HomeMy WebLinkAboutCC Reso 2018-046 PA 2016-113 (MSHCP) RESOLUTION NO. 2018-046
A RESOLUTION OF THE CITY COUNCIL OF THE CITY OF LAKE ELSINORE,
CALIFORNIA, FINDING THAT PLANNING APPLICATION NO. 2016-113
(CONDITIONAL USE PERMIT NO. 2017-03 AND INDUSTRIAL DESIGN REVIEW
NO. 2016-03) IS CONSISTENT WITH THE WESTERN RIVERSIDE COUNTY
MULTIPLE SPECIES HABITAT CONSERVATION PLAN (MSHCP)
Whereas, Chris Mulvania, Tige Watersports has filed an application with the City of Lake Elsinore
(City) requesting approval of Planning Application No. 2016-113 (Conditional Use Permit No.
2017-03 and Industrial Design Review No. 2016-03) for the development of the Tige Watersports
project (Project) to establish a boat sales, service, and assembly facility that involves the
construction of a 25,682 sq. ft. building and a 9,800 sq.ft. storage building with 66 parking spaces,
44,142 sq. ft. paved area, and 18,469 sq. ft. landscaped area on an approximately 2.78-acre lot.
The Project site is located on a currently vacant site, on the northwesterly side of Riverside Drive
and southwesterly of Collier Avenue. (APN: 378-030-031); and,
Whereas, Section 6.0 of the Multiple Species Habitat Conservation Plan (MSHCP) requires that
all discretionary projects within a MSHCP Criteria Cell undergo the Lake Elsinore Acquisition
Process (LEAP) and the Joint Project Review (JPR) to analyze the scope of the proposed
development and establish a building envelope that is consistent with the MSHCP Criteria Cell;
and,
Whereas, Section 6.0 of the MSHCP further requires that the City adopt consistency findings
demonstrating that the proposed discretionary entitlement complies with the MSHCP Criteria Cell,
and the MSHCP goals and objectives; and,
Whereas, the Project site is within the MSHCP Elsinore Area Plan, Subunit 3 (Elsinore). The
proposed project site lies within Criteria Cell #4266; and,
Whereas, pursuant to Chapter 17.168 (Conditional Use Permits) and Chapter 17.184 (Design
Review) of the Lake Elsinore Municipal Code (LEMC), the Planning Commission (Commission)
has been delegated with the responsibility of making recommendations to the City Council
(Council) pertaining to tentative maps and design reviews; and,
Whereas, on March 6, 2018 at a duly noticed Public Hearing the Commission has considered
evidence presented by the Community Development Department and other interested parties with
respect to this item; and,
Whereas, pursuant to Chapters 17.168 and 17.184 of the LEMC, the Council has the
responsibility of making decisions to approve, modify, or disapprove recommendations of the
Commission for conditional use permits and design review applications; and,
Whereas, on March 27, 2018, at a duly noticed Public Meeting, the Council has considered the
recommendation of the Commission as well as evidence presented by the Community
Development Department and other interested parties with respect to this item.
NOW THEREFORE, THE CITY COUNCIL OF THE CITY OF LAKE ELSINORE DOES HEREBY
RESOLVE, DETERMINE AND ORDER AS FOLLOWS:
CC Reso. No. 2018-046
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Section 1: The Council has considered the Project and its consistency with the MSHCP prior to
adopting Findings of Consistency with the MSHCP.
Section 2: That in accordance with the MSHCP, the Council makes the following findings for
MSHCP consistency:
1. The Project is a project under the City's MSHCP Resolution, and the City must make an
MSHCP Consistency finding before approval.
The Project is located within an MSHCP Criteria Cell. Pursuant to the City's MSHCP
Resolution, the Project has been reviewed for MSHCP consistency, including consistency
with "Other Plan Requirements." These include the Protection of Species Associated with
Riparian/Riverine Areas and Vernal Pool Guidelines (MSHCP, § 6.1.2), Protection of
Narrow Endemic Plant Species Guidelines (MSHCP, § 6.1.3), Additional Survey Needs
and Procedures (MSHCP, § 6.3.2), Urban/Wildlands Interface Guidelines (MSHCP, §
6.1.4), Vegetation Mapping (MSHCP, § 6.3.1) requirements, Fuels Management
Guidelines (MSHCP, § 6.4), and payment of the MSHCP Local Development Mitigation
Fee (MSHCP Ordinance, § 4).
