HomeMy WebLinkAboutGPA 06-09; Muroya Subdivision; General Plan Amendment (GPA) (5)-
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PRESERVE MANAGEMENT PLAN
for the
MUROYA PROPERTY
CITY OF CARLSBAD, CALIFORNIA
Prepared for:
Taylor Morrison of California, LLC.
15 Cushing
Irvine, California 92618
Prepared by:
DUDEK
605 Third Street
Encinitas, California 92024
Tel. 760.942.5147
rk-M1J:t.~
Anita M. Hayworth, D, Senior Biologist
JULY 2011
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Preserve Management Plan for the Muroya Property
TABLE OF CONTENTS
Section Page No.
1.0 INTRODUCTION .............................................................................................................. l
2.0 PRESERVE AREA DESCRIPTION ............................................................................. 13
3.0 HABITAT AND SPECIES DESCRIPTION ................................................................. 15
4.0 MANAGEMENT AND MONITORING GOALS AND ASMDS ............................... 25
5.0 ADAPTIVE MANAGEMENT ....................................................................................... 33
6.0 ADMINISTRATION AND REPORTING .................................................................... 35
7.0 LITERATURE CITED ................................................................................................... 3 7
APPENDICES
A
8
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List of Plant Species Observed on Site
Wildlife Species Observed on Site
PAR Habitat Planning in Perpetuity
LIST OF FIGURES
2
3
4
5
Regional Map ....................................................................................................................... 5
Vicinity Map ........................................................................................................................ 7
Focused Planning Area and Proposed Preserve ................................................................... 9
Biological Resources ......................................................................................................... 11
Muroya Project Preserve .................................................................................................... 17
LIST OF TABLES
2
3
Existing Plant Communities/Land Covers on the Muroya Property Preserve .................. .15
Common Weed and Invasive/Exotic Species to be Controlled within the Project Site ..... 30
Preserve Management Task Summary ............................................................................... 31
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1.0 INTRODUCTION
A. Purpose for Inclusion of the Preserve Area in the Habitat Management Plan
The proposed project on the Muroya property is an approximately 11.5-acre residential
development within the approximately 20-acre property. The proposed preserve area of the
project, a total of 8.50 acres is proposed to provide mitigation for direct impacts to the habitat on
site and to be included in the assembly of the Carlsbad Habitat Management Plan (HMP; City of
Carlsbad 1999, finalized 2004) preserve. This Preserve Management Plan (PMP) has been
prepared for the preserved open space areas (preserve) within the Muroya project site (Figures 1
and 2). The Muroya project was approved and mitigation identified in the Mitigated Negative
Declaration (State Clearinghouse 2010021061; City of Carlsbad, CA 2009). The project is
identified under the following application numbers: GPA 06-09/ AC 06-08/LCPA 06-09/SP
203D/CT 06-27.
The City of Carlsbad is a member ofthe North County Multiple Habitat Conservation Plan (MHCP;
San Diego Association of Governments 2001) and has adopted an HMP (Habitat Management
Plan) which is a subarea plan under the MHCP. The MHCP is a comprehensive, multiple
jurisdictional planning tool designed to create, manage, and monitor an ecosystem preserve in
northwestern San Diego County. The HMP is a citywide program with the purpose of preserving the
diversity of species and habitats as well as sensitive biological resources while allowing for
development that is consistent with City plans. The objectives of the HMP are to develop a plan that
conserves the full range of vegetation types with the focus on rare species and habitat; conserves
areas capable of supporting covered species in perpetuity; and maintains functional wildlife corridors
and habitat linkages. Under the HMP, a portion of the project area, as well as surrounding lands, are
within a Focused Planning Area (FPA) of the City. FPA boundaries were created based on the
existing distribution of vegetation communities and sensitive species. The FP As were further broken
down into HMP cores, linkages and Special Resource Areas.
The Muroya property is located within the Local Facilities Management Zone 20 and is
designated as a Standards Area in the HMP. It is located approximately in the central portion of
Linkage Area F which is part of a stepping stone linkage connecting Core Areas 4, 6 and 8 and
contains significant amounts of coastal sage scrub acting as a corridor for movement for the
gnatcatcher and other avian species. The property is somewhat isolated from other patches of
native habitat except for the southern boundary. However, Aviara Parkway lies adjacent to those
habitats and fragments any potential corridors resulting in a stepping stone linkage.
Figure 3 provides an overview of surrounding development, adjacent preserve areas and the
proposed standards areas within the HMP. As a standards area, the Muroya property goals and
standards for preservation have been identified according to the Local Facilities Management
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Plan. These standards, as applicable to this specific property, include avoiding impacts to
southern maritime chaparral and narrow endemic plant species, minimizing impacts to coastal
sage scrub, providing continuous habitat connectivity within the zone, but allowing reasonable
development with a focus on the lower habitat quality areas.
The Citywide standard for the narrow endemic species is to conserve 100% within preserve areas
and conserve at least 80% outside preserve areas. Within the Muroya project, there are no narrow
endemic species so this requirement is not applicable. Section 7-14 of the HMP states that
Assessor Parcel 215-040-03 (Muroya property) proposes to cluster development within existing
disturbed areas to the maximum extent feasible and that a maximum of 10% impact may occur to
coastal sage scrub and southern maritime chaparral. The project proposes to impact 5.6% of
these habitats and thus is in compliance. The HMP also identifies the need for buffers and fuel
modification zones to be provided between preserve areas and proposed development within the
study area. The HMP identifies that a 20-foot buffer is required between development and native
vegetation. The proposed development of the Muroya Property conforms to all of the identified
goals and standards outlined in the HMP.
The development of the site is consistent with the HMP with respect to the covered species of the
HMP (Figure 4). Currently three HMP-covered plant species (Nuttall's scrub oak) and one HMP-
covered wildlife species (California gnatcatcher) are found to be present on site. Two plant
species that are covered contingent on other subarea plans are also found on site, including wart-
stemmed ceanothus and Englemann oak. One special status non-covered plant species is present
on site, California adolphia. The HMP management and conservation goals for these species are
discussed below.
B. Preserve Area History
The proposed 8.50-acre Muroya Property preserve has been within the ownership of the overall
approximately 20-acre Muroya Property. An additional 1.3 acres of preserve area is located
within the SDG&E easement north of the project preserve. The SDG&E preserve area is not part
of this PMP. There has been no specific management of the proposed preserve area prior to the
current plan.
C. Purpose Of This Management Plan
1. The plan guides management of habitats, species, and programs described herein to
achieve the City's obligation to protect and enhance wildlife values under the MHCP,
HMP, and Implementing Agreement.
2. The Plan serves as a guide for appropriate public uses of the preserve area.
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3. The plan serves as a descriptive inventory of native plant and wildlife species and
habitats, which occur on or use this preserve area .
Preserve Manager contact information:
TBD
Preserve Manager must have appropriate qualifications consistent with CDFG guidelines and be
approved by the City .
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Preserve Management Plan for Muroya Project I FIGtEl
Regional Map
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Vicinity Map
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&S] Proposed Development
~ HMPCore
Linkages
HMP Conservation Areas:
! :::::: j: j Proposed Standards Area
188.88 Existing Hardline Conservation Area
[:sJ Proposed Hardline Conservation Area
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HMP Planning Area and Proposed Preserve
Preserve Management Plan for the Muroya Property
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~ Muroya Project Preserve HMP Species:
c::J HMP Preserve AC , California adelphia
HMP Vegetation Communities: AG, Del Mar manzanita
Chaparral AI , San Diego thorn-mint
Agriculture BF, Thread-leaved brodiaea
.. Oak Woodland BO, Orcutt's brodiaea
Coastal Sage Scrub BS, Belding's Savannah sparrow
Disturbed Habitat BV, Encinitas baccharis
.. Eucalyptus Woodland
.. Maritime Succulent Scrub
Native Grassland
Non-native Grassland
Riparian Scrub/Forest
.. Southern Maritime Chaparral
Urban/Developed
BW, Burrowing owl
CG, California gnatcatcher
CH, Cooper's hawk
CN , San Diego sand aster
CV, Wart-stemmed ceanothus
DO, Western dichondra
HL, San Diego homed lizard
HP, Palmer's grappling hook
LH, Loggerhead shrike
LN, Nuttall's lotus
MD, Southern mule deer
NH, Northern harrier
OW, Orange-throated whiptail
PT, Torrey pine
QD, Nuttall's scrub oak
QE, Engelmann oak
RH , Red-shouldered Hawk
RP, CA rufous-crowned sparrow
SC, Ashy spike-moss
SO, San Diego sea-dahlia
SY, Summer holly
TV, Turkey Vulture
~ ----===::JFeet "1' 0 1,000
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Biological Resources
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2.0 PRESERVE AREA DESCRIPTION
A. Geographical Setting
The approximately 20-acre Muroya property is located within the City of Carlsbad, San Diego
,.. County, California. The study area is physically located along the west side of Black Rail Road, a
111111 secondary street off A viara Parkway (Figure 1 ). The property is situated centrally within the U.S.
