# ENVIRONMENTAL ASSESSMENT (2017)

> Briefs, arguments, decisions, and more.

URL: https://www.frixlaw.com/law-library/documents/tribal%3Acher-ae_heights%3A10eb985573888d56

## Record

- **Collection:** Tribal code
- **Document type:** Tribal code

## Text

ENVIRONMENTAL ASSESSMENT
TRINIDAD RANCHERIA
STORMWATER IMPROVEMENT AND
INTERPRETIVE VISITOR CENTER PROJECT

."3$) 2017
LEAD AGENCY:
Bureau of Indian Affairs
2800 Cottage Way
Sacramento, CA 95825
(916) 978-6000

ENVIRONMENTAL ASSESSMENT
TRINIDAD RANCHERIA
STORMWATER IMPROVEMENT AND
INTERPRETIVE VISITOR CENTER PROJECT

."3$) 2017
LEAD AGENCY:
Bureau of Indian Affairs
2800 Cottage Way
Sacramento, CA 95825
(916) 978-6000
PREPARED BY:
Analytical Environmental Services
1801 7th Street, Suite 100
Sacramento, CA 95811
(916) 447-3479
www.analyticalcorp.com

TABLE OF CONTENTS
TRINIDAD RANCHERIA
STORMWATER IMPROVEMENT AND INTERPRETIVE
VISITOR CENTER PROJECT
ENVIRONMENTAL ASSESSMENT
1.0

INTRODUCTION
1.1
Introduction......................................................................................................................1-1
1.2
Background......................................................................................................................1-1
1.3
Location and Setting ........................................................................................................1-3
1.4
Purpose and Need for the Proposed Action .....................................................................1-3
1.5
Overview of the Environmental Review Process ............................................................1-8
1.6
Environmental Issues Addressed .....................................................................................1-8
1.7
Regulatory Requirements and Approvals ........................................................................1-8

2.0

PROPOSED ACTION AND ALTERNATIVES
2.1
Selection of Alternatives for Detailed Evaluation ...........................................................2-1
2.2
Proposed Action and Proposed Project............................................................................2-1
2.3
No-Action Alternative .....................................................................................................2-9
2.4
Comparison of the Proposed Action and the Project Alternatives.................................2-10

3.0

DESCRIPTION OF AFFECTED ENVIRONMENT
3.1
Land Resources................................................................................................................3-1
3.2
Water Resources ..............................................................................................................3-5
3.3
Air Quality and Greenhouse Gas ...................................................................................3-10
3.4
Biological Resources .....................................................................................................3-15
3.5
Cultural Resources.........................................................................................................3-21
3.6
Socioeconomic Conditions / Environmental Justice......................................................3-24
3.7
Transportation and Circulation ......................................................................................3-27
3.8
Land Use ........................................................................................................................3-28
3.9
Agriculture .....................................................................................................................3-29
3.10
Public Services...............................................................................................................3-31
3.11
Noise ..............................................................................................................................3-33
3.12
Hazardous Materials ......................................................................................................3-36
3.13
Visual Resources............................................................................................................3-36

4.0

ENVIRONMENTAL CONSEQUENCES
4.1
Proposed Action...............................................................................................................4-1
4.2
No-Action Alternative ...................................................................................................4-17
4.3
Cumulative Effects ........................................................................................................4-19
4.4
Indirect and Growth-Inducing Effects ...........................................................................4-25

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5.0

MITIGATION MEASURES
5.1
Land Resources................................................................................................................5-1
5.2
Water Resources ..............................................................................................................5-3
5.3
Air Quality .......................................................................................................................5-3
5.4
Biological Resources .......................................................................................................5-3
5.5
Cultural Resources...........................................................................................................5-5
5.6
Socioeconomic Conditions / Environmental Justice........................................................5-6
5.7
Transportation and Circulation ........................................................................................5-6
5.8
Land Use ..........................................................................................................................5-6
5.9
Agriculture .......................................................................................................................5-6
5.10
Public Services.................................................................................................................5-6
5.11
Noise ................................................................................................................................5-6
5.12
Hazardous Materials ........................................................................................................5-7
5.13
Visual Resources..............................................................................................................5-7

6.0

CONSULTATION, COORDINATION AND LIST OF PREPARERS
6.1
Federal Agencies..............................................................................................................6-1
6.2
Local Government ...........................................................................................................6-1
6.3
Preparers of Environmental Assessment .........................................................................6-1