2. The Project is subject to the City's LEAP and the County's Joint Project Review (JPR)
processes.
The Project site (2.78 acres) is located within Criteria Cell#4266. Therefore, a formal and
complete LEAP application, LEAP 2017-02 was submitted to the City on August 11, 2017
and the JPR application, JPR 17-10-06-02 was submitted to the County on October 3,
2017. The County's Regional Conservation Authority (RCA) completed the review on
November 15, 2017 and found the Project consistent with both the Criteria and Other Plan
Requirements.
3. The Project is consistent with the Riparian/Riverine Areas and Vernal Pools Guidelines.
The property was assessed for the presence of Riparian/Riverine and Vernal Pool habitats
through a review of literature sources and an on-site evaluation. No drainage features
were found on the Project site, and hydrological flow occurs only as sheet flow from the
northeast toward the southwest corner. It was determined that the project site does not
support any areas that would be considered to be jurisdictional waters under the Clean
Water Actor State regulation for isolated waters or streambeds. No riparian habitats were
observed on the project site nor were any plant species typically associated with riparian
areas observed on the project site. The "Western Riverside MSHCP Habitat Assessment
Report"dated October 31, 2017 prepared by Blackhawk Environmental, Inc. identified no
drainage features, water bodies, vernal pools or seasonally inundated waters within the
Project site. There is no suitable habitat for fairy shrimp to occur. The Project is therefore
consistent with the Riparian/Riverine Areas and Vernal Pool Guidelines set forth in Section
6.1.2 of the MSHCP. No further action regarding this section of the MSHCP is required.
4. The Project is consistent with the Protection of Narrow Endemic Plant Species Guidelines.
The property is located within the Narrow Endemic Plant Species Survey Area (NEPSSA).
No suitable habitat was found onsite for narrow endemic sensitive plant species slender-
horned spineflower, spreading navarretia, California Orcutt grass, San Miguel savory,
Hammitt's clay-cress or Wright's trichocornis. One additional sensitive plant species,
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Palmer's grapplinghook, was found to have a low potential to occur onsite, but since it is
a CRPR 4.3 species, this species does not require a focused plant survey per CEQA
standards. No additional non-MSHCP-covered sensitive or narrow endemic plant species
with the potential to occur on site were identified during the literature review and site
assessment. However, the Project site does support suitable habitat for narrow endemic
sensitive plant species Munz's onion, San Diego ambrosia and many-stemmed dudleya.
Therefore, for MSHCP consistency, a focused rare plant survey for these species was
completed. The focused plant survey found no Narrow Endemic Plant Species on the
project site. The proposed project is therefore consistent with the Protection of Narrow
Endemic Plant Species Guidelines.
5. The Project is consistent with the Additional Survey Needs and Procedures.
The MSHCP requires additional surveys for certain species if the project is located in
certain locations. Pursuant to MSHCP Figure 6-2 (Criteria Area Species Survey Area),
Figure 6-3 (Amphibian Species Survey Areas with Criteria Area), Figure 6-4 (Burrowing
Owl Survey Areas with Criteria Area), Figure 6-5 (Mammal Species Survey Areas With
Criteria Area), burrowing owl surveys and surveys for Criteria Area species are required
for the subject property prior to approval of a development proposal. Therefore, for
MSHCP consistency, additional focused rare plant surveys for these species are required.