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Geological Survey (USGS) 7.5-minute Encinitas quadrangle, T12S, R4W; Section 28 (Figure 2).
B. Geology, Soils, Climate and Hydrology
The topography on site consists of a flat bench where the nursery and single family home are
located. From the bench the topography slopes quickly down into a network of incised ravines
that are oriented from east to west/southwest. Elevations range from approximately 50 to 180
feet above mean sea level. The climate of the region is Mediterranean with mild summers and
winters and rainfall occurring predominantly during the winter.
The soil types on site, according to the San Diego County Soil Survey (Bowman 1973), include
Chesterton fine sandy loam (CfC), 5% to 9% slopes; Chesterton fine sandy loam (CfD2), 9% to
15% slopes; and rough broken lands (RuG). Chesterton fine sandy loams occur on coastal ridges
and are moderately well drained with a sandy clay subsoil. The soils were formed in material
weathered in place from soft ferruginous sandstone. Rough broken land is made up of well
drained to excessively drained, steep and very steep land dissected by many narrow v-shaped
valleys and divides. Areas of exposed soil, is common within rough broken land making runoff
very rapid and creating a high potential for erosion.
C. Preserve Area Boundaries and Historic/Adjacent Land Use
Approximately 8 acres of the study area is currently being used as a palm tree nursery. This
includes shade houses, outbuildings, and associated access roads. A single-family residence is
located in the southeastern portion of the property. The remaining area is undeveloped and
dominated by native vegetation. Surrounding land use is currently developed as single-family
residential homes. The preserve is a stepping stone corridor within Linkage F for the movement
and dispersal of the California gnatcatcher. This linkages contains fragmented patches of coastal
sage scrub and chaparral.
D. Ownership and Legal Description
The owner/developer is Taylor Morrison of California, LLC. The Assessor Parcel Number is
215-040-03. The preserve manager has not been selected. The qualifications of the Preserve
Manager must be consistent with CDFG guidelines and approved by the City.
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E. Conservation Easement Compliance
The Conservation Easement (CE), anticipated to be approved in August 2011, provides a list of
permitted and prohibited uses of the land. These include the following permitted uses:
• Reasonable access through the preserve to perform obligations permitted by the CE;
• Access to safety organizations for a public health or safety matter;
• Habitat enhancement activities;
• Debris and exotic species removal;
• Installation of signs;
• Fire protection.
The following are prohibited uses:
• Supplemental watering;
• Use of pesticides or fertilizers
• Incompatible fire protection activities
• Use of off-road vehicles unless necessary for restoration;
• Livestock grazing or other agriculture;
• Recreations activities except as allowed in the PMP;
• Residential, commercial, retail, institutional, or industrial uses;
• Construction or placement of buildings or other improvements
• Dumping of soil, trash, refuse, etc.;
• Planting or introducing non-native plants or animals;
• Filling, dumping, excavating, etc.;
• Altering the topography;
• Removing, destroying or cutting trees, shrubs, or other vegetation;
• Manipulating, impounding or altering natural watercourses;
• Fuel modification zones.
Conservation Easement compliance monitoring will be conducted on an annual basis to
document that the requirements and stipulations of the CE are being followed. The compliance
monitoring visit is conducted in conjunction with other regularly scheduled visits and includes
filling a form to document that the Preserve is in compliance with the CE and taking photographs
at the specified photo monitoring points as described below.
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3.0 HABITAT AND SPECIES DESCRIPTION
Biological surveys of the property, including vegetation mapping, a wetland delineation and
wildlife and plant surveys were conducted by Dudek biologists Scott M. Boczkiewicz, Clint J.
Emerson, Anita M. Hayworth, PhD, Paul M. Lemons, and Michelle L. Balk. Surveys were
conducted by foot and the entire property was surveyed and inventoried for biotic components. A
focused survey for the coastal California gnatcatcher (Polioptila californica californica) was
conducted by Mr. Lemons and Dr. Hayworth. A spring survey for special-status plant species
was conducted in April 2007; the fall survey was conducted in October 2006. An update and
confirmation of existing biological resources conditions was conducted in July 2009 by Tricia L.
Wotipka. Detailed information on the biological resources of the site is provided in the
Biological Technical Report (Dudek 2010).
A. Vegetation Communities
Based on species composition and general physiognomy, nine plant communities/land cover
types were identified within the study area: southern maritime chaparral, coastal sage scrub,
southern mixed chaparral, developed land, native grassland, ornamental plantings, disturbed
land, and agricultural lands. The plant communities/land covers are shown in Figure 5 and
tabulated in Table 1.
Table 1
Existing Plant Communities/Land Covers on the Muroya Property Preserve
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Agriculture
This land cover refers to the part of the study area in which palm trees are actively being grown
for retail sale. The area consists of rows of potted palm trees that are anywhere from seedlings to
large mature trees and occur under shade houses and in the open. Agricultural lands account for
the largest amount of land within the study area covering 0.71 acres.
Coastal Sage Scrub
Coastal sage scrub is a native plant community composed of a variety of soft, low, aromatic
shrubs, characteristically dominated by drought-deciduous species such as California sagebrush
(Artemisia californica), flat-top buckwheat (Eriogonum fasciculatum), and sages (Salvia spp.);
with scattered evergreen shrubs, including lemonadeberry (Rhus integrifolia), laurel sumac
(Malosma laurina), and toyon (Heteromeles arbutifolia). It typically develops on south-facing
slopes and other xeric situations.
Two areas of coastal sage scrub were found within the study area. One large area in the
southwestern portion of the project is characterized by narrow ridges dissecting incised gullies
with exposed barren soils. The second small polygon is along the western portion of the property
and occurs on a short steep slope that quickly intergrades into southern maritime chaparral. A
total of 2.01 acres of coastal sage scrub were mapped within the study area.
Within the southern portion of the site, there is a small patch of coastal sage scrub dominated by
coyote brush (Baccharis pilularis). Baccharis-dominated coastal sage scrub typically develops in
drainage bottoms or mesic floodplains following disturbance to the native plant community. This
community is dominated by coyote brush, with a few successional elements of the former native
community, including California sagebrush, flat-top buckwheat, coast goldenbush (Isocoma
menziesii), or other disturbance-tolerant native plants. The understory usually includes a variety
ofnon-native herbs and grasses. The polygon continues to the south offthe property. Within the
study area there was 0.02 acre of Baccharis-dominated coastal sage scrub mapped.
Disturbed Land
Disturbed land refers to areas where vegetation growth is limited as the result of mechanical
perturbation causing bare dirt to exist in perpetuity. Disturbed land on site includes all dirt roads
that dissect the nursery facility allowing access to transport palm trees. A total of 0.06 acres of
disturbed land was mapped within the study area.
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Q Muroya Project Preserve
CZ) HMP 20-Foot Buffer
Sensitive Animal Species:
CAGN = California gnatcatcher
Sensitive Plant Species (with counts):
Ac = Adolphia califomica
Cv = Ceanothus verrucosus
Qd = Quercus dumosa
Qe = Quercus engelmannii
0 Vegetation Communities:
.... ~ ... ~--Jurisdictional Waters (1-ft widths)
G Data Station with Unique ID
AGR =Agriculture
CSS = Coastal Sage Scrub
DEV = Developed Land
DH = Disturbed Habitat
NG =Native Grassland
ORN = Ornamental Planting
SMC =Southern Maritime Chaparral
SMX =Southern Mixed Chaparral
LOT, IMPACTS
0 Proposed Development Lot & HOA Lot -Developed
0 Proposed HOA Lot -BMZ 1 & 2
Proposed HOA Lot -HMP 20-Ft Buffer & BMZ3
0 Proposed HOA Lot -HMP 20-Ft Buffer only
0 Proposed HOA Lot -Additional HMP Buffer
0 Proposed OS Lot -Project Preserve
0 Proposed OS Lot -SDG&E NCCP Governed Preserve
0 Muroya Residence
II Muroya Residence -HMP 20-Ft Buffer
Proposed Chaparral Restoration
c:::J Southern Maritime Chaparral
E3 Southern Mixed Chaparral
Preserve Management Plan for Muroya ProJect 5 . I FIGURE I
Muroya Project Preserve
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Native Grassland
This vegetation community type occurs in flat basin areas at the termination of narrow channels
where giant wild rye (Leymus condensatus) has formed dense thickets and is the only species
occurring in the area. The areas appear to be potential wetland sites but soils are not hydric and
hydrology indicators are absent. A total of 0.19 acre of native grassland was mapped within the
study area.