7.0

BIBLIOGRAPHY............................................................................................................................7-1

LIST OF TABLES
2-1
3-1
3-2
3-3
3-4
3-5
3-6
3-7
3-8
3-9
3-10
3-11
3-12
4.1-1
4.1-2
4.1-3
4.1-4
4.1-5
4.3-1
4.3-2

Requested Trust Parcels...................................................................................................2-2
Soil Properties for Soils on the Project Site.....................................................................3-2
General Water Quality Objectives for the Eel River ......................................................3-9
2010 Clean Water Act Section 303(D) List .....................................................................3-9
Water Quality Objectives for Groundwater .....................................................................3-9
National Ambient Air Quality Standards.......................................................................3-11
NCAB Attainment Status...............................................................................................3-14
Potentially Occurring Federal Special-Status Species ...................................................3-20
Trinidad, Humboldt County, California Demographics ................................................3-25
Trinidad, Humboldt County, California Employment ...................................................3-25
Cher-Ae Heights Inidan Community of Trinidad Rancheria Estimates ........................3-26
Humboldt County Race/Income Profile.........................................................................3-26
Typical Sound Levels of Common Noise Sources ........................................................3-34
Wastewater Flows for Alternative A ...............................................................................4-3
Unmitigated Construction Emissions ..............................................................................4-7
Unmitigated Operational Emissions ................................................................................4-7
Typical Construction Noise Levels................................................................................4-15
Typical Noise Levels from Construction Equipment ....................................................4-15
Greenhouse Gas CO2 Equivalent ...................................................................................4-22
Alternative A GHG Emissions.......................................................................................4-22

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Table of Contents

LIST OF FIGURES
1-1
1-2
1-3
2-1
2-2
3-1
3-2
3-3
3-4

Regional Location............................................................................................................1-4
Site and Vicinity ..............................................................................................................1-5
Aerial Photograph ............................................................................................................1-6
Site Plan ...........................................................................................................................2-4
Interpretive Center Site Plan............................................................................................2-5
Regional Faults ................................................................................................................3-3
Soil Types ........................................................................................................................3-4
Habitat Types and Potential Waters of the U.S. ............................................................3-18
General Plan Land Use ..................................................................................................3-30

APPENDICES
Appendix A
Appendix B
Appendix C
Appendix D
Appendix E
Appendix F
Appendix G

Bay Street Stormwater Improvement Plans
New Interpretive Center Building at Trinidad Pier Plans
Pier Stormwater Plans
Biological Resources
Cultural Resources Study (Bound Under Separate Cover)
Phase I Environmental Site Assessment
CalEEMod Results

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SECTION 1.0
INTRODUCTION
1.1

INTRODUCTION

The U.S. Bureau of Indian Affairs (BIA) is the federal agency that is charged with reviewing and approving
tribal applications pursuant to 25 C.F.R. Part 151 to take land into federal trust status. This Environmental
Assessment (EA) has been prepared for the BIA to support the application of the Cher-Ae Heights Indian
Community of the Trinidad Rancheria (Tribe) for land to be placed into federal trust (Proposed Action) in
Humboldt County, California. This land, also referred to as the Tribe’s Harbor Properties, consists of nine
parcels and three non-parceled areas, in part and whole, totaling approximately nine acres adjacent to
Trinidad Bay. The land is currently owned by the Tribe in fee simple status. This land is intended to be
used for an interpretive visitor center (visitor center), open space, and operation of currently existing
facilities (Proposed Project). Currently existing facilities consist of the Seascape Restaurant, Seascape
vacation rental house, Trinidad pier, a vessel haul-out hoist, surface parking, and several outbuildings. The
BIA will use this EA to determine if the Proposed Action would result in adverse effects to the
environment.
This document has been prepared in accordance with the requirements set out in the National
Environmental Policy Act (NEPA) of 1969 (42 United States Code [USC] §4321 et seq.), the Council on
Environmental Quality (CEQ) Guidelines for Implementing NEPA (40 C.F.R. Parts 1500-1508), and the
BIA’s NEPA Guidebook (59 Indian Affairs Manual [IAM] 3-H). Section 2.0 of this EA provides a detailed
description of the Project Alternatives. Section 3.0 provides a description of the existing environmental
conditions on and in the vicinity of the project site. Section 4.0 provides an analysis of the potential
environmental consequences associated with the Project Alternatives. A discussion of impact avoidance
and mitigation measures is provided in Section 5.0. Consistent with the requirements of NEPA, the BIA
will review and analyze the environmental consequences associated with the Proposed Action and Project
Alternatives, and either determine that a Finding of No Significant Impact (FONSI) is appropriate, request
additional analysis, or request that an Environmental Impact Statement (EIS) be prepared.

