HomeMy WebLinkAbout; Municipal Golf Course Revised Upland Minigation; Upland Mitigation Plan Revised Muni Golf Course; 2004-11-01CITY OF CARLSBAD
REVISED
GOLF COURSE
UPLAND MITIGATION PLAN
Prepared for:
CITY OF CARLSBAD
1635 Faraday Avenue
Carisbad, Cahfomia 92008
Contact; John Cahill
Telephone: 760-602-2926
Prepared by:
P&D ENVIRONMENTAL
A Division of P&D Consultants, Inc.
8954 Rio San Diego Drive, Suite 610
San Diego, Califomia 92108
Contact: Chuck Moore
Telephone: 619-291-1475
November 2004
fA
TABLE OF CONTENTS
Section Page
1.0 Revegetation Mitigation :.... 1
1.1 Personnel 1
1.2 Contractor Education.. 2
2.0 Methodology: :.: 2
2.1 Upland Habitat Creation 2
2.2 Monitoring and Maintenance : 4
3.0 Final Mitigation Success 7
3.1 Success Criteria. , 7
3!2 Contingency Measures 8
LIST OF TABLES
Table Page
1 Hydroseed Mix 3
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1.0 REVEGETATION MITIGATION
This report will discuss the upland mitigation measures and the critical elements of the upland
mitigation plan for the Carlsbad Municipal Golf Course.
Regular monitoring until the plants are established will allow early detection of areas of poor
growth or cover, dying plantings, weed invasion, and erosion problems. These problems can then
be addressed and appropriate corrective actions taken. The monitoring will be performed in
conjunction with a long-term maintenance program.
1.1 Personnel
Restoration Biologist
An experienced restoration biologist will coordinate the mitigation installation and maintenance
activities. The restoration biologist will supervise these activities and provide quality assurance
and control including confirming that the site is prepared properly, the exotic plant eradication
measures are implemented properly, and that the seeding and planting specifications follow those
outlined in this mitigation plan. The restoration biologist will also oversee mitigation measures
during the 5-year monitoring and maintenance period, including horticultural and botanical
monitoring requirements.
The restoration biologist shall have the following minimum qualifications:
• a bachelor's degree in biology, ecology, botany, horticulture, or landscape architecture
• knowledge of the vegetation associations proposed for the restoration effort including
species identification, composition, canopy, understory, and species ecological positions
• a minimum of 2 years of practical horticultural experience or equivalent study, including
plant installation, fertilization, weeding, pmning, irrigation, and pest control
• knowledge of avian biology, the Federal and Califomia Endangered Species Act (FESA/
CESA), the Clean Water Act, and jurisdictional boundaries
Installation Contractor
An experienced native habitat landscape contractor shall be retained to perform the mitigation
installation under the direction of the restoration biologist. The installation contractor must be
experienced in installing native habitat mitigation areas in southem Califomia. The installation
contractor will be responsible for the following:
• ordering specified plant materiai and seed from appropriate vendors, based on the
specifications of the mitigation plan. In order to ensure the availability of the appropriate
plant materials and achieve the minimum cost, sufficient lead time should be allocated
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• installing the plant materials per the specifications of the mitigation plan
• implementing remedial actions under the direction of the restoration biologist
1.2 Contractor Education
All contractors that complete some aspect of the mitigation plan will meet at the site with the
project's restoration biologist before beginning any work in the area. The restoration biologist
will review all requirements of the plan that concern each contractor, including site protection,
inspections, landscape procedures, and guarantees. The restoration biologist will have final
supervisory control over field installation.
2.0 METHODOLOGY
There are seven primary requirements for the success of a habitat restoration effort:
1. Selecting an appropriate location for the restoration effort.
2. Removing nonnative mderal species that compete with desired species.
3. Preparing soil, including topsoil importation and/or mycorrhizal fungi inoculation if
necessary.
4. Seeding or planting with appropriate plant species for the location and microclimate.
5. Protecting the site from further disturbance.
6. Monitoring success and making changes to the program if necessary.
7. Maintaining the site during the plant establishment period. This may include weeding,
trash removal, irrigation, and barrier repair.
2.1 Upland Habitat Creation
Areas for upland habitat creation are identified on the landscape plans prepared by KTU+A.
Hydroseed Mix
The hydroseed mix will include the designated seed mix and a light mulch. The hydroseed mix
should be spread over the site to conceal the seed from predators, protect it from wind and rain
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erosion, and help retain moisture. The mulch should be made of 93%o wood cellulose/fiber matrix
with 7% organic soil stabilizer. The seed mix includes the following species:
Table 1. Hydroseed Mix
Species Pounds/Acre %) Purity % Germination
Adolphia californica 1.0 . — —
Artemesia californica 3.0 15 50
Coreopsis gigantea 3.0 40 60
Diplacus longiflorus 3.0 — —
Encelia californica 6.0 40 60
Eriogonum fasciculatum 15.0 10 65
Eschscholzia californica 4.0 98 75
Lots scoparius 6.0 90 60
Rhus laurina 4.0 • 95 60
Salvia aliana 5.0 70 50
Salvia mellifera 5.0 70 50
Solanum xantii 1.0 — —
TOTAL 56 lbs/acre
Source Material
It is preferred that the source of all seed used at the mitigation site originate from the vicinity of
the mitigation site. Although not required for this site, experienced native plant nurseries
regularly contract grow locally collected plant material for use in mitigation projects. If
sufficient time does not exist in which to collect and propagate site-specific plant materials,
native plant nurseries typically have plant material local to the southem Califomia coastal region,
which would be suitable for this restoration plan. Many nurseries in southem Califomia supply
native plants.
