656, Construct a new SFR requirerin, Studies & Reports•
HORTICULTURAL RESOURCE REPORT
Prepared for
Dr. Robert Marshall
17 Portuguese Bend Road
Rolling Hills, California 90274
Prepared By
ig))
Robert h. McMahon, Jr.
Horticulturist
Landscape Architect
March 13, 1996
Robert J. McMahon. Horticultural smices. r 16 1;2 Sixth Street. Seal Beach. California. 90740, (310) 493-0186
CONTENTS Pale
I. Project Description 1.
H. Scope of the Horticultural Report 1.
III. Setting 2.
IV. Impacts
A. On -Site Impacts
B. Off -Site, Cumulative Impacts
2.
V. Mitigation 3.
VI. Remarks on Plant Regrowth, Fire Clearances 4.
and Habitat Maintenance
List of Figures:
EXHIBIT.1 Proposed Development Plan
EXHIBIT 2 Existing Conditions Plan
EXHIBIT 3 Relocated Stable Plan
EXHIBIT 4 Los Angeles County Fire Department
Brush Clearance Requirements
Appendices Containing:,
Plant Species List
Resumes of Project Horticulturist/Landscape Architect
• •
I. Project Description
The subject property hereafter also referred to as the site; is located at 17 Portuguese
Bend Road in the City of Rolling Hills, Los Angeles County, California. The site consists
of 5.39 acres of residentially zoned land with one single family residence, with lawn,
gardens„ ornamental trees, and shrubs, driveway, walkways, swimming pool, and patio.
The some acreage in the study area is covered by native coastal sage scrub and chaparral
vegetation.
The owner Dr. Robert W. Marshall is applying for a permit to subdivide the site for one
additional single-family residence. The proposed 2-lot subdivision of land at Lot 79-RH,
and currently, 17 Portuguese Bend Road, Rolling Hills, CA, an existing lot that has one
residential unit, to be implemented by Dr. Robert W. Marshall. Lot 79-RH consists of
5.39 acres gross to be divided into two parcels as follows: Parcel 1-2.896 acres gross,
2.242 acres net; and Parcel 2 - 2.520 acres gross, 2.046 acres net (Exhibit 1).
II. Scope of the Horticultural Report
The applicant Dr. Robert W. Marshall has contracted Robert J. McMahon a horticulturist
and landscape architect to prepare a report for submission to the Rolling Hills Planning
Commission that includes the following:
• Identification of native plants on the site.
• Identification of wildlife utilizing native habitat on the site.
Evaluation of the relationship of the site to wildlife habitat currently existing in the
City of Rolling Hills (i.e. an estimation of the ecological importance of the site)
• Evaluation of impacts on wildlife on the site and in the City of Rolling Hills as a result
of implementation of the proposed project (i.e. an estimation of direct and cumulative
impacts on wildlife).
• Recommended mitigation, if necessary, emphasizing low cost and low maintenance
measures, such as revegetation.
• Evaluation of the County Fire Department regulations with respect to habitat
maintenance and respective impacts on wildlife on the site.
Horticultural Resource Report
III Setting
March 13, 1996
Page 2
The subject property area, with predominantly west facing slopes, ranging in elevation
from about 500 to 600 feet, is centrally located within the City of Rolling Hills (Exhibit 2).
Almost the entire area within the City limits of Rolling Hills has undergone severe habitat
alterations (i.e. clearing, grading, exotic landscaping) commonly associated with suburban
developments in Southern California. Most of the developments are hillside and hilltop, 1
to 5-acre homesteads, such as those currently surrounding the subject property.
Very little (perhaps less than 10 percent) of the original coastal sage scrub and chaparral
vegetation remains within the City limits (much of it has been removed prior to 1930, as a
result of fanning and cattle ranching), and whatever native habitat still exists, is isolated on
steep, unstable slopes bordering in intermittent streams. Exotic planting (of blue gum,
pepper tree, olive, pine) trees now dominate the landscape. In this regard, the suburban
setting of the subject property is rather typical for Rolling Hills.
About (50) fifty percent of the site is covered by a heterogeneous assemblage of native
vegetation, growing in an isolated stand, largely undisturbed, in loose, clay -sediment soils
on west facing slopes, the dominant shrubs are coastal sage, Lemonade berry and elements
of moist chaparral are found on the lower slopes. This relatively large proportion of
native shrubs, combined with its high visibility from a adjacent neighbors seems to enhance
the uniqueness of the site.