1.2

BACKGROUND

The Cher-Ae Heights Indian Community of the Trinidad Rancheria is a federally-recognized Indian Tribe
with ancestral ties to the Yurok, Wiyot, Tolowa, Chetco, Karuk, and Hupa peoples. The Tribe is located
within the ancestral territories of the Yurok, with core land holdings located on a coastal bluff east of
Highway 101, just south of the town of Trinidad. Trinidad is located approximately 25 miles north of the

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1.0 Introduction

City of Eureka. Under a 1906 Congressional act authorizing the purchase of land for “homeless Indians,”
60 acres were purchased in 1908 on Trinidad Bay for the original members of the Tribe. Federal
recognition was subsequently granted by the Department of the Interior in 1917, Articles of Association
were enacted by 1961, and a new Tribal Constitution was passed in 2008. The Tribe currently has
approximately 228 members. The governing body of the Tribe is ultimately the Community Council,
which consists of enrolled members who are eligible to vote. Eligible voters are tribal members at least 18
years of age who satisfy a number of annual requirements to maintain voting privileges. The Community
Council meets monthly as a forum opportunity to discuss aspects of Tribal business and services. The
Tribal Council is elected from those members comprising the Community Council. The duty of the Tribal
Council is to govern all the people, resources, land, and water reserved to the Tribe, in accordance with the
Tribe’s Constitution, all laws adopted by the Tribal Council, and any limitations lawfully imposed by the
Tribal Council and/or the United States through statute or Constitution. The Tribal Council Officers’ duties
include a wide range of responsibilities including attending all meetings, serving as liaisons to advisory
committees, and most importantly, upholding the Tribal Constitution. Specific responsibilities, duties,
expectations, and guidelines are thoroughly outlined in the Trinidad Rancheria’s Tribal Constitution. The
Tribal Council consists of a Chairperson, Vice-Chairperson, Secretary/Treasurer, and two additional
Council members.
The Tribe’s culture, including but not limited to traditional and customary fishing and gathering, is
inextricably tied to the land and marine resources found within the traditional homeland, which is defined
as a 20-mile area of interest and concern surrounding the Tribe’s lands. The Tribe has made a significant
investment to revitalize the local economy and preserve the Tribe’s cultural heritage, and has developed a
model that advances economic development and stewardship. In January 2000, Trinidad Rancheria
purchased the Trinidad Pier, harbor facilities, and the Seascape Restaurant, including the parking along Bay
Street. The Trinidad Pier was built between 1945 and 1946 to serve commercial and recreational users. A
cannery at the end of the pier was swept away by a storm in 1957 and never replaced. Due to the
deterioration of the original wooden supports, the Tribe, with funding in part by the California State Water
Resources Control Board (SWRCB), the California Coastal Conservancy (CCC), the Environmental
Protection Agency (EPA) Brownfield Grant, the Federal Highway Administration (FHWA), and the BIA,
completed a reconstruction of the pier in 2013. The deteriorated creosote-treated wood pilings and the
wood decking were replaced by polymer-coated steel pilings and pre-cast concrete decking. The Trinidad
Pier is currently the northernmost oceanfront pier in California and serves a fleet of commercial winter crab
fishing vessels and year-round water angling for salmon and near shore fish species. The Trinidad
Rancheria currently operates the pier, and upland improvements including a boat launch ramp and the
Seascape Restaurant. Since taking over the operations of the Trinidad Pier and upland improvements in
2000, the Tribe has incurred losses of over $1.3 million.