Ornamental Plantings
Ornamental plantings within the study area are mostly dominated by iceplant
Mesembryanthemum crystallinum) and hottentot-fig (Carpobrotus edulis). It is likely that these
areas were not planted with these species but have probably spread and encroached from the
original areas where they were planted. There were 0.16 acres of ornamental plantings mapped
within the study area.
Southern Maritime Chaparral
Southern maritime chaparral is similar to southern mixed chaparral but is restricted to coastal
localities within the fog belt and typically develops on sandstone soils. This community is
characterized by several shrubs of limited distribution, including Del Mar manzanita
(Arctostaphylos glandulosa var. crassifolia), wart-stemmed ceanothus (Ceanothus verrucosus),
coast spicebush (Cneoridium dumosum), and Nuttall's scrub oak (Quercus dumosa). Other
shrubs encountered frequently in this community are chamise (Adenostoma fasciculatum),
lemonadeberry, laurel sumac, toyon, and summer-holly (Comarostaphylis diversifolia).
Within the study area, southern maritime chaparral consists primarily of Nuttall's scrub oak,
wart-stemmed ceanothus, chamise, and mission manzanita (Xylococcus bicolor). Understory
species include monkey-flower (Mimulus aurantiacus) and black sage (Salvia mellifera).
Southern maritime chaparral is well distributed within the undeveloped portion of the property
accounting for a majority of the area. There were 4.64 acres of southern maritime chaparral
mapped within the study area.
Southern Mixed Chaparral
Characterized by broad-leaved sclerophyll shrubs generally 1.5-3 meters tall forming dense
impenetrable vegetation dominated by a mix of chamise, lemonade berry, toyon (Arctostaphylos
spp.), and Nuttall's scrub oak. It is usually found on north facing slopes in dry rocky areas and is
often adjacent to chamise chaparral, southern maritime chaparral, and coastal sage scrub
vegetation associations .
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Within the study area southern mixed chaparral occurs as a large polygon on a steep rocky north
facing slope in the southern portion of the site. Dominant species include to yon and lemonade
berry. There was 0.72 acre mapped as southern mixed chaparral within the study area.
B. Jurisdictional Resources
There were seven separate drainages found within the study area where highly incised channels
drain water seasonally during high rainfall events. These ephemeral waters do not drain into any
wetlands or navigable waters ofthe U.S. and therefore are not considered jurisdictional wetlands
by the ACOE, CDFG, or Regional Water Control Board (RWQCB). Ephemeral waters are
waters that are not inundated or saturated for extended periods and generally have surface water
only for a very short time (24 hours or less) following a significant rain event. In contrast,
intermittent waters have a surface flow that, although not perennial, may be present for relatively
long periods (greater than 24 hours) following rainfall events. Intermittent streams may support
some vegetation characteristic of wetlands, whereas ephemeral streams typically do not.
Hydrology is indicated in these stream channels by the presence of an ordinary high water mark.
Mapped waters of the U.S. account for a total of 0.02 acre of the study area and are mapped as
linear features in Figure 5, but are not included in the total for the plant communities because
they are located within upland plant communities.
C. Plant Species
All plant species encountered during the field surveys were identified and recorded. Latin and
common names of plants follow the Jepson Manual (Hickman 1993). Where not listed in
Hickman (1993), common names are taken from Beauchamp (1986). A list of plant species
observed on the property during the surveys is presented in Appendix A. A total of 59 plant
species were recorded for the site within the preserve area. Of this species inventory, 17 species
(29%) are non-native and 42 species (71%) are native. The dominant plant species within each
vegetation community are provided above under the descriptions of the vegetation communities.
D. Wildlife species
A total of 25 bird species were recorded during the general field survey of the site. Additional
species commonly observed on site included western scrub-jay (Aphelocoma californica),
Anna's hummingbird (Calypte anna), California towhee (Pipilo crissalis), song sparrow
(Melospiza melodia), and northern mockingbird (Mimus polyglottos). A complete list of bird
species observed during the field surveys are listed in Appendix B.
No amphibian species were observed on site. One reptile species, western fence lizard
(Sceloporus occidentalis), was observed on site.
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Five mammal species were observed or detected (by scat and other sign) during the mammal
surveys, including California ground squirrel (Spermophilus beecheyi), coyote (Canis latrans),
brush rabbit (Sylvilagus bachmani), woodrat (Neotoma sp.), and mouse (Peromyscus sp.).
E. Species Covered by the HMP and Other Sensitive species
No plant species listed as rare, threatened, or endangered by USFWS or the California CDFG
were detected in the project area. Four species designated as sensitive by the California Native
Plant Society (CNPS) were detected in the project area: California Adolphia (Adolphia
californica), a CNPS List 2.1 species; Nuttall's scrub oak (Quercus dumosa), a CNPS List lB.l
species; wart-stemmed ceanothus (Ceanothus verru~osus), a CNPS List 2.2 species; and
Engelmann's oak (Quercus engelmannii), a CNPS List 4.2 species. These species are discussed
in more detail below and are provided in Table 2. All of these species will be monitored
periodically to document their numbers and distribution. The monitoring will be summarized in
Section 4A.
Table 2
Special Status Plant Species Present within the Muroya Preserve
Wart-stemmed ceanothus1
Ceanothus verrucosus
Nuttall's scrub oak1
Quercus dumosa
Engelmann oak1
Quercus enge/mannii
None/None
None/None
None/None
1 Carlsbad HMP Species of Concern
2.2
18.1
Chaparral, coastal scrub, valley
and foothill grassland; clay/
shrub/ blooms December-May
Sandstone and metavolcanic
soils in mixed chaparral and
chamise chaparral; elevation 1-
380 meters. Shrub (evergreen),
blooms December-April.
total of three individuals
observed on site within
southern portion of the
property.
14 individuals found within
southern maritime chaparral in
the study area in fall 2006.
Closed-cone coniferous forest, 16 individuals
chaparral, coastal scrub/ sandy, scattered throughout southern
clay loam soils; elevation 15-400 maritime chaparral within the
meters. Shrub (evergreen), study area.
blooms
4.2 Chaparral, cismontane woodland, One individual tree located on
riparian woodland, valley and the edge of the palm tree
grassland; elevation 120-nursery and a polygon of
1,300 meters. Tree (deciduous), southern mixed chaparral.
blooms M<>rrr'-""""
California adolphia was found in a small clump of three individuals within the southern portion
of the site within the coastal sage scrub (Figure 5). This species tends to occur on clay soils
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within shrub, scrub and grassland communities. As a shrub, threats to the species are limited and
predominantly due to development. This species is considered somewhat endangered in
California but is common and stable outside of the state.
Nuttall's scrub oak was found growing in southern maritime chaparral and is a key species
indicating that vegetation association. Approximately 16 Nuttall's scrub oaks were found
scattered throughout the study area (Figure 5). This species occurs in shrub and scrub vegetation
communities on sandy and clay loam soils. Nuttall's scrub oak is known only from southern
California and northern Baja California and is very rare and threatened by development.
Wart-stemmed ceanothus is also a species indicator of southern maritime chaparral and was
found scattered throughout the vegetation association within the study area. Approximately 14
individual shrubs were found scattered throughout the study area. This species occurs on
sandstone and metavolcanic soils in mixed chaparral and chamise chaparral vegegtation
communities. As a shrub, threats to the species are limited and predominantly due to
development. Wart-stemmed ceanothus is rare and somewhat endangered in California but is
common and stable outside of the state.
One old and large Engelmann oak tree was found on the property. The tree is located on the edge
of a bench that slopes quickly down into a ravine in a transition area between agricultural and
southern mixed chaparral. This species occurs in chaparral, cismontane woodland, riparian
woodland and valley and foothill grasslands. Engelmann oak is a watch list species because it
has a limited distribution but is fairly common within the area where it occurs.
Special status wildlife species included the California gnatcatcher (Polioptila californica), a
federally listed threatened species (Table 3). Two pairs of California gnatcatcher were observed
within coastal sage scrub on the project site. One pair was observed in the northernmost portion
of the preserve adjacent to the agriculture area. The other pair was observed in the southern area
adjacent to the off site undeveloped land. This species occurs predominantly in coastal sage
scrub but also in coastal sage scrub-chaparral and coastal sage scrub-grassland ecotones. The
California gnatcatcher is threatened by development and edge effects including urban
mesopredators such as dogs and cats.
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Table3
Special Status Wildlife Species Present within the Muroya Preserve
Coastal California FT/CSC Coastal sage scrub, coastal sage Two pair observed on site during
Gnatcatcher1
Polioptila califomica califomica
1 Carlsbad HMP Species of Concern
Federal Designations:
FT = Federally listed Threatened
State Designations:
scrub-chaparral mix, coastal sage focused surveys.
scrub-grassland ecotone, riparian in
late summer
CSC = California Department of Fish and Game Species of Concern
A. F. Fire history
No fire history is available other than from the current owner. There have been no fires recorded
for the site under the current owner.