IV. Impacts
A: On -site impact
Implementation of the proposed project will result in the destruction of no native
vegetation. Only trimming (i.e. "lollipopping" and checker boarding") to comply with fire
regulations Lemonade berry, purple sage, California sage, and buckwheat will be the
principal native vegetational elements. Dominant plant species should remain intact and
viable retaining the native vegetation on the site and only thinning 38 areas of the entire
5.39 acres will not disturb the existing wildlife habitat (Exhibit 1).
The proposed Lot 2.52 acres will result in the thinning of only .38 acres of the acres of the
site. The areas in which the thinning will occur is depicted on Exhibit 1. South Bay
Engineering, which is familiar with grading projects in the City, regarding whether grading
would occur beyond the proposed pads. They confirm that there would be no need to go
beyond the boundary of the proposed pads during grading.
•
Horticultural Resource Report
March 13, 1996
Page 3
Depending on the size and location of the residence on the pad no brush would need to be
removed.
The area of brush that will not be affected by the project is depicted in (Exhibit 1).
Without the proposed lot the existing stable structure would remain, resulting in the
removal of .06 acres and thinning of .60 acres of brush which will adversely effect wildlife
habitat. (Exhibit 2)
The Proposed stable location on the existing lot will have no adverse effects on the
wildlife, due to no brush within the surrounding area will be cleared or thinned (Exhibit 3).
B: Off -site, cumulative impacts
In view of widespread habitat destruction in Rolling Hills, loss of any coastal sage scrub
and chaparral is ecologically insignificant. Natural 'communities in this region are highly
fragmented and could scarcely be considered integrated components of a natural
ecosystem.
Locally, within a few hundred yards of the site, there are patches of coastal sage and
riparian vegetation on the east facing slopes along with a significant patch of baren soil.
This baren soil area will erode, during heavy rains causing slope failures. It is not
recommended to remove the native vegetation in this measure. (refer to City of Rolling
Hilts Fire Department brush clearance maintenance Exhibit 4.)
V Mitigation
Implementation of the proposed project will result in no disturbance of native vegetation
on the site (see Exhibit 1). Although presumed impacts to biotic resources, both on and
off -site, are herein judged to be overall insignificant, to the extent mitigation measures are
implemented, they can be accomplished in the form of revegetation of previously cleared
areas. The end result of this proposal will be no net loss of native habitat. In connection
with habitat restoration and maintenance, the following measures of mitigation are
suggested.
• No developments shall be permitted outside the footprints and fire clearances of
proposed buildings, roadways and easements shown on the approved site plan, without
further review by the Rolling Hills City Planning Commission.
• Fire clearances shall be limited to minimum distances allowable by City regulations.
• No new trails or access roads shall be created except as designated on the approved
subdivision map and site plan.
• •
Horticultural Resource Report
March 13, 1996
Page 4
• No new trails or access roads shall be created except as designated on the approved
subdivision map and site plan.
• No chemicals (i.e. fertilizers, pesticides, herbicides, detergents, drain oil) shall be used
or disposed of within the streambed or adjacent watershed where they might leach into
the natural drainage system.
• Revegetation shall be done predominantly with plants native to Southern California, or
of the Southwestern united States, and of the drought -resistant type. We recommend
widespread initial plantings, about five feet apart, from 1-2 gallon containers of low,
relatively fast-growing shrubs (i.e. buckwheat, purple sage, California sage). Slower
growing shrubs (i.e. lemonade berry, toyon, elderberry), from 5 or 10-gallon
containers, can be interspersed with the mentioned species.
• Prior to revegetation, we recommend consultation with an authority on landscaping
with native plants.
VI Remarks on plant regrowth, fire clearances and habitat maintenance
Any number of revegetation schemes may be used on the subject property. Depending on
the availability of plantings, water, and care, complete revegetation of cleared areas can
occur in five to ten years. Existing native plants will recognize without assistance, going
through successional stages (i.e. grasses, herbs, fast growing shrubs, slower -growing,
larger shrubs) and eventually (perhaps ten years) entirely reclaim the clearings. Natural
recolonization of native vegetation is relatively slow, but can be accelerate dramatically by
an aggressive native plant recovery program.
Fire clearances required by the City and fire department from buildings are generally
required to be 130 linear feet (measu'red horizontally from the edge of the building) (see
Exhibit 4).