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1.3

LOCATION AND SETTING

The trust acquisition parcels addressed in this EA are located west of Highway 101 in Humboldt County,
approximately 18 miles north of the City of Eureka and within the City of Trinidad (project site). The
project site is located in Section 26 of the ‘Trinidad, CA’ U.S. Geological Survey (USGS) quadrangle
within Township 8 North and Range 1 West, and unsectioned areas of Trinidad Bay. Figures 1-1 and 1-2
show the regional location and vicinity of the project site. Figure 1-3 shows an aerial photograph of the
project site. The project site includes nine parcels, totaling approximately six and a half acres, which are
held partially or wholly in fee by the Tribe. These parcels are identified by Assessor Parcel Numbers
(APNs) 042-07-101, 042-07-102, 042-07-105, 042-07-108, 042-07-112, 042-07-113, 042-07-114, 042-09108, and 042-09-110. The project site also includes approximately two and a half acres that do not have
APNs for a total of nine acres of lands for the requested trust transfer. Although these parcels are not
contiguous with the current Rancheria, they are within approximately 0.5 miles of the Tribe’s Reservation.
Regional access is provided by Highway 101, which travels in a general north-south direction and is located
approximately 0.5 miles east of the site. Local access to the project site is provided by Lighthouse Road
and Bay Street. Lighthouse Road is a two-lane road that runs adjacent to the northwestern half of the
project site. Bay Street, which transitions from Lighthouse Road, runs northwest to southeast though the
western half of the project site. Access to Lighthouse Road from Highway 101 is provided via Main Street,
Trinity Street, and Edwards Street. Edwards Street parallels the northern border of the project site.
The project site is composed of a mosaic of ruderal and developed habitat, coastal dune grass habitat, beach,
and two vegetated rock heads which project southwards into Trinidad Bay. The topography of the site
consists of coastal beachfront and bluffs with elevations of 0 to 55 feet above mean sea level (amsl).
Surrounding land uses include private residences, surface parking, Humboldt State University’s Marine
Laboratory, Trinidad State Beach, and undeveloped parcels. The current Rancheria, approximately 0.5
miles east and opposite the bay from the project site, includes Tribal government center, Tribal housing,
and a casino and associated facilities.

1.4

PURPOSE AND NEED FOR THE PROPOSED ACTION

The Tribe’s purpose for taking the approximately nine acres of land into trust is to:
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Facilitate Tribal self-governance and self-determination by allowing the Tribal Government to
exercise Tribal sovereign authority over the land;
Protect and enhance the economic well-being of Tribal resources further establishing economic
self-sufficiency;
Further the Tribe’s goal to restore its original land base;
Further the Tribe’s goal to preserve the surrounding environment and cultural resources for future
generations and the entire community;
Reduce the current stormwater runoff into Trinidad Bay from Harbor Properties improving the
quality of the Trinidad Bay;

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_
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_ Project Site
^
Humboldt County

SCALE

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Miles

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4

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^

P A
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Project Site

SOURCE: ESRI Data, 2016; AES, 2/12/2016

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

Figure 1-1
Regional Location

Patric
oint
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101
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h a ve n

Dr

W es t

Propery Boundary

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SCALE

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Feet

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1,000

2,000

SOURCE: "Trinidad, CA" USGS 7.5 Minute Topographic Quadrangle,
T8N R1W Section 26 and Unsectioned Areas of Trinidad Bay,
Humboldt Baseline & Meridian; AES, 2/25/2016

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

Figure 1-2
Site and Vicinity

Ewing St

Galindo St

Pacific Ct

Edwards St

Azale a Way

Property Boundary
Van Wycke St

2
Ba
y

9

St

1

8
3
4
5

6

LEGEND

7

Property Boundary 9.38 ac
PARCELS:
Pie r

1, APN 04207101, 2.02ac
2, APN 04207102, 0.50ac
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3, 04207105, 0.01ac

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eR
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4, APN 04207108, 2.81ac
5, APN 04207112, 0.40ac
6, APN 04207113, 0.80ac
7, 04207114, 0.46ac
8, APN 04209108, 0.22ac
9, APN 04209110, 0.38ac
No APN, 2.85ac

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Feet

0

125

250

SOURCE: Humboldt County Parcel GIS Data, 2013;
DigitalGlobe aerial photograph, 6/6/2013; AES, 2/25/2016

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

Figure 1-3
Aerial Photograph

1.0 Introduction

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Highlight the cultural and economic background and importance of the Trinidad Harbor to the
surrounding region; and
Form a Trinidad Harbor District which would include all of the Tribe’s current harbor properties.