The property is located within a Criteria Area Species Survey Area (CASSA). No suitable
habitat was found onsite for criteria area sensitive plant species Davidson's saltscale,
Parish's brittlescale, Coulter's goldfields or little mousetail, nor narrow endemic sensitive
plant species slender-horned spineflower, spreading navarretia, California Orcutt grass,
San Miguel savory, Hammitt's clay-cress or Wright's trichocomis. One additional sensitive
plant species, Palmer's grapplinghook, was found to have a low potential to occur onsite,
but since it is a CRPR 4.3 species, this species does not require a focused plant survey
per CEQA standards. No additional non-MSHCP-covered sensitive or narrow endemic
plant species with the potential to occur on site were identified during the literature review
and site assessment. However, the Project site does support suitable habitat for criteria
area sensitive plant species thread-leaved brodiaea, smooth tarplant and round-leaved
filaree, plus narrow endemic sensitive plant species Munz's onion, San Diego ambrosia
and many-stemmed dudleya. Therefore, for MSHCP consistency, a "Focused Rare Plant
Survey Report"dated July 12, 2017 was prepared by Blackhawk Environmental, Inc. The
focused plant survey found no Criteria Area Species on the project site.
The Project is not located within survey areas for amphibian species (MSHCP Figure 6-3)
or mammal species (MSHCP Figure 6-5) and surveys for those species are not required.
As noted in the "Focused Burrowing Owl Survey Report"dated July 12, 2017 prepared by
Blackhawk Environmental, Inc., a focused Burrowing owl(Athene cunicularia) survey was
conducted between April 6, 2017 and June 29, 2017. While most of the Project site is
composed of open, disturbed vegetation suitable for burrowing owl foraging, nesting
opportunities are limited to those areas supporting potential host burrows. Abundance of
suitable burrows was generally low, and all soils onsite appeared to have been graded,
filled, or otherwise leveled to the present human-altered condition. Developed Areas
surrounding the Project were excluded from the surveys due to lack of suitable burrows
or burrow surrogates. The surveys resulted in 15 burrows and one burrow surrogate
(debris pile) suitable for burrowing owl within the Project and associated 150-meter buffer
(Survey Area). No burrowing owls and/or burrowing owl sign was observed during the
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focused surveys. The Project site appears to undergo periodic maintenance through
vegetation management. Burrowing owl-suitable burrows were found in several areas of
the Project site and Survey Area. Optimally suitable areas were correlated with high
California ground squirrel activity, with the greatest concentration in the eastern end of the
Survey Area, outside the Project footprint. Since no burrowing owls were identified during
the focused survey efforts, no impacts to burrowing owls are anticipated to occur. Although
suitable burrows were present onsite, many appeared currently occupied by California
ground squirrels, and no burrowing owls or sign were observed. However, as a standard
condition of approval for the development application, the City of Lake Elsinore will require
a pre-construction presence/absence survey for burrowing owl to be conducted within 30
days of the commencement of project-related grading or other land disturbance activities
to ensure that the species has not moved onto the site since completion of the surveys.
Therefore, the subject project is consistent with the Additional Survey Needs and
Procedures of the MSHCP.
6. The Project is consistent with the UrbanMildlands Interface Guidelines.
Section 6.1.4 of the MSHCP sets forth guidelines that are intended to address indirect
effects associated with locating development in proximity to the MSHCP Conservation
Area, where applicable. The Project site is not immediately adjacent to a MSHCP
Conservancy Area and thus does not pose a risk of causing direct or indirect effects to
MSHCP Conservancy Areas. However, there are two parcels removed from the Project
site but within Cell 4266 that are set aside as Public Quasi-Public Conserved Lands. Both
preserved parcels are owned by the Riverside County Flood Control and occur within and
adjacent to the riparian area of Alberhill Creek. One parcel includes 4.72 acres and the
other includes 0.86 acres. Both preserved parcels occur toward the western end of the
cell, while the Project site is toward the eastern end of the cell, with several parcels
separating the Project site from the preserved parcels. As such, the Project will have no
direct or indirect effects on the Urban Wildlands Interface. For these reasons, the
Urban/Wildlife Interface Guidelines are not applicable.