We have confirmed with the County of Los Angeles Fire Captain Colmerauer that the fire
department requires a clear area of 30 feet from a structure. Another 100 feet from the
structure may be thinned by techniques known as "checker boarding" or "lollypopping,"
which are depicted in (Exhibit 4). These techniques do not result in a complete loss of
habitat.
Captain Colmerauer confirmed that the clearance and thinning areas are measured from
the structure and not from the edge of the pad. He confirmed that the method we used to
measure the areas that would be affected is correct.
Consequently, recommend plantings of native lemonade berry, a hearty, low fire -risk
shrub, which can help maintain the integrity of the natural community on the site.
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015.1. I CLEARANCE REQUIREMENT
Thousands of homes ar. . serious d>..,ger of destruction by fire because 4. . e .y to brush -covered
areas. Homes with wood shake roofs, wood siding, decks, patio covers or exposed eaves are particularly
vulnerable to the spread of fire. Despite efforts by firefighters, wildland fires fanned by strong winds, can
destroy homes. It b your legal responsibility to take the necessary adions to dear vegetation around any given
structures. A firesafe landscape creates a defensible space to help protect against approaching wildfires.
1. All flammable vegetation identified as a fire hazard by the inspecting officer shall be mowed or cut
to a stubble height of 3 inches, for 30 feet around any structure or 50 feet in high hazard areas.
2. Create a firebreak for the next 70 feet, for a total of 100 feet, around any structure by clearing,
trimming. thinning, cutting back and removing flammable vegetation. For high hazard areas, this
distance can be increased to a maximum of 200 feet.
3. Single specimens of trees, ornamental shrubbery, or ground covers are permissible. provided that they
do not form a means of transmitting fire to any structure. Such specimens shall be spaced a minimum
of 15 feet or 3 times their diameter from other specimens, structures or surrounding native brush.
4. All trees and shrubs shall be maintained free of dead wood and litter. Trees and shrubs shall be
trimmed up from the ground 1/3 of their height.
5. Access roads shall be maintained with a minimum of 10 feet brush clearance on each side. Trees and
shrubs overhanging roadways shall be trimmed to a minimum of 16 feet vertical clearance.
6. Provide a minimum 3 feet clearance around all lire hydrants.
All plants will burn under extreme fire weather conditions. Fire resistant plants burn at a relatively low intensity,
slow rates of spread and with short flame lengths. To best protect your home from fire, it is recommended that fire
resistant plants are used when landscaping. A list of these plants can be obtained through the Los Angeles County
Fire Department, Forestry Division, telephone number: (213) 881 - 2481
BRUSH CLEARANCE MAINTENANCE IS A YEAR-ROUND RESPONSIBILITY
REMEMBER: EXTRA HAZARDOUS AREAS MAY REQUIRE 200 FEET OF CLEARANCE
NOTE: Care should be taken when reducing the amount of fuel cover on slopes so as not to create an
erosion problem.
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CHECKBOARDING
CHECKBOARDING IS A TERM TO DESCRIBE ONE FORM OF FUEL
MODIFICATION. IT SERVES TO REDUCE FUEL LOAD AND CONTINUITY
WHILE PREVENTING EROSION, LOSS OF WILDLIFE HABITAT, AND
RETAINS VIEWING ESTHETICS. THE DRAWINGS BELOW DEPICT AN
AERIAL VIEW OF A SLOPE BEFORE AND AFTER CHECKBOARDING.
DIMENSION "A" SHOULD BE THREE TIMES THE DIAMETER OF THE PLANT
CROWNS. CHECKBOARDING IS USUALLY COMBINED WITH
LOLLYPOPPING.
BEFORE
**or***
AFTER
*****
0 0
�P.
LOLLYPOPPING
MOST BUSHES AND SOME TREES IF ALLOWED TO GROW UNATTENDED
WILL DEVELOP THE SHAPE SHOWN IN FIGURE A. WHEN THIS HAPPENS,
DEAD MATERIAL, WILL START ACCUMULATING IN AND UNDER THEM
AND CREATE A FIRE HAZARD. TO INCREASE FIRE SAFETY, THESE
PLANTS NEED TO BE "LOLLYPOPPED". IN OTHER WORDS, THE PLANT
NEEDS TO BE THINNED AND THE LOWER BRANCHES REMOVED. THIS
SERVES TWO PURPOSES IN THAT THE FUEL LOAD IS DECREASED AND
THE FUTURE ABILITY TO REMOVE FUEL FROM UNDER THE PLANT IS
MADE EASIER.