The Tribe’s culture, including but not limited to traditional and customary fishing and gathering, is
inextricably tied to the land and marine resources found within traditional homeland, which we define as a
20 mile area of interest and concern around the Tribe’s lands. The Tribe has made a significant investment
to revitalize the local economy and preserve the Tribe’s cultural heritage, and we have developed a model
that advances economic development and stewardship as complementary goals. Land acquisition and
transfer to trust is now, and has historically been, a top priority for the Tribe, which owns less than eighty
percent of the land originally purchased under the 1906 Congressional act. The Trinidad Pier and
development of harbor businesses represent the best parcels of land for economic development for the
Rancheria.
Trinidad Harbor is designated by the California Coastal Commission as a Critical Coastal Area and by the
State Water Board as an Area of Special Biological Significant (ASBS). In 2005, the Rancheria received a
cease and desist order (CDO) from the SWRCB for prohibited discharges from the Trinidad harbor and pier
facilities to the Trinidad Head ASBS. The list of prohibited discharges in the CDO included the freshwater
hose on the pier, the fish cleaning station, runoff from the pier itself, boat cleaning activities in and around
the boat launch, and runoff from the harbor parking lot facility. Since 2005, the Rancheria has completed
significant modifications at the Trinidad harbor and pier facilities to eliminate the prohibited discharges as
set forth in the CDO. Major site improvements that have been undertaken include removal of the fish
cleaning station and freshwater hose at the pier, construction of a new wastewater treatment system for the
Seascape Restaurant and adjacent vacation rental, construction of new public restrooms, and reconstruction
of the pier including installation of a stormwater capture and treatment system for runoff from the pier.
These modifications resulted in elimination of all of the discharges of concern with the exception of
stormwater runoff from the parking lot. The Rancheria is continuing to implement facility improvement
efforts to reduce nonpoint sources of discharge further, with the goal of eliminating all nonpoint-source
discharges from the Trinidad harbor and pier facilities. Public parking areas associated with the Trinidad
harbor and pier facilities include the main parking lot and boat launch area. These parking areas are used by
beachgoers, boaters, and patrons of the Seascape Restaurant, tackle shop, and pier. A significant portion of
the traffic at the main parking lot is from boaters with trailers using the launching facilities or boaters
without trailers using the mooring facilities. The main parking area contributes stormwater runoff as a
nonpoint-source to the adjacent beach area referred to as Launcher Beach. The parking lot is often used as a
staging area for boat and trailer repairs, potentially contributing repair-related pollutants to the harbor. This
parking lot has been identified by the SWRCB as a nonpoint source area that contributes discharges to the
Trinidad ASBS, and this area falls under the CDO issued in 2005
As a governmental entity, the Tribe has a responsibility to meet the economic, social, cultural and
environmental needs and concerns of its people. The primary task of the Tribe is to increase the standard of

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1.0 Introduction

living and quality of life for Tribal members for the Cher-ae Heights Indian Community of the Trinidad
Rancheria; and to provide employment opportunities, education and job training. Placing this land into trust
will allow the tribe to develop a stronger economic foundation, employing more tribal members, and
developing additional amenities to enhance the overall operation. It will allow the land to fall under the
Tribe’s authority, critical for the exercise of Tribal self-governance and self-determination, and is consistent
with the Bureau’s trust responsibility to Indian Tribes and the federal policies supporting Indian selfdetermination and self-sufficiency.

1.5

OVERVIEW OF THE ENVIRONMENTAL REVIEW PROCESS

This EA is intended to satisfy the environmental review process of 59 IAM 3-H, 40 Code of Federal
Regulations (CFR) § 1501.3, and 40 CFR § 1508.9. The EA has been released for a 30-day comment
period. Comments will be considered by the BIA, and either a FONSI will be prepared, or additional
environmental analysis will be conducted. After the NEPA process is complete, the BIA may issue a
determination on the Tribe’s fee-to-trust application.

1.6

ENVIRONMENTAL ISSUES ADDRESSED

In accordance with NEPA and because the Proposed Action is located within a coastal zone, this EA
evaluates the following environmental issue areas outlined within the BIA’s NEPA Guidebook:
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1.7

Land Resources;
Water Resources;
Air Quality and Greenhouse Gas;
Biological Resources;
Cultural Resources;
Socioeconomic Conditions / Environmental Justice;
Transportation and Circulation;
Land Use;
Agriculture;
Public Services;
Noise;
Hazardous Materials; and
Visual Resources.