The restoration biologist will work closely with the landscape contractor and the suppliers to
approve all sources or plant materials. The landscape contractor will provide the restoration
biologist with information on the sources of all plant and seed materials grown, collected, or
acquired for the project for final approval. If necessary, the project restoration biologist will help
the contractor locate local sources of plant materials.
Substitutions ' . " • '
The native habitat landscape contractor is expected to secure the necessary plant material prior to
the expected planting date. In general, no substitutions above 10 percent of any specified species
number will be allowed.
Seeding Specifications
All seeding activities in the mitigation area will occur after all container plants have been
installed and any necessary weed eradication is complete. The mitigation area will be seeded
with the mix shown in Table 1. This approach will be used to mimic the natural distribution of
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Revised Golf Course Upland Mitigation Plan
these species. Seeding activities will proceed only after the restoration biologist certifies that the
site preparation has been completed. Seed quality will be the best obtainable in the year of
application for both purity and germination. Amount of seed purchased, germination, and seed
purity will be provided in writing to the restoration biologist by the contractor for all seed used.
Irrigation Plan
Temporary irrigation -will be provided to ensure plant establishment. Watering will be provided
during the dry season for the first two years of the plant establishment period. Following the
second winter season, the watering schedule will be gradually reduced to allow the plants to
acclimate to the natural seasonal water supply.
As-Built Conditions
Within 6 weeks of project installation, the restoration biologist will certify in writing that
mitigation installation has been completed. The restoration biologist will submit a report to the
City and resource agencies describing as-built conditions of the mitigation area.
2.2 Monitoring and Maintenance
A vital component of any revegetation program developed to mitigate habitat loss is
documentation of the progress of the revegetation program until the plants are established.
General observations will be important in documenting areas of poor growth or cover, dying
plantings, weed invasion, and erosion problems. These areas can then be independently
monitored and scheduled for rhore intensive maintenance activities. If necessary, the areas may
be replanted or reseeded.
The monitoring program will use a variety of qualitative and quantitative procedures to
document the changes in plant gro-wth of the target species and changes in the density and
dominance of all plant and wildlife species within the sampled areas. One of the most important
procedures will be standardized observation of the entire site to provide a general record of
trends on the mitigation site including plant growth. Potential coverage may include
photographic documentation from designated points which would give a visual record of the
changes in stmcture and cover of the sites over time. Quantitative studies would be conducted to
obtain plant cover estimates, make seedling counts, and monitor changes in plant diversity
onsite.
Performance Criteria
There are generally two types of performance criteria used to monitor the success of a
revegetation effort; measurements of survival rates and measurements of vegetation coverage.
Which of these criteria is appropriate depends on several factors, including the goals and
objectives of the project, the time frame of the monitoring effort, and the types of habitat being
established. For the Carlsbad Golf Course mitigation project, determination of vegetative cover
is the appropriate measure of project success.
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The performance goal of the project in the upland revegetation areas will be 75 percent
vegetative cover in late spring or early summer at the end of 5 years. The 75 percent figure was
chosen because coastal sage scmb is a habitat that naturally has a patchy distribution with many
interstitial areas that support only annual herbs or no vegetation. Intermediate growth and
coverage goals established for the areas have also been identified. These goals should be
considered progress indicators, rather than success or failure criteria. The goals include:
• 60 percent cover at the end of two years
• 70 percent cover at the end of three years
• 75 percent cover at the end of four years
The 75 percent cover is the ultimate goal, and should be sustained through year 5. If the 75
percent goal is reached and sustained for one year prior to the five-year monitoring and
maintenance period, the portion of the project will be considered a success and the monitoring
period will end. The intermediate goals will serve as indicators ofthe plan's interim success. In
the event that the intermediate goals are not reached the plan vvill be adapted to improve project
success. Ifthe 75 percent coverage goal is not reached by the end of the maintenance period, the
problem will be analyzed to determine the reason for the lack of success. Required adjustments
to the plan will be made and the monitoring period will be extended.
Additionally, as required by Special Condition 2 of the Coastal Development Permit, the
following goals, objectives, and success criteria shall be met:
• At minimum, five years after the initial planting, the restored areas shall support at least
10 species of native plants appropriate to characterize .the vegetation type.
• At minimum, five years after the initial planting, the restored areas shall show evidence
of recmitment for at least five species of native plants appropriate to characterize the
vegetation type.
• Weeds shall be controlled and never constitute more than 10 percent ofthe total cover.