B. G. Threats
Threats to the native species and habitats are minimal. There is currently very little human
intrusion into the preserve area because it has been under gated control. Threats are
predominantly due to weed invasion from the previous agriculture use of the property.
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4.0 MANAGEMENT AND MONITORING GOALS AND ASMDS
The monitoring and management of the Muroya preserve follows the guidelines developed by
the MHCP and provided in the MHCP Monitoring and Management Plan (SANDAG 2003).
Initial tasks that will be conducted within the preserve include weed removal and restoration of
the agriculture, disturbed habitat, and ornamental areas to southern maritime chaparral. The
initial weed control is discussed below and is the responsibility of Taylor Morrison of California,
LLC. The restoration also is the responsibility of Taylor Morrison of California, LLC. The
restoration areas will not be included within the preserve until the restoration has met success
criteria. A total of eight fixed photo point locations will be established during the initial tasks
within the first year of the management of the preserve. These points will be established
according to the Preserve Manager in order to obtain the best view but generally will be located
at the north and south perimeters, facing into the preserve, and at two locations along the east
and west perimeters. Two additional points will be located along the central ridge within the
preserve and will face towards the opposite direction from their corresponding location.
In general, the open space area is composed of native vegetation communities, however two
conditions were noted that need to be addressed prior to the conveyance of the open space lot.
There appear to be some deposits of landscape clippings and roadside debris; however. large
trash items such as refrigerators and abandoned vehicles do not appear to be a problem. Weeds
are also a minor problem and should be controlled prior to conveyance. Three non-native
invasive weed species were noted to be of noticeable coverage within the open space; however,
other weeds also are present. The main non-native invasive species that need to be controlled
include hottentot-fig (Carpobrotus edulis), pampas grass (Cortaderia sp.), and black mustard
(Brassica nigra).
The project proposes to conduct on-site restoration of suitable disturbed, agriculture or other
non-functional habitat within the coastal zone for all of the impacts. The mitigation for the
southern maritime chaparral and southern mixed chaparral will be accomplished through the on-
site restoration of non-native habitat. These areas currently do not function as native habitat and
have no native plant species present. A total of 0.87 acre of southern maritime chaparral and 0.05
acre of southern mixed chaparral will be restored within the areas currently mapped as
agriculture, disturbed land, and ornamental as described above. This acreage suitable for
restoration totals 0.93 acre. The bulk of the potential restoration areas are in the southern portion
of the site currently mapped as agriculture. If needed the northern portion of agriculture land will
also be restored. If the restoration biologist feels it is more appropriate to restore all of the
required mitigation area to southern maritime chaparral, this will satisfy the requirement for the
southern mixed chaparral mitigation. Prior to implementing the restoration activities, conceptual
mitigation plans will be prepared and approved by the City and resource agencies. These plans
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will identify the location of the on-site restoration, the plant palette to be used and the goals and
success criteria of the mitigation. The restoration activities are not the responsibility of the
Preserve Manager and upon completion of the restoration, the areas mapped as agriculture,
disturbed land, and ornamental will be southern maritime and/or southern mixed chaparral.
Once the success criteria have been met, the restoration site will become part of the preserve and
will be managed according to this PMP.
A. Biological Monitoring and Management
The biological goals for the PMP include the maintenance of the existing condition of the
preserve. Restoration of the agriculture, ornamental, and disturbed habitat has been planned and
is part of the development proposal. The restoration will be conducted by the project applicant.
There will be a number of documents and tasks required for the restoration activities including:
conceptual mitigation plan, plans and specifications, installation, 5-year monitoring and
management of the restoration area. The monitoring of the restoration area will also be the
responsibility of the applicant until it is considered successful and has been signed off,
approximately 5 years from installation. Upon successful completion of the restoration, the
restored area, which will be restored to native southern maritime chaparral, will be included in
the overall preserve management and monitoring.
Monitoring tasks include vegetation community monitoring, plant species monitoring and
wildlife monitoring. Quarterly monitoring visits will be conducted and may focus on wildlife or
botany and for general purposes to view the site conditions and detect trash and invasive plant
populations that need control. Annually, photos will be taken from the eight fixed points within
the preserve; locations are described in general terms above and will be established during the
first year of the management of the preserve. These photos will provide documentation of the
quality of the habitat and in conjunction with the quarterly visits, will determine if other actions
are required in order to maintain the habitat. The photos from the eight fixed photo point
locations will be included in the appendix of the annual monitoring report.
According to the MHCP Monitoring and Management Plan (SANDAG 2003), vegetation
community mapping is required initially, and then every five years to update the information. All
habitats within the open space preserve will be mapped on aerials of the site at a scale of one
inch equals 1 00 feet. This work shall include accessing and obtaining available updated aerial
photographs of the site every five years.
Four plant species and one wildlife species considered sensitive were identified on site, including
Nuttall's scrub oak, wart-stemmed ceanothus, California adolphia, Engelmann oak and coastal
California gnatcatcher. The California adolphia, wart-stemmed ceanothus, Nuttall's scrub oak
and coastal California gnatcatcher are HMP-covered species. Details about conservation goals,
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impact avoidance/minimization measures and management recommendations can be found in the
HMP. In accordance with the MHCP Monitoring and Management Plan (SANDAG 2003), plant
and wildlife presence/absence surveys are required for the four HMP-covered species that occur
on site to document the sensitive species occurrences within the open space areas.
For special status plant species it is assumed that managing the habitat will be sufficient to
maintain the species. The objective for monitoring these species is to track its presence in the
open space preserve using a systematic survey (SANDAG 2003). A presence/absence survey
will be conducted, wherein the general condition of the habitat and the degree of disturbance, if
any, will be observed and recorded. For the plant survey, the timing of the survey is not critical
because the species are perennial species that are observable year-round. Monitoring focused on
determining the number and location of each of these species will be conducted every 5 years.
For coastal California gnatcatcher, focused surveys will be conducted every five years. Focused
surveys will consist of three site visits during the breeding season, with surveys conducted during
February through August as deemed most appropriate by the biologist, with at least a seven-day
interval between site visits, in accordance with USFWS survey requirements (USFWS 1997) and
the requirements ofthe MHCP Monitoring and Management Plan (Section 3.1.3, SANDAG 2003).
The focused surveys will be conducted by a biologist holding a valid lO(a) permit. A report
detailing the results of the focused survey will be prepared and submitted to the appropriate
agencies. This will be in addition to the overall general report for the open space preserve.
Constraints
Due to the presence of the federally listed threatened California gnatcatcher, constraints to
activities within the preserve may be due to the need to avoid activities during the breeding
season. Weed removal may need to be conducted by hand if done within the areas occupied by
the gnatcatcher .
Potential Impacts
Potential impacts from the monitoring and management may occur if weed removal is conducted
during the breeding season of the gnatcatcher. To avoid impacts, weed removal, if required to be
done within areas actively used by the gnatcatcher, will be conducted by hand or outside of the
breeding season. No other impacts from the monitoring and management activities are anticipated.
Area Specific Management Directives
Individual project or tasks that implement a particular goal are considered Area Specific
Management Directives (ASMDs). These tasks are described below in greater detail.
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Erosion Control
Any significant unnatural erosion occurring within the open space preserve shall be repaired
promptly after it is detected, to minimize additional soil loss. For the purposes of this document,
unnatural erosion is considered to be erosion that may occur as a direct or indirect result of
human activity. Erosion control measures shall be implemented, as necessary, to prevent
recurring erosion problems. Erosion control measures can include, but are not limited to,
installing water bars, silt fencing, straw wattles, filter fabric, or other appropriate material, and
seeding with natives, to minimize or prevent erosion.
Erosion control measures are anticipated to be minimal for the open space preserve because it is
mostly covered by established vegetation. However, there are jurisdictional ephemeral drainages
and erosional features that occur naturally within the open space preserve, and some small areas
that currently do not support vegetation that may require some erosion control measures in the
future. Minor erosion control problems such as rill erosion repair, minor sediment deposition, or
erosion repairs may need to be addressed.
Landscaping Restrictions
Active landscaping should be absent within the open space area. However, if problems are
detected at the interface between nearby development slopes and the open space area, then
intervention shall be initiated to correct these problems. Potential problems could include the
introduction of and/or expansion of nonnative invasive plant species into the open space,
irrigation runoff, excess nitrogen runoff, or pesticide overspray into the open space area.