FUEL REDUCTION IS AN IMPORTANT ASPECT OF WILDLAND FIRE
SAFETY BUT TT MUST BE BALANCED WITH EROSION CONTROL. BY
LOLLYPOPPING SHRUBS AND TREES WE REDUCE THE FUEL LOAD BUT
RETAIN THE ROOTS FOR SLOPE CONTROL. THE CANOPY FOR ENERGY
ABSORPTION OF RAIN AND THE PLANT ITSELF FOR ESTHETICS AND
ANIMAL HABITAT.
4
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PLAN I rc.t.ica
OFL .tAL COMPENDIUM
•
LEGEND
HABITAT
CSS : Coastal Sege Scrub
CH : Chaparral
AG : Annual Grassland (Disturbed, Weedy areas)
ABUNDANCE
e - abundant - ubiquitous throughout the noted community; occurs in
high numbers or In large, pure strands
c - common - e dominant species In the noted community; occurs in
relatively high numbers
f - frequent - occurs in moderate numbers, but not a dominant element
of the noted community
o - occasional - occurs sporadically in the noted community; generally
not an obvious or conspicuous component
I - , Infrequent - occurs rarely, or only In a small portion of the noted
community; often not apparent unless searched for
STATUS
" Non-native
'IILAR PLANTS
•
' FILICAE
ASPIDIACEAE - WOOD FERN FAMILY CSS CH AS
D, 'opteris elute
coostol wood fern - 1
CONIFERAE
PINACEAE - PINE FAMILY
• Pints cenen'ensrs
Canary island pine 1 1
• Pinus pinester
Cluster pine 1 1
4111
ANSIOSPERMAE (DICOTYLEDONES)
AIIATANTHACEAE - AMARANTH FAMILY
Ameren(Aus Dlltnides
prostrate amaranth 1 1 e
ANACARDIACEAE - SUMAC FAMILY
Ilolosme leurine
laurel sumac 1' o
Rhos Inte rifolle
Iemonodeberry o a
• Solinus molls
Peruvian pepper -tree 1 1
• Schinus t tbinthifclius
Brazilian pepper -tree - 1
APIACEAE - CARROT FAMILY
•
•
•
• Conium meculelum
poison - hemlock o o -
Deucus pus/llus
rattlesnake weed o 0 1
• foeniculum ►avlgere
sweet fennel 0 0 0
ASCLEPIAOACEAE ' IOW, .0 FAMILY
•
Asclepie.$ fssc'cvlens
narrow -leaved milkweed I 1
ASTERACEAE - SUNFLOWER FAMILY
Ariemisis cell/arnica
. coastal sagebrush c
Artemisle Orecrmnrilus
tarragon
Beccheris piluIeris
coyotebush
• C/rsium Wore
bull thistle
• Cnny: a caned?nsi
horseweed 1
Corethrogyne !/leginitoiie
cudweed ester • o
&cella cell/cynics
California bush sunflower
6frephel unt D/color
bicolored cudweed o
6hephe//um celifornictan
California everlasting o
ensonellum CenescenSSsp. micrccephelum
white everlasting o
Hellenthus em%
common sunflower
• [ octucs serriole
prickly lettuce 1
I'telecolhrix satellite
cliff melecothrlx
• Picris echio/des
bristly ox-tongue 1
• Scnrlius ever
prickly sow -thistle
Stephenomerlo virge/e
twiggy wreethplent 1
• Torexecten elic/ene/0
common dandelion -
ORASSICACEAE - MUSTARD FAMILY
0
0
0
0
0
1
1
1
• Bress/ce gen/cvlete
short -podded mustard o i o
• lires$Fce Mrs di
black mustard
• RsjAOAu' Jet ivut
Wild reddish
CACTACEAE - CACTUS FAMILY
• Mantis ficus-indice
Indian fig
°pantie lit torelis
coastal prickly peer
CAPRIFOLIACEAE - HONEYSUCKLE FAMILY
1
i
1
•
41.
