc: Ed Ballman
Chris Guillard
Attachment D: Dublin Ranch Water Quality Basin
WATER QUALITY BASIN MAINTENANCE TASKS
Maintenance Description
I. BASIN HYDROLOGICAL MONITORING & MAINTENANCE'I
1. Routine Hydrological Monitoring Tasks
2. Routine Hydrological Maintenance Tasks
3, Non-Routine Monitoring & Maintenance Tasks
Subtotal
II. PLANTING & IRRIGATION MAINTENANCE
A. FRONTAGE LANDSCAPE
1 Mowing (3 per year), Weeding, Irrigation Maintenance
2. Tree Work
Subtotal
B. UPPER AREAS
--,
Regular Mowing, Weeding, Irrigation Maintenance, Leaf Collection &
1. Removal
2. Tree Work
Subtotal
C. BASIN SLOPES
~ ___M___~" _.__
1, Mowing (3 per year), Weeding, Irrigation Maintenance
2. Tree Work
Subtotal
III. PAVEMENT MAINTENANCP
1. Gravel Access Road Resurfacing
2. Crushed Stone Pedestrian Paths - replace/regrading of 1/3 of area
CMG Landscape Architecturee
1
5/18/2005
Water Quality Basin Hydrological Monitoring and Maintenance
First-Year Routine Monitoring and Maintenance Activities
Monitorina Tasks
Water level and drawdown time
Water surface elevation checks
Drawdown time
Overall pond integrity
Side slopes and embankments
Presence of rills, slides, piping, etc,
Inlet structures
Evidence of erosion
Inlet structure integrity
Presence of litter and coarse debris in pond
Pump intake structure
Intake structure integrity
Presence of vegetation and debris around inlet. trash rack cleaning
Pump station
Pump and emergency power testing
Pump house maintenance
Check valve and flapgate integrity and operation
Sediment accumulation in ponds
History of sediment removal and testing activities
Assessment of sedimentation and neccessity of removal
Vegetation control in ponds
Assessment of trees, shrubs, weeds, and woody plants within pond
Access and fencing
Access road integrity and repair
Perimeter fencing integrity
Levee integrity
Side slopes and embankments
Presence of rills, slides, piping, etc,
First-year storm evene
Storm-event monitoring
Maintenance Tasks
Inlet and intake structures
Cleaning of inlet structures
Removal of litter and coarse debris in ponds
Cleaning of trash racks
Other routine maintenance
Vegetation control in ponds
Removal of trees, shrubs, weeds, and woody plants (routine trimming)
Levee system
Routing repair of rills and erosion
Control of vegetation and rodents (as needed)
Post First-Year Routine Monitoring and Maintenance Activities4
Monitoring Tasks
',-
Water Quality Basin Hydrological Monitoring and Maintenance
Maintenance Tasks
Estimated Post First-Year Annual Total
Non-routine Monitoring and Maintenance ActivitiesS
Repair of major structures (infrequently, if ever)6
Inlet or pump station repairs, pump replacement
Repair of access roads and fencing
Estimated Total
Sediment removal (approximately every 10 years or greater)
Labor
Sediment testing
Off-haul (2000 yd3 x $12/yd3)
Estimated Total
Large-scale vegetation removal (approximately every 5 years, as needed)
Labor
Off-haul (1000 yd3 x $12/yd3)