Fencing, Gates, Signs
Upon completion of grading and construction for the proposed development area, the temporary
construction/silt fencing will be removed and a permanent fence will be placed at the edge of the
residential backyards to prevent access to the open space. Although the fencing will not be
placed along the edge of the preserve, by fencing the backyards, no additional fencing is
required. The responsibility for installation of the fencing, walls and gates will be borne by the
owner. The responsibility for maintenance and replacement of the fencing, walls and gates will
reside with the HOA or individual homeowners. No fencing is required along the western
boundary due to the existing fencing that is already in place. No fencing is required along the
southern portion because the preserve is contiguous with other preserve lands. Hence no fencing
maintenance or installation is required of the Preserve Manager.
Signs will be installed for access control and public education around the perimeter of the open
space preserve. These signs will inform the HOA of the location of the preserve boundary and
preclude brush management activities from extending into the preserve. Eight to fifteen small (14
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inches by 20 inches) aluminum signs displaying pertinent restrictive information, such as
"Habitat Conservation Area", and "No Trespassing" and "No brush management activities
beyond this sign" will be installed on posts at potential public access points. Initial installation of
signs will be provided by Taylor Morrison of California, LLC and replacement will be the
responsibility of the Preserve Manager.
Exotic Species Control
Exotic/invasive (non-native) plant species control will be an ongoing process in perpetuity .
Exotic/invasive plant species control will be conducted twice per year to keep weeds at
manageable levels. A general guide for which invasive exotic plants should be controlled if they
occur in the open space area is included in Table 2 ofthis PMP. The Preserve Manager will need
to determine which areas are in need of exotic/invasive plant species control. Therefore, this
PMP assumes that a habitat restoration specialist will survey the site twice per year for the
presence of exotic/invasive plant species. A combination of mechanical and chemical control
methods will be used to control exotic/invasive plants on site.
There are several non-native plant species that are present or have the potential to be present on
site. Target non-native species selected for control in this PMP include those non-native plant
species that are potentially invasive, and/or pose a threat to the establishment, development or
persistence of native habitat or wildlife. The primary target species shall be those species identified
and listed by The California Invasive Plant Council (Cal-IPC, formerly the California Exotic Pest
Plant Council, Cal EPPC) in the publication: "California Invasive Plant Inventory" (Cal-IPC,
2007). Target species of that publication are classified by Cal-IPC into list categories. List
categories established by Cal-IPC are based on aggressiveness of invaders, geographical
distribution throughout California and potential to spread explosively (Cal EPPC, 1999). The Cal-
IPC invasive plant categories include, High, severe ecological impacts on physical processes, plant
and animal communities, vegetation structure, and widely distributed ecologically; Moderate,
substantial and apparent, but generally not severe, ecological impacts on physical process, plant
and animal communities, vegetation structure, ecological amplitude and distribution may range
from limited to widespread; Limited, invasive but their ecological impacts are minor on a statewide
level or there was not enough information to justify a higher score, ecological amplitude and
distribution are generally limited but these species may be locally persistent and problematic .
Additional weed species may be added to this list if they appear to pose a risk, or a potential risk,
to the persistence of the native habitat and wildlife on site.
For the purposes of open space preserve management and maintenance measures, exotic weed
species requiring control are divided into two groups; Low Tolerance Species (Group 1) and No
Tolerance Species (Group 2, Table 4). In general, Low Tolerance Species are those that could
potentially pose a threat to the persistence of native habitats, but are usually not strong invaders.
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Most of the species in Group I are annuals. Species in Group 2 are considered strong invaders
and have the potential to displace native habitat. Species in Group 2 are perennials.
Table 4
Common Weed and Invasive/Exotic Species to be Controlled within the Project Site
Group1 Group2
Non-Native Weeds to be Controlled by Hand Removal or Invasive Exotics to be Controlled by Hand Removal or
Mechanical Removal if They Exceed 10% Over Baseline Herbicide Application if Detected
Common Name Scientific Name Common Name Scientific Name
Sweet alyssum Lobularia maritime tree tobacco Nicotiana glauca
mustard Brassica spp.; Hirschfeldia Radish Raphanus sativus
incana
Russian thistle Sa/sola tragus Myoporum Myoporum laetum
non-native annual grasses Bromus spp., Po/ypogon Pampas grass Cortaderia selloana
monspeliensis, Avena spp.,
Vulpia myuros, Schism us
barb at us
ice plant Carpobrotus spp.;
Mesembryanthemum spp.
English ivy Hedera helix
Sweet fennel Foeniculum vulgare
Exotic invasive plant species control measures will consist of the complete removal of selected
non-native vegetation (i.e., seed heads, stems, roots), and all debris and slash generated from the
weed removal activities will be disposed of off site in a legally acceptable manner. Weed
removal will be conducted twice annually.
Weed control measures will include the following: (1) hand removal, (2) mechanical removal (e.g.,
cutting with weed whip machines, hoeing) and (3) herbicide application. The method of weed
control shall be based on the most effective method for the species and stage of plant development.
In general, hand removal of weeds is the preferred method of control, with other methods
implemented, as necessary. If possible, depending on the project schedule, weeds shall be
controlled when plants are young (i.e., 6-10 inches tall) and prior to the formation of seed heads. If
large areas require hand weeding (e.g., areas over 0.25 acre) seeding the area with a native seed
mix appropriate to this site, and locally collected, should be considered to inhibit re-colonization of
the area by non-native plant species.
In general, weed species listed in Group 1 should be removed manually (hand removal or
mechanical removal). Group 2 species include those that will likely require chemical control.
Herbicide applications will either be foliar applications of the entire pla~t, or cutting the plant
and painting the severed stem or trunk with a systemic herbicide. Cutting and painting the
severed stems, as opposed to foliar applications, will likely be the preferred method of chemical
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control because it reduces the chance of inadvertent overspray and consequent non-target plant
damage. The maintenance contractor should coordinate with the project biologist to identify
specific locations within the site where chemical herbicide treatments would be acceptable. All
herbicide treatments must be supervised by a licensed pest control advisor and applied under the
direction of a licensed pest control applicator.
The following Table 5 provides the itemized preserve management and monitoring tasks based
on the descriptions of the tasks above.
Table 5
Preserve Management Task Summary
Task Timing Staff Type
Baseline Inventory Mapping and Update Once at beginning on management Preserve Manager or qualified staff
during initiation of PMP
Site Monitoring Quarterly Preserve Manager or qualified staff
Habitat Monitoring/fixed photos point Annually Preserve Manager or qualified staff
Sensitive Plant Species Monitoring Every 5 years during a quarterly Preserve Manager or qualified staff
monitoring visit
Vegetation Mapping/revisions Every 5 years during a quarterly Preserve Manager or qualified staff
monitoring visit
California Gnatcatcher Protocol Survey Every 5 years Qualified Biologist with 10(a) permit
Exotic Weed control Twice annually during quarterly Preserve Manager or qualified staff
monitoring visit
Trash removal As needed during quarterly visits Preserve Manager or qualified staff
Public awareness and outreach Once annually based on communication Preserve Manager or qualified staff
with HOA
Annual Report Once annually Preserve Manager or qualified staff
B. Public Use
There is no anticipated public use of the Muroya open space. No trails or other recreational uses
are planned.
A. C. Fire Management
Although it is not anticipated that a catastrophic fire may occur due to the location within an
urbanized setting, if a fire occurs within the open space preserve, either burning all or a portion
of the site, the vegetation will be allowed to naturally regenerate. No fire management is
anticipated for the preserve. Fire is a naturally occurring event that produces healthy vegetation.
The proposed Muroya development project has the required fuel management zones that are all
contained within the management of the HOA. The open space preserve does not include any
areas slated for brush control or fire/fuel management. Fire management, if it becomes
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necessary, is assumed to be the ongoing responsibility of the property owner. Therefore, fire
management between the open space preserve and the development edge is not a requirement of
this Property Management Plan.
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5.0 ADAPTIVE MANAGEMENT
Adaptive management is defined as a flexible, iterative approach to the long-term management
of biological resources that is guided over time by direct observation of the results of ongoing
management activities. Preserve areas are subject to a variety of changing conditions including
changes in biology such as normal population changes, legal such as new listings or de-listings
of resident species, and social such as pressures from recreational use. Adaptive management
will include the utilization of annual qualitative assessments and data gathered in the field to
assess the health and vigor of habitat within the preserve area. California gnatcatcher and special
status plant species monitoring shall be conducted consistent with the Carlsbad HMP. Results of
species monitoring shall be factored into adaptive management decision making and actions in
consultation with the Preserve Manager. Adaptive management actions will be implemented on
an as-needed basis to address perceived deficiencies. As such, adaptive management for the
Muroya preserve will include:
• Analysis and interpretation of the information gathered from the site will be viewed in
context with results from other preserve areas as appropriate.