• [muter, Japonica
Japanese honeysuckle - 1
SemPucus mexirene
Mexican elderberry o
CHENOPODIACEAE - 600SEFOOT FAMILY
• Chennpodium elDurn
lemb's-quarters
CONVOLVULACEAE - MORNING-GLORY FAMILY
Celystegieme ernstegie
Western bindweed
• Ipomnee purpuree
common morning-glory
1
•
1 - 1
0 0
Mir
CURCURBITACEAE - 6ORD FAMILY
Curcurtite /oetedissime
coyote -melon 1 i
Mere/I merrocerpus
wild cucumber o
EUPHOR6IACEAE - SPURGE FAMILY
ChemersyreelDn marginate
rattlesnake spurge
Eremocerpus setigervs
Ooveweed - - o
• Riclnus communis
castor -been 1 i
FAOACEAE - PEA rAPUL
• Arms /onginVie
Sydney golden wattle
upmusspp.
lupine
• finocesPo polymorrAe
bur -clover
• Me/i/olo% indigo'
yellow sweet -clover
• Spertium JenCPum
Spanish broom
• V/cie Sel/ve
Spring vetch
6ERANIACEAE - 6ERANIUM FAMILY
• Eroolum cicuterium
• red -stemmed fileree
HYOROPHYLLACEAE - WATERLEAF FAMILY
Evcrote chrysontMen ilnlie
common eucrypte
LAMIACEAE - MINT FAMILY
1 1 0
•
• tferrultium Kilgore
horehound 0 0 0
Se/vie leuciylle
purple sage c f
MALVACEAE - MALLOW FAMILY
• Neive NM flora
cheeseweed
MYOPORACEAE - MYOPORUM FAMILY
• tfyc'pnrvm lee t urn
myoporum - 1
•
MYRTACEAE - MYRTLE FAMILY
• E.ICOlytus g/ofuluS
blue gum
• Er/<e/y(!rss <0rn0/dl.'/0ncic
rod gum
OIEACEAE - OLIVE FAMILY
• 'minus sp
ash
• - Oleo europeee
olive
ONAGRACEAE - EVENING -PRIMROSE FAMILY
f piht um conum
California fuchsia
OXALIDACEAE - WOOD -SORREL FAMILY
• O e l i spe: l epree
Bermuda Du 1ercuo
PITTOSPORACEAE - PITTOSPORUM FAMILY
IND
POLYGOHACEAE - BUCKWHEAT FAMILY
Enegonom ciner"um
ashy -leaved buckwheat c o
• P /ygonum ertreslrum
common knotweet7 -
• ,Cum9X crispin •
ROSACEAE - ROSE FAMILY
c c r.
RUBIACEAE - MADDER FAMILY
Ce/fu-n any;: tilolwur+
rimer,.'-1e vet be4cfre.�
f1
•
41,
110
Robert J. McMahon, Jr.
Landscape Architect, Lic. 3463
1161 6th Street
Seal Beach, CA 90740
310.493.0186
Professional Experience
Mr. McMahon's project experience extends from California to Japan and Southeast Asia. Having spent nine years working
with an international landscape architectural and planning firm, Mr. McMahon has had the opportunity to worn on a variety of
project types covering conceptual design development to contraction otiservation — creating a strong multi-ciscipined
background.
Licensed to practice landscape architecture in the state of California, Mr. McMahon's design management expertise
includes a host of assignments ranging from illustrative renderings to graphic design computer system application.
In his professional capacity as Project Manager with Perican, Mr. McMahon has directed design efforts on the following
projects both locally and internationally.
southern California
Residential Bel Air Crest —Bel Air, California
The Enclave — Calabasas, California
Commensal Warner Gateway, Warner Center
Santa Ma Auto Mall, Santa Ma .
Resort The Ritz Carlton Hotel Marina Del Rey — Marina Del Rey, California
The Ritz Carlton Hotel Mauna Lani — Mauna Lani, Hawaii
Government The Arrny Corps of Engineers — Santa Ana River Mainstream Recreational Land Use Channel
Simi Valley Recreation and Park District — Rancho Tapo/Rancho Madera Community Parks
International
Residential Pinegate Development — Tokyo, Japan
Pandan Gardens Condominium Complex Competition — Singapore
Recreational Minami Nagano Sports Park — Nagano, Japan
(1998 Winter Olympics Stadium Site)
Tottori Flower Park Competition — Tottori, Japan
Zhaoging Gotf and Resort Community — Zhaoging, China
Mixed -Use Nishi Umeda Redevelopment Project and Ritz Carlton Hotel Osaka — Osaka, Japan
Education
1982-1986 Bachelor of Landscape Architecture — State University of New York at Syracuse. Off campus thesis,
Spring 1985 'Cafes of Venice' Venice, Italy
1980-1982 Applied Associate Silence in Ornamental Horticulture at Community College of the Finger Lakes
Professional Affiliations
American Society of Landscape Architecture, ASLA
Horticulture Society
Alumni Association at Syracuse University