HomeMy WebLinkAbout; Macario Canyon Final Biological Monitoring Ltr Rpt; Biological Monitoring Letter Final Macario Canyon; 2006-12-01,:ONE .COMPANY Many Solutions-
December 1, 2006
Mr. Michael Sweesy
Dudek & Associates
605 Third Street
Encinitas, Califomia 92024
RE: Final Letter Report: Biological Monitoring Letter Report for Macario
Canyon (Carlsbad Mumcipal Golf Course)
Dear Mr. Sweesy:
HDR, Inc. is please to present the final letter report for the recently completed
biological monitoring effort associated with the Carlsbad Municipal Golf Course.
Introduction
HDR, Inc. was contracted by Dudek and Associate's to perform biological
monitoring during exotic vegetation removal in the Macario Canyon section of the
Carlsbad Municipal Golf Course.
The HDR biological monitor was responsible for ensuring removal of only noxious,
invasive, and/ or non-native vegetation. The biological monitoring was conducted
in compliance with the City of Carlsbad. In addition, the biological monitoring
noted the presence of any sensitive flora and fauna in the project site.
Proiect Description
The Carlsbad Municipal Golf Course (project site) is located approximately two
miles east of lnterstate-5 and a half mile north of Palomar Airport Road off Faraday
Road in the City of Carlsbad. The Carlsbad Municipal Golf Course is a new 18-
hole public golf facility with a club house, driving range, support facilities, and two
industrial pads, located on an estimated 400 acre site. HDR Biologists Nick
Muscolino and Eric Peffer monitored the removal of exotic species within the
riparian project site; Habitat Restoration Sciences (HRS) perfonned the exotic
vegetation removal.
The project site consisted primary of disturbed Southern Arroyo WiUow Riparian
Forest (Holland Code 61320). Landscape exotics were noted at the east end of the
site, adjacent to an old trailer park. The entire site is primarily dominated by Arroyo
willow (Salix lasiolepis) and also supports mule fat (Baccharis salicifolia), bulmsh
(Scirpus acutus), and cattails (Typha angustifolia). The primary invasive exotic
species being eradicated from the site include Brazihan pepper trees (Schinus
terebinthifolius), white ash trees (Fraxinus,americana), Italian cypress trees
(Cupressus sempervirens), tamarisk (Tamarix sp.), Mexican fan palm trees
(Washingtoniafilifera), and pampas grass (Cortaderia selloana). Refer to
Appendix B for all flora and fauna observed onsite during the biological monitoring.
HDR Engineering, Inc. 8690 Balboa Avenue
Suite 200
San Diego, CA 92123
858-712-8400
858-712-8333 (fax)
Site Monitoring
Daily Biological monitoring was initiated on 17 October 2006 and was terminated
on 30 November 2006. HDR biologists were directed to be onsite and monitor for
approximately four hours per day during vegetation removal. Typically, the
biological monitor was onsite to observe vegetation removal activities during the
moming hours from 0700 to 1100. Per direction from the client on 7 November
2006, the monitoring schedule was modified from five days a week to two days a
week. Refer to Appendix C for the daily field monitoring forms.
The crew of HRS was monitored and directed, as necessary, when sensitive
biological resoiu-ces were encountered. For example, instmction was provided to
the crew not to dismantle or disturb woodrat (Neotoma sp.) nests when encountered.
No disturbance occurred to known woodrat nests during the biological monitoring.
The crew used hand tools, chain saws, and herbicides to remove and control the
invasive exotic species within the project site. All of the exotic trees were removed
by cutting them down with chains saws, followed by hand removal from the project
site. Care was employed by the crews not to fell trees onto native vegetation. All
tree stumps were left in place but were treated with a commercial herbicide. The
majority of the pampas grass was previously treated with herbicide earlier in the
year and was dead. Removal of the dead pampas grass was performed using hand
tools such as picks and pitchforks. Approximately 25 live pampas grass plants were
observed and removed from the project site. No motorized equipment was used in
the open waters of the project site. Appendix A contains photo documentation of
the on site activities.
Conclusions
No biological issues of concem were noted during the field monitoring. Work
crews successfiilly removed exotic, invasive, and noxious vegetation without
harming sensitive biological resources (i.e., woodrat nests and riparian areas).
Further maintenance and monitoring is recommended, as necessary, to hamper re-
establishment of exotic vegetation. Currently, a small retention pond supporting
invasive tamarisk is located south of the project site. Because of its close proximity,
tamarisk eradication from this pond should be considered to keep the invasive
species from encroaching into the project site.
If there are any questions regarding the monitoring effort, results, or conclusions
please feel free to contact me at 858-712-8360. Submission of this final letter report
successfiilly completes our contractual agreement to provide biological monitoring
services.
Sincerely,
Nick Muscolino
Staff Biologist
HDR Engineering, Inc.
DUDEK
605 THIRD STREET
ENCINITAS, CALIFORNIA 92024
T 760.942.5147
F 760.632.8710
LETTER OF TRANSMITTAL
To:
Attention:
City of Carlsbad
1200 Carlsbad Village Drive
Carlsbad, California 92008
John Cahill
DATE: 11-30-07 JOBNO. 4821-05
RE: Carlsbad Municipal Golf Course
Contact No. 2 - Golf Course Construction
We are sending you the following items:
MECEIVEB
DEC 0 4 2007
ENGINEERING
DEPARTMENT
Copies DATE NO. DESCRIPTION
1 12/1/2006 Final Letter Report: Biological Monitoring Letter Report for Macario Canyon
(Carlsbad Municipal Golf Course)
THESE ARE SENT as checked below:
For approval X For your use As requested For review and comment
Other
Remarks: This report should be included with the Phase 2 final report we recently sent to you.
Please call, fax, or e-mail any questions or comments you have about the report
and we will be happy to discuss it.
Copy to: Signed:
Appendix A
Looking west over the project site after exotics were removed from the east end.
Cuttings hand carried out of riparian area to be chipped.
HRS crew performs chipping of cuttings outside of the riparian area.
•.»•'•» ••^^•*'^'^M'^^*%'oi(ri'-^'' • •
A Brazilian pepper tree smmp treated with herbicide.
Wood rat nest left undisturbed during exotic vegetation removal.
HRS crew using hand tools to removing pampas grass from the project site.
Appendix B
Species List
Birds
House finch Carpodacus mexicanus
Yellow-mmped warbler Dendroica coronata
Common yellowthroat Geothlypis trichas
White-crowned sparrow Zonotrichia leucophrys
Song sparrow Melospiza melodia
Black phoebe Sayomis nigricans
Califomia towhee Pipilo crissalis
Anna's hummingbird Calypte anna
Westem scmb jay Aphelocoma californica
American crow Corvus brachyrhynchos
Common raven Corvus corax
Cooper's hawk Accipiter cooperii
Red-tailed hawk Buteo jamaicensis
American coot Fulica americana
Killdeer Charadrius vociferus
Belted king fisher Ceryle alcyon
Nuttall's woodpecker Picoides nuttallii
Mammals
Woodrat Neotoma sp (nests)
Coyote Canis latrans (tracks)
Flora
Arroyo willow Salix lasiolepis
Mule fat Baccharis salicifolia
Coyote bush Baccharis pilularis
Califomia sycamore Platanus racemosa
Tamarisk Tamarix sp.
Buhush Scirpus acutus
Cattail Typha angustifolia
Brazilian pepper Schinus terebinthifolius
Italian cypress Cupressus sempervirens
Mexican fan palm Washingtonia filifera
Pampas grass Cortaderia selloana
Appendix G
Biological Monitoring Field Forms
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