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NORTH AGUA HEDIONDA INTERCEPTOR WESTERN
SEGMENT REALIGNMENT PROJECT
Prepared for:
City of Carlsbad
1635 Faraday Avenue
Carlsbad, California 92008
Contact; Mork Biskup
760 602 2763
Prepared by:
605 Third Street
Encinitas, California 92024
Contact: Vipul Joshi
vjoshi@dudek.com
MARCH 2010
Printed on 30% post-consumer recycled material.
Final Monitoring Report for the
North Agua l-ledionda Interceptor Western Segment
Realignment Project
TABLE OF CONTENTS
Section Page No.
1.0 INTRODUCTION 1
2.0 PROJECT CONSTRUCTION/MONITORING ACTIVITIES 1
2.1 Western Staging Area 2
2.2 Central Staging Area 2
2.3 Eastern Staging Area. 8
3.0 IMPACTS 8
3.1 Post-Construction Survey 9
3.2 Impacts Summary '. 10
4.0 MITIGATION 10
APPENDIX
A Photo Documentation
LIST OF FIGURES
1 Regional Map 3
2 Vicinity Map 5
3 Impact Map 11
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Final Monitoring Report for the
North Agua Hedionda Interceptor Western Segment
Realignment Project
1.0 INTRODUCTION
The purpose of this final monitoring report is to summarize the construction and monitoring
activities of the completed North Agua Hedionda Interceptor (NAHI) Western Segment
Realignment Project (Project) arid related impacts to demonstrate compliance with the permit
conditions set forth in Coastal Development Permit No. 6-07-92 issued by the California Coastal
Commission (CCC) August 12, 2008.
The NAHI Project is constructed primarily by means of micro-tunnel installation, as opposed to
traditional trench excavation and installation. Consequently, the impacts of the Project are
limited to construction staging areas and access roads. The Coastal Development Permit (CDP)
requires that all staging and storage areas be maintained within the proposed staging areas
located outside of sensitive habitat. The Project's construction monitoring activities are provided
here to demonstrate compliance with this condition. This report also provides the results of a 90-
day post-construction survey conducted February 23, 2010, as required under CDP.
The applicant for the Project is the City of Carlsbad (City). The Project involved relocating the
existing NAHI located along the northern shoreline of the Agua Hedionda Lagoon farther inland
using micro-tunneling techniques.
The Project site is located in the City, within the County of San Diego, California. The Project
site is located along the north shore of Agua Hedionda Lagoon from Hoover Street in the west to
Cove Drive in the east. It is situated on the U.S. Geological Survey 7.5-minute San Luis Rey
topographic quadrangle, Section 8, Range 4 West, Tovraship 12 South (Figures 1 and 2).
2.0 PROJECT CONSTRUCTION/MONITORING ACTIVITIES
Construction began on February 2, 2009, with clearing of the western staging area. Construction
monitoring was conducted to ensure compliance with permit conditions regarding avoidance of
native biological resources. Monitoring confirmed compliance with the CDP Special Condition
(SC) #8 that all staging and storage areas shall be maintained within the proposed staging areas
located outside of sensitive habitat. Photographs for photo documentation were taken during
each site visit. Pre-construction, during construction, and post-construction photographs are
provided in Appendix A. The monitor also attended weekly progress update meetings during the
initial stages of the Project.
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2.1 Western Staging Area
Vegetation was cleared and silt fencing installation began February 2, 2009, prior to drill arrival
on site. This area was mapped as disturbed habitat and consisted primarily of fig-marigold
{Carpobrotus edulis). There were no impacts to native vegetation.
The coastal salt marsh along the southern boundary was not included within the staging area as
this area did not require disturbance. ^
The vegetation clearing initially followed the flagging that had been established prior to
construction. However, after referencing the construction plans, it became clear that the global
positioning system (GPS) used to delineate the boundaries must have not been calibrated
correctly. Triangulation was used to correct this error, making the staging area extend farther
west on the western side. No native vegetation was impacted as a result of this change.
Vegetation clearing continued and pipes were unloaded onto the staging area February 4, 2009.
Drilling began after this and continued through February 11, 2009. A steel pipe was installed
after drilling ceased. Work subsequent to that included filling the pipe and moving material
around to set up the staging area.
The steel pipe had been installed and the drill was no longer set up at this staging area by
February 13,2009.
The construction trailer was set up at this staging area in March.
2.2 Central Staging Area
Dudek biologists flagged and recorded the limits of native vegetation using a global GPS prior to
construction on September 25, 2008. This established the limit of work outside of coastal sage
scrub habitat.
Trenching for the installation of silt fencing began February 2, 2009, and installation was
completed February 4, 2009. Sandbags were placed along fencing on February 5, 2009. Grading
of disturbed vegetation followed installation of silt fencing.
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FIGURE 1
Regional Map
FINAL MONITORING REPORT for the NORTH AGUA HEDIONDA INTERCEPTOR WESTERN SEGMENT REALIGNMENT PROJECT DRAFT
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Realignment Project
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Dudek biologists walked the perimeter of the staging area, which was already flagged, with the
contractor as he painted the limits for the installation of the silt fencing to ensure no native
vegetation would be impacted. Silt fencing was installed outside of all native vegetation (i.e.,
coastal sage scrub).