• The management plan will be updated every five years in order to incorporate
information from the monitoring. This provides an opportunity to review the relevant
information from the site as well as other preserve areas.
• The Preserve Manager will have a strong background in biological sciences and
familiarity with the management techniques in similar preserves.
• Sound recording keeping will provide the support for any changes that occur and will
document when conditions continue to be stable .
This PMP provides the biological monitoring methods and schedule that provides input into the
adaptive management approach.
Fire is a natural occurrence in the San Diego County back country. Many upland, as well as
native wetland, species are adapted to survive and recover following a fire event. Should fire
damage reduce the native cover and/or cause other damage to the site, an assessment will be
made to determine the level of damage and an appropriate course of action as demonstrated in
this PMP. Fire response may range from letting the site recover on its own with weed control,
removing burned snags to reduce organic build up/future fuel loads, and/or replanting portions of
the site.
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6.0 ADMINISTRATION AND REPORTING
A. Annual Reports, Work Plans, and PMP
Annual reports detailing all management activities and an annual financial summary are required
under the MHCP program. Additionally, the annual reports will include the results of plant and
wildlife surveys that were conducted that year. The separate gnatcatcher survey report will be
included in the appendix of the report as an attachment for the year that it was conducted. Annual
reports will be submitted to the appropriate organizations. The annual report will include
information on the extent and condition of the habitats, changes to the condition of the habitat or
species, summary of management issues/tasks, and recommendation for tasks for the upcoming
year. The annual report also will include the photographs of the site from fixed photo points, a
summary of the endowment, the funds generated and expenses incurred as well as maps that
show species locations and the vegetation communities .
The Property Analysis Record (PAR), provides the estimated cost for the implementation of this
PMP and is provided as Appendix C.
Data Management:
As needed for documenting changes to the preserve, GPS data will be recorded. A GIS coverage
will be created .
Communication and coordination:
The selected Preserve Manager will be responsible for communicating with the City HMP
Administrator. Annual reports will be provided to the City.
Budget and endowment management:
Taylor Morrison of California, LLC will be responsible for all funding requirements for this
PMP. This would include establishing a non-wasting endowment to fund the PMP. Long-term
management tasks involve activities associated with the management and maintenance of the
preserve in perpetuity as funding permits and include habitat monitoring/mapping, exotic species
control, species surveys, general management, and public outreach. The PAR includes
contingency funds to address unforeseen events. The endowment amount is required to meet the
estimated costs identified in the PAR.
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7.0 LITERATURE CITED
Beauchamp, M.R. 1986. A Flora of San Diego County, California. Sweetwater River Press,
National City, CA
Bowman, R.H. 1973. Soil Survey, San Diego Area, California, Part 1. United States Department
ofthe Agriculture. 104 pp. +appendices.
Cal-IPC (California Invasive Plant Council). 1999. The CalEPPC List: Exotic Pest Plants of
Greatest Ecological Concern in California. October. 12 pages.
Cal-IPC. 2006. California Invasive Plant Inventory
City of Carlsbad. 1999. Habitat Management Plan for Natural Communities in the City of
Carlsbad. Finalized in 2004.
City of Carlsbad. 2009. Mitigated Negative Declaration for the Muroya Project. State
Clearinghouse 2010021061.
Hickman, J.C. 1993. The Jepson Manual: Higher Plants of California. University of California
Press, Berkeley. 1,400 pp.
SANDAG (San Diego Association of Governments). 2001. Multiple Habitat Conservation Plan.
San Diego Association of Governments. 2003. Final MHCP Biological Monitoring and
Management Plan-Volume III. March.
SDG&E (San Diego Gas and Electric Company). 1995. Subregional Natural Community
Conservation Plan. Real Estate Operations Natural Resource Group,
USFWS (U.S. Fish and Wildlife Service). 1997. Coastal California Gnatcatcher (Polioptila
califomica califomica) Presence/Absence Survey Protocol. July 28.
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APPENDIX A
List of Plant Species Observed on Site
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APPENDIX A
List of Plant Species Observed on Site
ANGIOSPERMAE (DICOTYLEDONES)
ANGIOSPERMS (DICOTS)
AIZOACEAE-FIG-MARIGOLD FAMILY
*
*
Carpobrotus edulis-hottentot-fig
Mesembryanthemum crystal/inurn -crystalline iceplant
ANACARDIACEAE -SUMAC FAMILY
Malosma laurina-laurel sumac
Rhus integrifolia -lemonadeberry
AP/ACEAE-CARROT FAMILY
* Foeniculum vulgare-fennel
ARALIACEAE-GINSENG FAMILY
* Hedera helix-English ivy
ASTERACEAE-SUNFLOWER FAMILY
Ambrosia psilostachya-western ragweed
Artemisia californica-California sagebrush
Baccharis pilularis -chaparral broom, coyote brush
Baccharis salicifolia-mulefat, seep-willow, water-wally
Carduus pycnocephalus-Italian thistle
Conyza canadensis -horseweed
Heterotheca grandiflora -telegraph weed
Deinandra [=Hemizonia]fasciculata-fascicled tarweed
Encelia californica-California encelia
Gnaphalium californicum -California everlasting
/socoma menziesii ssp. menziesii-spreading goldenbush
Pluchea odorata -salt marsh fleabane
Stephanomeria virgata ssp. virgata-virgate wreath-plant
BRASSICACEAE-MUSTARD FAMILY
*
*
*
Brassica nigra-black mustard
Lobularia maritima -sweet alyssum
Raphanus sativus -radish
DUDEK A-1
5332-01
July 2011
APPENDIX A (Continued)
CACTACEAE-CACTUS FAMILY
Opuntia littoralis-coastal prickly-pear
Opuntia prolifera-coast cholla
CAPR/FOLIACEAE-HONEYSUCKLE FAMILY
Sambucus mexicana -Mexican elderberry
CARYOPHYLLACEAE-PINKFAMILY
Loejlingia squarrosa var. squarrosa-California loeflingia
CHENOPODIACEAE-GOOSEFOOT FAMILY
*
*
*
A triplex semibaccata -Australian saltbush
Chenopodium album-pigweed, lamb's quarters
Salsola tragus -Russian thistle, tumbleweed
CRASSULACEAE-STONECROP FAMILY
Dudleya edulis -ladies' fingers
Dudleya pulverulenta-chalky live-forever
ERICACEAE-HEATH FAMILY
Xylococcus bicolor-mission manzanita
EUPHORBIACEAE-SPURGEFAMILY
Chamaesyce albomarginata -rattlesnake weed
Eremocarpus setigerus -doveweed
Ricinus communis -castor bean
FABACEAE-PEA FAMILY
Lotus scoparius var. scoparius-deerweed
FAGACEAE-OAKFAMILY
Quercus agrifolia var. agrifolia -coast live oak
Quercus dumosa-Nuttall's scrub oak
Quercus engelmannii-Engelmann oak or mesa oak
HYDROPHYLLACEAE-W ATERLEAF FAMILY
Eriodictyon crassifolium var. crassifolium -thickleaf yerba santa
LAMIACEAE-MINT FAMILY
Salvia mellifera-black sage
DUDEK A-2
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July 2011 ..
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---...