However, further Urban Wildlands Interface analysis is required under section 6.1.4 of the
MSHCP for proposed Linkage 2 and the flood control mitigation area immediately west of
the Project site. Specifically, edge effects due to construction and long-term operations
and maintenance of the proposed Tige Watersports facility are to be addressed. The
Project design includes a number of features to reduce edge effects to less than significant
levels. First, the Project site will be graded such that Project site runoff(and any toxins)
would be directed toward the north side of the Project site, where a proposed bio-filtration
basin planted with native riparian plant species would be placed. The bio-filtration basin
would be designed to filter out runoff and toxins from the Project site, before directing any
excess runoff to a proposed riprap energy dissipater/secondary filtration zone that
ultimately ends at the Project site boundary. The combination of the bio-filtration basin and
the energy dissipater, when factoring in the volume of Project site-generated runoff
potential, is designed to reduce runoff and toxin thresholds into the adjacent natural lands
to less than significant levels. Second, noise-generating activities due to construction of
the Project would be kept below 60 dBA in the adjacent natural lands through the
implementation of sound walls at the Project boundary; there are no noise impacts
associated with the long-term operations and maintenance of the proposed business
usage of the Project site. Third, any exterior lighting will be shielded away from the natural
lands. Fourth, the proposed usage of the Project site is as a contained hand-built boat
construction and sales business, and as such, there are no plans to introduce domestic
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predators. Fifth, the proposed buildings are situated toward the eastern edge of the parcel,
as far as possible from the adjacent natural lands. Sixth, invasive and/or non-native plant
species on the California Invasive Plant Council List will not be used to landscape the
Project site. All of these design features collectively reduce potential construction-related
and long-term operations and maintenance impacts to less than significant levels, through
avoidance and/or minimization techniques. For these reasons, the subject Project is
consistent with the Urban/Wildlife Interface Guidelines.
7. The Project is consistent with the Vegetation Mapping requirements.
The proposed Project is located within 2.78 acres of entirely disturbed/developed, vacant
land 600 feet west of the intersection of Collier Avenue and Riverside Drive, isolated to
the north and east from the larger extant habitats of the region; however, expansive,
natural riparian willow woodland and mulefat scrub habitat exists to the west and
southwest, adjacent the parcel limits. The southwestern boundary of the Project abuts an
improved drainage channel and dirt roads. Natural mulefat scrub habitat exists beyond the
aforementioned drainage channel and some disturbed-mulefat scrub exists within the
drainage itself. The northwest boundary abuts a parking lot and gymnastics facility. The
northeast borders an RV facility, storage buildings and a vacant disturbed lot. The
southeast perimeter of the project site in bound by Riverside Drive, beyond which exists
a vacant disturbed lot. No native vegetation communities exist on the Project site, and the
entire Project site appears to have been disturbed through disking and grading. One
distinct vegetation community/land use type was observed within the Survey Area. A total
of 2.56 acres of Exotic— Disturbed Areas were identified to occur within the Project site.
The balance of the site (0.22 acres) is developed.
Per the MSHCP, Exotic-Disturbed Areas land uses often include ruderal plant
communities. These areas often occur as a result of the edge effects of developed roads
and associated urban land uses. Typical species include common knotweed(Polygonum
arenastru), common sow thistle (Sonchus oleraceus), horseweed (Conyza canadensis)
and goosefoot (Chenopodium spp.). Disturbed areas may also include escaped
landscaping and ornamentals. Within the Project, these ruderal plant communities are
further described as "Disturbed Areas."Disturbed Areas at the time of the survey included
ruderal vegetation with moderate vegetative cover. These areas exhibited non-native,
ruderal, vegetative ground cover typical of frequent soil disturbances such as black
mustard (Brassica nigra), smooth barley (Hordeum murinum), bur-clover (Medicago
polymorpha) red brome (Bromus madritensis ssp. rubens), red-stem filaree (Erodium
cicutarium), rat-tail fescue (Festuca myuros), Mediterranean schismus (Schismus
barbatus), Indian sweet clover(Melilotus indicus), Russian tumbleweed (Sa/sola tragus),
London rocket (Sisymbrium irio), cheeseweed (Malva parvifora), tocalote (Centaurea
melitensis), prickly lettuce (Lactuca serriola), tree tobacco (Nicotiana glauca), goosefoot
(Chenopodium sp.), prickly sow thistle (Sonchus asper), common sow thistle and wild oat
(Avena fatua), with occasional native species such as rancher's fiddleneck (Amsinckia
menzieseii), checker fiddleneck (Amsinckia intermedia), common sunflower (Helianthus
annuus), jimson weed (Datura wrightii), telegraph weed (Heterotheca grandiflora)
horseweed (Erigeron canadensis), pygmy weed (Crassula connata), ragweed (Ambrosia
acanthicarpa), Coulter horseweed (Laeneccia coulteri), forget-me-not (Cryptantha spp.),
comb-bur(Pectocarya linearis ssp. ferocula) and popcorn flower(Plagiobothrys sp.).