The surveyors established where the drill pit would be placed on February 4, 2009. There was an
approximate 20-foot buffer around this location, which enabled the crew to install and operate
the drill without extending the silt fencing outward and impacting coastal sage scrub.
Grading continued within the limits established by the silt fencing to improve the access "road"
through the staging area for the drill rig to be moved to this location February 12, 2009.
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The drill rig was set up at the southern end of the staging area. A sound wall intended to reduce
noise levels at adjacent occupied California gnatcatcher {Polioptila californica) habitat was
installed. The sound wall consisted of K-rails with 20-foot-high posts lined with plywood and
sound blankets and was located around the area where the drill was to be operating in the
southern portion of the central staging area.
A Dudek biologist reported at the weekly update meeting on February 18, 2009, that although
the Project was out of compliance with the Mitigated Negative Declaration (MND) regarding
California gnatcatcher mitigation, both the City and the U.S. Fish and Wildlife Service (USFWS)
were in agreement that work could be allowed to continue given the establishment of a sound
barrier. California gnatcatcher monitoring had not reported the birds to be nesting at that time.
Drilling at the central staging area was scheduled to begin February 19, 2009, and be completed
February 25, 2009.
At the subsequent weekly update meeting, the status of the California gnatcatcher was discussed.
Specifically, the birds were found nesting on February 23, 2009, and the agencies (California
Department of Fish and Game (CDFG) and USFWS) had been notified. California gnatcatcher
monitoring would no longer be necessary and noise walls would remain in place at that time.
Drilling at this staging area was competed February 26, 2009 and demobilization followed.
Roads were closed as the drill was moved from the work area.
At the weekly update meeting on March 4, 2009, it was reported that the California gnatcatcher
should not be a concern unless noise levels increased. However, it was agreed that the issue
would remain on the agenda to address potential noise increases associated with mobilization of
the micro-tunneling effort, which was not scheduled until April.
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The sound wall was restored after wind knocked it down in late March. While the noise wall was
beneficial and the resource agencies had asked for it during the drilling phase of the Project,
dismantling it at this stage was determined to not be a concern.
Micro-tunneling from the center staging area westward begari in April. The noise generated by
the micro-tunneling process was generally lower than the ambient noise generated from freeway
traffic near the California gnatcatcher nest location.
2.3 Eastern Staging Area
On February 24, 2009, silt fencing was installed where a 15-foot-wide easement exists.
Native vegetation was flagged at this staging area. An area of approximately 8 x 15 feet located
at the northeastern edge of the coastal sage scrub would be impacted by the installation of a 6-
inch pipeline. This area primarily consisted of an immature stand of California encelia (Encelia
californica), but also included prickly-pear cactus (Opuntia littoralis), California sagebrush
{Artemisia californica), California buckwheat (Eriogonum fasciculatum), coyote bush
(Baccharis pilularis), and deerweed {Lotus scoparius), all small in stature. Mustard {Sisymbrium
sp.) and bare ground also composed approximately 25% cover in this area. However, this area
does not require additional mitigation, since it had already been mitigated for and thus authorized
by the CCC for impact. The City and Dudek reviewed the existing conservation credit purchase
agreement and acknowledgement obtained by the property owner, and determined that the
impacts would be allowable under the existing agreement. The conservation credit purchase
agreement and acknowledgement confirmed that the property owner had purchased 0.5 credit
fi-om the Carlsbad Highland Conservation Bank for construction of a two-story single-family
residence at 4485 Adams Street in the City of Carisbad (APN 206-200-04), for which the CCC
had issued a permit (Application No. 6-68-14) in 1998.
Initial work at the eastern staging area involved prepping for the installation of the 6-inch
pipeline, which involved excavating a trench north of the silt fencing.
3.0 IMPACTS
Hydroseed application followed completion of construction and was completed November 23,
2009. Hydroseed was applied to all impacted staging areas in accordance with the
landscaping/replanting plan. Biological monitoring was conducted to ensure the correct seed mix
was applied in the appropriate manner. The following species were included in the hydroseed
mix:
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Big saltbush {Atriplex lentiformis)
Bush monkey flower {Mimulus aurantiacus var. aurantiacus)
Common yarrow {Achillea millefolium)
Golden-yarrow {Eriophyllum confertiflorum)
Salt heliotrope {Heliotropium curassavicum)
Deerweed
Purple needlegrass {Nassella pulchra)
Foothill needlegrass {Nassella lepida)
Coast range melic {Melica imperfecta)
Salt grass {Distichlis spicata)
Deergrass {Muhlenbergia rigens)
California poppy {Eschscholzia californica)
Owl's-clover {Castilleja exserta)
Miniature lupine {Lupinus bicolor)
Arroyo lupine {Lupinus succulentus)
Dot-seed plantain {Plantago erecta)
Fringed willowherb {Epilobium ciliatum), which replaced hummingbird trumpet
{Epilobium canum) after approval due to availability.