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APPENDIX A (Continued)
POLYGONACEAE-BUCKWHEAT FAMILY
*
Eriogonum fasciculatum var. foliolosum -California buckwheat
Rumex crispus -curly dock
RHA~ACEAE-BUCKTHORNFANULY
Ceanothus verrucosus-wart-stemmed ceanothus
ROSACEAE-ROSE FAMILY
Adenostoma fasciculatum -chamise
Heteromeles arbutifolia -to yon, Christmas berry
SALICACEAE-WILLOW FAMILY
Salix lasiolepis -arroyo willow
SCROPHULARIACEAE-FIGWORT FAMILY
Mimulus aurantiacus -coast monkey flower, bush monkey flower
Scrophularia californica var. floribunda -California figwort
SOLANACEAE-NIGHTSHADE FANOLY
* Nicotiana glauca-tree tobacco
Solanum xanti -chaparral nightshade
ANGIOSPERMS (MONOCOTS)
LILIACEAE-LILY FAMILY
Yucca schidigera-Mohave yucca
POACEAE-GRASSFANULY
*
*
*
*
*
Avena barbata-slender wild oat
Bromus diandrus -ripgut grass
Cortaderia selloana -pampas grass
Leymus condensatus -giant wild rye
Melica imperfecta -coast range melic
Schismus barbatus -Mediterranean schismus
Vulpia myuros var. myuros-rattail fescue
* signifies introduced (non-native) species
DUDEK A-3
5332-01
July 2011
APPENDIX A (Continued)
INTENTIONALLY LEFT BLANK
DUDEK A-4
5332-01
July 2011
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APPENDIX B
Wildlife Species Observed on Site
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APPENDIX B
Wildlife Species Observed on Site
VERTEBRATES
REPTILES
IGUANIDAE-IGUANID LIZARDS
Sceloporus occidentalis -western fence lizard
BIRDS
PHASIANIDAE-PHEASANTS AND QUAILS
Callipepla californica -California quail
COLUMBIDAE-PIGEONS AND DOVES
* Columba Iivia -rock dove
TROCH/LIDAE-HUMMINGBIRDS
Calypte anna-Anna's hummingbird
PICIDAE-WOODPECKERS
Colaptes auratus -northern flicker
TYRANNIDAE-TYRANTFLYCATCHERS
Sayornis nigricans -black phoebe
Tyrannus vociferans -Cassin's kingbird
CORVIDAE-JAYS AND CROWS
Aphelocoma californica -western scrub-jay
Corvus brachyrhynchos -American crow
Corvus corax-common raven
AEGITHALIDAE-BUSHTITS
Psaltriparus minimus -bushtit
TROGLODYTIDAE-WRENS
Thryomanes bewickii-Bewick's wren
Troglodytes aedon-house wren
REGULIDAE-KINGLETS
Regulus calendula-ruby-crowned kinglet
DUDEK 8-1
5332-01
July 2011
APPENDIX 8 (Continued)
SYLVIIDAE-GNATCATCHERS
Polioptila californica-California gnatcatcher
TIMALIIDAE-LAUGHINGTHRUSH AND WRENTIT
Chamaea fasciata -wrentit
~I~IDAE-THRASHERS
Mimus polyglottos -northern mockingbird
STURNIDAE-STARLINGS
* Sturnus vulgaris-European starling
PARULIDAE-WOOD WARBLERS
Dendroica coronata -yellow-rumped warbler
E~BERIZIDAE-BUNTINGS AND SPARROWS
Chondestes grammacus -lark sparrow
Melospiza melodia-song sparrow
Pipilo crissalis -California towhee
Pipilo maculatus -spotted towhee
Zonotrichia leucophrys -white-crowned sparrow
FRINGILLIDAE-FINCHES
Carpodacus mexicanus-house finch
Carduelis psaltria-lesser goldfinch
MAMMALS
LEPORIDAE-HARES AND RABBITS
Sylvilagus bachmani -brush rabbit
SCIURIDAE-SQUIRRELS
Spermophilus beecheyi-California ground squirrel
~URIDAE-RATSANDMICE
Neotoma sp.-woodrat (midden)
Peromyscus sp. -mouse (sign)
CANIDAE-WOLVES AND FOXES
Canis latrans -coyote
DUDEK B-2
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5332-01 ..
July 2011 ...
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APPENDIX B (Continued)
WILDLIFE SPECIES -INVERTEBRATES
BUTTERFLIES AND MOTHS
PIERIDAE-WHITES AND SULFURS
Pieris rapae rapae-cabbage butterfly
Pontia sisymbrii -California white
LYCAENIDAE-BLUES, HAIRSTREAKS, AND COPPERS
Glaucopsyche lygdamus -southern blue
NYMPHALIDAE-BRUSH-FOOTED BUTTERFLIES
Junonia coenia -buckeye
Vanessa cardui-painted lady
* signifies introduced (non-native) species
DUDEK B-3
5332-01
July 2011
--
APPENDIX B (Continued) --., -
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5332-01 c DUDEK B-4 July 2011
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APPENDIX C
PAR Habitat Planning in Perpetuity
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Title:
PAR
Habitat Planning In Perpetuity
The Property Analysis Record
Muroya
Par Code: 01
Prepared by: Walsh & Hayworth
Date:
Dudek
07/26/2011
The Center for Natural Lands Management prepared this software to assist habitat conservation planners to
develop the management tasks and costs of long-term stewardship. While the sources are thought to be
reliable, the Center makes no representations about the accuracy of cost estimates. The date of the cost
information is 2007. The operation of the program is not guaranteed by the Center. Management requirements
are determined by the user. Users should consult with their own financial advisors before relying on the results
of their analysis.
Property Analysis Record 3 ·Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Section 1 -Property I nformatidn
Property Title: Muroya
Location/ Jurisdiction Carlsbad
County
Address
City, State, Zip
Conserved Acres
Management type
Date Created
Prepared for
Prepared by
San Diego
Black Rail Road
Carlsbad, CA 92011
8.5
Conservation Easement
04/04/2011 09:22:12 AM
Taylor Morrison
Walsh & Hayworth
Dudek
Project Management Information
Contact
Company TBD
Address
City, State, Zip
Phone
Fax
E-Mail address
Cost Year
Date of site visit:
Development Project
2012
Project Name Muroya
Total Project Acres 20
Stage of planning Permitting
Notes
PAR ID: 01 Last Modified: 07/26/2011
Developer/Proponent Information
Contact April Tornillo
Company Taylor Morrison of CA, LLC
Address 15 cushing
City, State, Zip Irvine, CA 92618
Phone 949-341-1200
Fax 949-341-1400
E-Mail address Atornillo@taylormorrison.com
Assumed at this time the HOA will contract long-term lands managment with qualified entity.
Property Analysis Record 3 • Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
07/26/2011 Sect.1 Page 1
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Section 2-Division of Responsibility
Property Title: Muroya
Description: Responsible Party:
Biological Surveys Manager
Debris Removal Manager
Erosion Control Project
Fence Maintenance Association
Fire ZonefBuffer Management Association
Habitat Assessment Manager
Habitat Restoration Project
Maintenance. Road Association
Monitoring, Plant Manager
Monitoring, Wildlife Manager
Non-native plant removal -Initial Project
Non-native plant removal -Ongoing Manager
Patrolling Manager
Plant Surveys Manager
Signs, Access Control Manager
Wildlife Surveys Manager
PAR 10:01 07/26/2011
Notes:
Preserve manager to perform surveys as outlined in
PAR for areas within preserve boundary.
Reserve Manager responsible for removing trash within
preserve boundaries.
Project proponent to control erosion until project N.O.T.
filed with RWQCB.
HOA/Homeowner responsibility. HOA If on common
areas and property owner if on private residential lot.
HOA responsibility. FMZ is not located within Preserve
area.
Manager to perform assessment during long term
management for areas within preserve.
Proponent to implement habitat restoration/mitigation
as outlined in Conceptual Mitigation Plan and monitor
for five years before being assumed by the Manager .
Preserve manager to perform as outlined in PAR for
areas within preserve boundary.
Preserve manager to perfrom as outlined in PAR for
areas within preserve boundary .
Preserve manager to perform as outlined in PAR for
areas within preserve boundary.
Preserve manager to perform as outllend In PAR for
areas within preserve boundary.
Preserve manager to perform as outlined in PAR for
areas within preserve boundary.
Preserve manager to perform as outlined in PAR for
areas within preserve boundary.
Preserve Manager to provide signs at boundary of
preserve.
Preserve manager to parfrom as outliend in PAR for
areas within preserve boundary .
Property Analysis Record 3-Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect.2 Page 1
i:
-;
Section 5 -Purpose of Preser-Vation
Property Title: Muroya PAR ID: 01 07/26/2011
Purpose of Preservation Prioritize Goals and Objectives
Open Space
Other
Wildlife Corridor
5 Contribute to regional Carlsbad HMP.
8
7
Habitat preserve for various vegetation communities, sensitive plant
species and wildlife species.
Stepping stone linkage connecting core areas 4, 6, and 8.
Generally assisting movement of gnatcatcher and other avian
species.
Property Analysis Record 3-Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect.5 Page 1
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• Section 6-Site Conditions
,.. Property Title: Muroya PAR ID: 01 07/26/2011
IIIII Permitted/ Future
Fire/Fuel Management Legal Permitted Problem Location Notes
Fuel Management Zones . Yes No . Low Adjacent FMZ exist adjacent to open preserve
area-generally on slopes between
residences and open space preserve. FMZ
is HOA responsibility.
Permitted/ Future
Structures Legal Permitted Problem Location Notes
Power or Utility Lines No No Low Adjacent SDGE easement is located adjacent to
preservation area, along northern boundary.
SDG&E easement managed under
SDG&E's NCCP.
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Property Analysis Record 3-Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect.6 Page 1
.,
Section 7 -Land Use
Property Title: Muroya
Future
Adjacent Land Use Permitted Permitted Problem
Minor Roads Yes No Low
Residential -High Density Yes No Low
Location
North
North
PAR ID: 01 07/26/2011
Notes
Residential streets and collector roads adjacent to
Preserve.
Preserve surrounded on three sides by residential
development and buffered by fuel modification zone.
FMZ to be maintained for invasive species and weeds
by HOA.