This mapping is sufficient under the MSHCP and is consistent with the MSHCP vegetation
mapping requirements.
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8. The Project is consistent with the Fuels Management Guidelines.
The MSHCP acknowledges that brush management to reduce fuel loads and protect
urban uses and public health/safety shall occur where development is adjacent to
conservation areas. Surrounding land uses include the developed Twist'n U Gymnastics
facility and associated parking lots to the northwest; an RV facility, storage buildings and
a vacant disturbed lot to the northeast; Riverside Drive and beyond a vacant disturbed lot
to the southeast, and an improved drainage channel containing disturbed mulefat scrub,
beyond which lies a riparian woodland, to the southwest. The Project site is not
immediately adjacent to a MSHCP Conservancy Area and thus does not pose a risk of
causing direct or indirect effects to MSHCP Conservancy Areas. Therefore, the Project is
consistent with the Fuels Management Guidelines as set forth in Section 6.4 of the
MSHCP.
9. The proposed project will be conditioned to pay the City's MSHCP Local Development
Mitigation Fee.
The project has been conditioned to pay MSHCP Local Development Mitigation fees prior
to issuance of a grading permit, in effect at the time of permit issuance.
10. The proposed Project is consistent with the MSHCP.
Target conservation in Criteria Cell#4266 will range from 30% to 40% of the Cell focusing
in the western portion of the Cell. There are two parcels removed from the Project site but
within Cell 4266 that are set aside as Public Quasi-Public Conserved Lands. Both
preserved parcels are owned by the Riverside County Flood Control District and occur
within and adjacent to the riparian area of Alberhill Creek. One parcel includes 4.72 acres
and the other includes 0.86 acres. Both preserved parcels occur toward the western end
of the cell while the Project site is toward the eastern end of the cell, with several parcels
separating the Project site from the preserved parcels. Additionally, the Project site does
not meet the conservation requirements set forth for Subunit 3 of the Elsinore Area Plan.
Therefore, conservation of the project site or any portion thereof, is not required. The
proposed project is consistent with the MSHCP.
Section 3: Based upon the evidence presented, both written and testimonial, and the above
findings, the Council hereby finds that the Project is consistent with the MSHCP.
Section 4: This Resolution shall take effect immediately upon its adoption.
Section 5: The City Clerk shall certify to the adoption of this Resolution and enter it into the book
of original Resolutions.
Passed and Adopted on this 27th day of March 2018.
CC Reso. No. 2018-046
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Nasha John o
Mayor
Attest:
Susaa-n . Domen, MMC
City Clerk
STATE OF CALIFORNIA )
COUNTY OF RIVERSIDE ) ss.
CITY OF LAKE ELSINORE )
I, Susan M. Domen, MMC, City Clerk of the City of Lake Elsinore, California, do hereby certify
that Resolution No. 2018-046 was adopted by the City Council of the City of Lake Elsinore,
California, at the regular meeting of March 27, 2018, and that the same was adopted by the
following vote:
AYES: Council Members Hickman, Tisdale and Magee; Mayor Pro-Tern Manos and Mayor Johnson
NOES: None
ABSENT: None
ABSTAIN: None
5"usan M. Domen, MMC
City Clerk
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