3.1 Post-Construction Survey
A post-construction survey was conducted February 23, 2010, by Dudek biologist Kathleen
Dayton (from 8:15 a.m.-9:45 a.m.; conditions were surmy, clear, little to no wind). Each stagirig
area was walked and observations regarding existing conditions in terms of impacted areas,
vegetation, and general site conditions were recorded. Photographs wei"e taken to document
conditions and the location of the silt fencing was recorded with a GPS unit to document the
final limits of impact.
The silt fencing installed prior to construction was still standing. Straw wattles were also still in
place as erosion control features at each staging location. Fericing to control access had been
installed along the northern boundary of the central staging area and along the road at the eastern
staging area.
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Realignment Project
No impacts outside of the established silt fencing were evident at the time of the post-
construction survey at each staging area. Minimal evidence of erosion was present at each
staging area. Total vegetative cover of the hydroseeded western staging area was relatively low.
However, evidence of hydroseeded plants were observed, such as lupine {Lupinus sp.), purple
owl's-clover, and dot-seed plantain. Vegetative cover along the edges of the staging area was
greater than at the center, which was covered by more bare ground. Total vegetative cover was
greater at both the central and eastern staging areas. These areas were primarily dominated by |||
non-native species, including mustards and wild radish {Raphanus sdtiva).
Since impacts were limited to approved staging area locations within disturbed/non-native
habitat and previously mitigated land, no temporary impacts remain that would require additional
mitigation or restoration.
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3.2 Impacts Summary |
I Impacts documented during NAHI western segment alignment activities did not exceed the
permitted impacts (Figure 3). The western staging area consisted entirely of disturbed habitat
dominated primarily by fig-marigold. The cismontane alkali marsh south of this staging area was
not impacted. All of the coastal sage scrub was avoided at the central staging area via pre-
construction flagging and verified during monitoring of silt fence installation. Although minor
impacts to native vegetation occurred at the eastern staging area (120 square feet), this area was
previously mitigated. I
4.0 MITIGATION
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1 The City plans to maintain the staging areas for at least 1 year and maintenance needs will be re-
evaluated in the future in order to meet the 5-year standard stipulated in the CDP. The CDP
requires a landscape monitoring report to be completed 5 years from the date of issuance of the
permit (issued March 6, 2008). This report will include photo documentation of plant species and I
coverage in order to ensure that all on-site landscaping complies with the approved
landscape/planting plan. A revised supplemental landscape plan will be required if landscaping is ^
not in conformance with the landscape/planting plan or if it has failed to meet the specified .1
performance standards.
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SOURCE: DIGITALGLOBE 2008. FIGURE 3
Impact Map
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APPENDIX A
Photo Documentation
APPENDIX A
Photo Documentation
PRE-CONSTRUCTION
Western Stage
Pre-construction Survey. Photo taken 1/22/09
Pre-construction Survey. Photo taken 1/22/09
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APPENDIX A (Continued)
Central Stage
Pre-construction Survey. Photo taken 9/25/08
Pre-construction Survey. Photo taken 9/25/08
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APPENDIX A (Continued)
Pre-construction Survey. Photo taken 9/25/08
Pre-construction Survey. Photo taken 9/25/08
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APPENDIX A (Continued)
Pre-construction Survey. Photo taken 9/25/08
Pre-construction Survey. Photo taken 9/25/08
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APPENDIX A (Continued)
Eastern Stage
Pre-construction Survey. Photo taken 1/22/09
Pre-construction Survey. Photo taken 1/22/09
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APPENDIX A (Continued)
DURING CONSTRUCTION
Western Stage
Vegetation clearing of staging area and silt fence installation. Photo taken 2/2/09.
Staging area set-up. Photo taken 2/3/09.
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APPENDIX A (Continued)
Set-up with construction trailer. Photo taken 5/28/09.
Central Stage
Silt fence installation and vegetation clearing. Photo taken 2/4/09.
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APPENDIX A (Continued)
Stage preparation for drill rig set-up. Photo taken 2/11/09.
Drill and sound wall. Photo taken 2/19/09.
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APPENDIX A (Continued)
Micro-tunneling. Photo taken 4/14/09.
Eastern Stage
Excavation for installation of the 6-inch pipeline. Photo taken 3/4/09.
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APPENDIX A (Continued)
Pipeline installation prep. Photo taken 3/16/09
POST-CONSTRUCTION
Western Stage
Post-construction Survey. Photo taken 2/23/10
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APPENDIX A (Continued)
Post-construction Survey. Photo taken 2/23/10
Central Stage
Post-construction Survey. Photo taken 2/23/10
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APPENDIX A (Continued)
Post-construction Survey. Photo taken 2/23/10
Post-construction Survey. Photo taken 2/23/10
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APPENDIX A (Continued)
Eastern Stage
Post-construction Survey. Photo taken 2/23/10
Post-construction Survey. Photo taken 2/23/10
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