--------------------------------------------------------------------------~-'
Property Analysis Record 3 -Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect.7 Page 1
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Section 8 -Biological Assessment
Property Title: Muroya PAR ID: 01 07/26/2011
ANIMALS
Common Name:
Scientific Name:
BIRDS
California Gnatcatcher
(Poliopfl'la catifornica)
Ranking:
Status:
Global: G3
Acreage: Individual: Notes:
National: N1 State: S2
2 pairs
Property Analysis Record 3 -Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect.8 Page 1
Section 8 -Biological Assessment
Property Title: Muroya PAR ID: 01
INVASIVE/EXOTIC
Common Name: Ranking:
Scientific Name: Status: Acreage: Individual: Notes:
FLOWERING PLANTS
Australian Saltbush Global: GNR National: NNA State: SNA
(Atrlplex semibaccata)
Baby Sun-rose Global: G5 National: NNA State: SNA
(Carpobrotus chllensls)
Black Mustard Global: GNR National: NNA State: SNA
(Brassica nigra)
Castor-bean Global: GNR National: NNA State: SNA
(Ricinus communis)
Common lceplant Global: GNR National: NNA State: SNA
(Mesembryanthemum crystallinum)
Curly Dock Global: GNR National: NNA State: SNA
(Rumex crispus)
English Ivy Global: GNR National: NNA State: SNA
(Hedera helix)
Garden Radish Global: GNR National: NNA State: SNA
(Raphanus sativus)
Great Brome Global: G5 National: NNA State: SNA
(Bromus diandrus)
Italian Thistle Global: GNR National: NNA State: SNA
(Carduus pycnocephalus)
Slender Oat Global: GNR National: NNA State: SNA
(Avena barbata)
Sweet Fennel Global: GNR National: NNA State: SNA
(Foeniculum vulgare)
Tree Tobacco Global: GNR National: NNA State: SNA
(Nicotiana glauca)
White Goosefoot Global: G5 National: N5 State: SNR
(Chenopodium album)
Property Analysis Record 3 -Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
07/26/2011
Sect.S Page 2
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... Section 8 -Biological Assessment
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Property Title: Muroya PAR ID: 01 07/26/2011
NATURAL COMMUNITIES
Common Name: Ranking:
Scientific Name: Status: Acreage: Individual: Notes:
CALIFORNIA
California Sagebrush I Giant Wildrye Global: G3 National: 0.19 State: Monotypic stand of Leymus condensatus
(Artemisia californica I Leymus condensatus 0.19 associated with drainage.
Common Chamise Shrubland Global: G5 National: 5.36 State: Approx 4.64 acres of Southern Maritime
(Adenostoma fasciculatum Shrubfand) 5.36 Chaparral and 0. 72 acre of Southern Mixed
Chaparral.
Coyotebrush -California Sagebrush Shrubland Global: G5 National: 2.03 State: Mapped as coastal sage scrub.
(Baccharis pilu/aris -Artemisia californica 2.03
Property Analysis Record 3-Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect.8 Page 3
_,
Section 8 -Biological Assessment
Property Title: Muroya PAR 10:01
PLANTS
Common Name: Ranking:
Scientific Name: Status: Acreage: Individual: Notes:
FLOWERING PLANTS
California Adolphia Global: G3 National: N3 State: S3.1
(Adolphia ca/ifornica) 3
California Scrub Oak Global: G1 National: N1 State: S1.1
(Quercus dumosa) 16
Engelmann Oak Global: G3 National: N3 State: S3.2 Large specimen
(Quercus engelmannii)
Warty-stem Ceanothus Global: G3 National: N2 State: S2.2
(Ceanothus verrucosus) 14
Property Analysis Record 3 ·Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
07/26/2011
Sect.8 Page 4
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... Section 14-Initial & Capital Tasks and Costs
Property Title: Muroya PAR JD: 01 07/26/2011
Ill Task Specific Cost I Annual Times Cont Total
List Description Unit Quantity Unit Cost Years % Cost
ACQUISITION
Legal Assistance Prepare/review Documents C. Hours 16.00 150.00 2,400.00 1.0 10.0 2,640.00
Sub-Total 2,640.00
REPORTING
Management Plan Initial Report L. Hours 8.00 55.50 444.00 1.0 10.0 488.40
Sub-Total 488.4& 1111 s"Ut>iotal--------------------------------------·· -·· ----------------------------------------3.1 is~4o
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Administration
Total
Property Analysis Record 3-Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
750.81
3,879.21
Sect.14 Page 1
Section 15-Ongoing Tasks and Costs
Property Title: Muroya
Task Specific
List Description Unit
BIOTIC SURVEYS
Plant Ecologist Field Survey L. Hours
Preserve Veg Once Every 10 Yrs L. Hours
Project Management Manage Project And Staff L. Hours
Qualitative Monitoring Annual L. Hours
Wildlife Biologist Field Survey L. Hours
Number Cost/
of Units Unit
8.00 110.00
8.00 110.00
4.00 110.00
2.00 110.00
15.00 110.00
PAR 10:01 07/26/2011
Annual Years Cont Total
Cost Divide % Cost
880.00 5.0 10.0 193.60
880.00 10.0 10.0 96.80
440.00 1.0 10.0 484.00
220.00 1.0 10.0 242.00
1,650.00 3.0. 10.0 605.00 ---------------------------------------------------------------------------------------------Sub-Total 1 ,621.4.9
GENERAL MAINTENANCE
Dump Fees Dump Fee Item 4.00 40.00 160.00 1.0 10.0 176.00
General Maintenance Qrtrly L. Hours 32.00 59.50 1 ,904.00 1.0 10.0 2,094.40 ---------------------------------------------------------------------------------------------Sub-Total 2,270.40
OPERATIONS
Budgeting
Contracts
Sub-Total
PUBLIC SERVICES
Patrolling
Sign, Aluminum
Sub-Total
REPORTING
Administrative
Agency Report
Annual Work Plan
Monitoring Reports
Photodocumentation
Report Production
Budget & Reconcile
Produce Contracts
Patrol
Aluminum 14" X 20"
Operations
Annual Report
Plan And Par Budget
L. Hours
L. Hours
L. Hours
Each
L. Hours
L. Hours
L. Hours
Monitoring Documentation L. Hours
Field Survey L. Hours
Labor L. Hours
4.00
4.00
2.00
15.00
4.00
16.00
4.00
8.00
4.00
3.00
55.50
59.50
40.00
24.20
55.50
55.50
55.50
55.50
55.50
55.50
222.00 1.0 10.0
238.00 5.0 10.0
80.00
363.00
222.00
888.00
222.00
444.00
222.00
1.0 10.0
1.0 10.0
1.0 10.0
1.0 10.0
1.0 10.0
1.0 10.0
1.0 10.0
244.20
52.36
296.56
88.00
399.30
487.30
244.20
976.80
244.20
488.40
244.20
166.50 1.0 10.0 183.15
Revise Hmp 5 Year Update Hour 12.00 55.50 666.00 5.0 10.0 146.52 ---------------------------------------------------------------------------------------------Sub-Total 2,527.47
Subtotal
Administration
Total
Property Analysis Record 3-Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
7,203.13
1,728.75
8.931.88
Sect. 15 Page 1
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,.Section 16 -Financial Summary
•Property Title: Muroya
,,,.Jst Budget Year: 2016 State: CA
,,nitial & Capital Ft'nancial Requirements
Revenues
Management Costs
..-. Contingency Expense
IIIIIIAmtual Ongoing Financial Requirements
1111 Revenues
Ongoing Costs
,.. Contingency Expense
,.,Endowment per acre $26,270
~tewardship costs are based on4.00% of Endowment Earnings per Year
Ongoing managementfumling per year is $8,932
• II
Re~·ulting in a per acre per year cost of $1,051
PAR Code: OJ
Property Analysis Record 3 -Version 1.03 {C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Date: 07/26/2011
$0
$2,844
$284
$0
$6,548
$655
Sect.16 Page 1
Section 17: Labor Summary
Property Title: Muroya
Initial & Capital
Position Description
Project Manager
Preserve Manager
Biologist
Area Manager
Ranger
Total
Hours Cost
0.00 0.00
8.00 444.00
0.00 0.00
0.00 0.00
0.00 0.00
8.00 444.00
Hours
12.00
62.00
10.00
32.00
2.00
118.00
PAR 10:01 07/26/2011
Ongoing Total
Cost Hours Cost
223.60 12.00 223.60
3,376.50 70.00 3,820.50
308.00 10.00 308.00
1,904.00 32.00 1,904.00
80.00 2.00 80.00
5,892.10 126.00 6,336.10
Property Analysis Record 3 -Version 1.03 (C) 1999-2008 Center for Natural Lands Management
www.cnlm.org
Sect. 17, Page 1
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