Quantitative Monitoring
The line-intercept sampling method will be used to determine the amount of cover achieved. To
measure coverage by the line intercept method a transect (line) is established between two
points. A tape measure is then stmng between the two points, and the length of intersection that
each species has with the line is measured. When the coverage of all species is totaled, the result
is frequently greater than the length Ofthe transect, because many species have overlapping areas
of coverage. By measuring the area of bare ground intersection, the total vegetative cover can be
established. The number of transects required will be determined by the monitoring biologist for
the upland revegetation area.
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Data obtained from the transect monitoring will be analyzed using appropriate statistical methods
as determined by a qualified restoration biologist. These methods will include the use of a'power
analysis, and will be used to monitor the species diversity at the site as well as the level bf cover.
Qualitative Monitoring
The upland mitigation sites will be visually inspected, and qualitative or subjective
determinations about the success of the revegetation will be made. This is necessary because the
quantitative sample sites might not include important data.
Schedule
Immediately following installation, the site will be monitored monthly for six months to evaluate
germination and the initial success of the revegetation effort. If germination is unsuccessful or
the seedlings do not survive, a change in scope may be required to determine the cause of failure.
For the 6- to 12-month period, monitoring will be quarterly. If the success criteria are being met
at the end of 12 months, from Month 12 to the end of the 5-year monitoring period, the site will
be monitored annually. To ensure the success of the revegetation program, any areas that require
reinstallation of materials will have their monitoring program started over at the time of
reinstallation.
Annual Reports
The restoration biologist will be responsible for conducting monitoring ofthe project through the
5-year monitoring period. The restoration biologist will qualitatively and quantitatively evaluate
project success in relation to the project performance criteria and submit reports documenting
project progress. Annual reports will be submitted to the City of Carlsbad. The City of Carlsbad
will be responsible for submitting the report to the USFWS, CDFG, and CCC.
Reports filed at the end of each year will include a summary and analysis of the abiotic and
biotic monitoring data collected and an evaluation of project progress relative to success
standards.
These reports will include the following:
• a list of names, titles, and companies of all persons who prepared the content of the
annual report and participated in monitoring activities for that year;
• an analysis of all qualitative and quantitative monitoring data, including applicable
statistical analyses;
• a report of number of acres of exotic vegetation removed, treated, and retreated;
• copies of monitoring photographs; and
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• maps identifying monitoring areas, ttansects, planting zones, etc., as appropriate.
Maintenance
The restoration biologist will supervise the control and eradication of invasive exotic species
from the restoration/enhancement area. Invasive exotics control will require effort throughout
the 5-year maintenance and monitoring period to achieve effective control. Many invasive
exotics require repeated and properly timed control measures. In addition, propagules are likely
to wash or blow into the mitigation site and recolonize it. The Maintenance Program includes
this ongoing exotics control component. The restoration biologist will direct the contractor
regarding the selection of target weed species, their location, and the timing of weed control
operations to ensure that native plants are avoided to the maximum extent possible. The
restoration biologist will determine if, at any time, chemical control is to be used. As required by
Special Condition 2(g) of the Coastal Development Permit, no weed whips shall be permitted
after installation of the seed mixes. The type, quantity, and method of herbicide application will
be determined by a California licensed pest control adviser (PCA) who will inspect the site and
recommend methods of application and rates to the restoration biologist. Pesticide
recommendations shall be limited to those appropriate for native habitat restoration. The
restoration biologist will approve the rates, methods, and areas to which pesticides are to be
apphed.
Weed control requires constant diligence by the landscape maintenance contractor. The first 18
months of the project establishment is the cmcial period for weed control. A 48-inch-wide plant-
free band will be maintained around all container plants and cuttings for the first 18 months after
planting. Throughout the rest ofthe project, the restoration biologist will specify which weed
species are to be controlled. Weed control procedures will take place at least monthly during the
first 18 months. More frequent control measures will be performed as necessary or as
recommended by the restoration biologist to keep weeds at manageable levels. The landscape
maintenance contractor should consult a hcensed Pest Control Advisor if specific pest control
recommendations are necessary. The landscape maintenance contractor will give special
attention to the control of invasive exotic weed species in the wetland mitigation areas.
3.0 FINAL MITIGATION SUCCESS
3.1 Success Criteria
If the project meets all success standards at the end of the 5-year monitoring period, the
mitigation will be considered a success. When the initial 5-year monitoring period is complete
and if the City believes final success standards have been met, the City will notify the resource
agencies when submitting the annual report that documents this completion. The City recognizes
that failure of any portion of the mitigation plan shall result in the requirement to replace that
portion of failed mitigation.
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2.4 Contingency Measures
The project includes a mitigation monitoring and reporting program that requires the mitigation,
to meet the success criteria. In the event that the site is considered a failure and remedial actions
are unacceptable due to engineering, chemical, or physical constraints, the City will work with
the USFWS, CCC and CDFG in identifying a suitable remedial action program.
Additionally, in accordance with the Coastal Development Permit requirements, if the success
criteria are not met after 6 years, an amendment to the permit shall be required. No changes to
the mitigation plans shall occur without a CCC approved amendment to the Coastal
Development Permit unless the Executive Director determines that no amendment is legally
required.
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