REGULATORY REQUIREMENTS AND APPROVALS

The following direct and indirect federal approvals and actions may occur as a result of the Proposed
Action:

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Transfer of the approximately nine-acre site into federal trust status for the Tribe by the Secretary
of the Interior.
Submission of inventory information to the Environmental Protection Agency (EPA) for the Class
V stormwater wells under the Safe Drinking Water Act Underground Injection Control Program.
Application for a National Pollutant Discharge Elimination System (NPDES) General Permit for
Storm Water Discharges Associated with construction activity.
Consultation with the U.S. Fish and Wildlife Service (USFWS) and the National Marine Fisheries
Service (NMFS) under Section 7 of the Federal Endangered Species Act (ESA), if endangered
species may be impacted by the Proposed Action.
Consultation with the State Historic Preservation Office under Section 106 of the National Historic
Preservation Act (NHPA).
Request for a California Coastal Commission Federal Consistency Determination.

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SECTION 2.0
PROPOSED ACTION AND ALTERNATIVES
The Project Alternatives are described in this section. This section also summarizes the protective measures
and Best Management Practices (BMPs) incorporated into each alternative to reduce potential adverse
impacts to environmental resources.

2.1

SELECTION OF ALTERNATIVES FOR DETAILED EVALUATION

As discussed in Section 1.4, the Purpose and Need of the Proposed Action relates to the protection of the
harbor and harbor environment (including cultural resources) while furthering Tribal goals of economic
self-sufficiency, reestablishment of its original land base, self-governance, and self-determination. The
only reasonable alternatives are to either take no action or take the requested parcels into trust on behalf of
the Tribe. Other potential alternatives to the Proposed Action, such as alternative locations or a reduction in
the size of the area taken in to trust, do not meet the definition of “reasonable” under the Council on
Environmental Quality’s (CEQ’s) Regulations for Implementing the National Environmental Policy Act
(NEPA) because the purpose and need would not be met. Being the only harbor currently owned by the
Tribe in close proximity to Tribe’s existing lands, there are no other available comparable lands that would
meet the purpose and need of the Proposed Action. Furthermore, all the parcels constitute the Trinidad
Harbor lands and are vital to the operation of the pier and protection of cultural resources. For example, as
shown on Figure 1-3, the spacing between Assessor’s Parcel Number (APN) 042-071-08 and 042-071-01 is
vital to maintain public access to the trail head of Trinidad Head, which can be seen on the aerial
photograph. Furthermore, APN 042-071-01 is an important storage area for operation of the pier during the
crab and fishing seasons. Accordingly, a smaller area for the trust acquisition is not evaluated within the
Environmental Assessment (EA).
The Tribe has proposed the development of a visitors’ center and formation of a Trinidad Harbor District
(Proposed Project). There are no alternative lands available that would allow the Tribe to form the Trinidad
Harbor District. Furthermore, all of the currently proposed lands are vital to the protection of the Trinidad
Harbor District. Therefore, alternative locations for trust acquisitions are not evaluated within this EA. The
Proposed Project would allow the Tribe to better market, manage, and operate its harbor properties more
effectively. The Proposed Project is detailed below in Section 2.2.

2.2

PROPOSED ACTION AND PROPOSED PROJECT

The Proposed Action consists of placing nine parcels and three non-parceled areas totaling approximately
nine acres as detailed in Table 2-1 into Federal trust status. These parcels are collectively known as the
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2.0 Proposed Action and Alternatives

Tribe’s Harbor Businesses. This includes the pier, boat launch, boat cleaning and maintenance facilities,
two parking lots (Bay Street and western parking lots), the Seascape Restaurant, a bait and gift shop, a
vacation rental house, recreation areas, and areas for boat parking. The Proposed Action would include the
construction of a visitor center, improvements to the existing parking lot, and the formation of a Trinidad
Harbor District for the Tribe’s Harbor Businesses (Proposed Project). The development footprint of the
visitor center would be approximately 0.03 acres. Approximately one acre of the project site is currently
paved or otherwise developed with existing structures and signs of surface and subsurface disturbance (such
as the presence of utilities). The majority of the project site (approximately five acres) would remain
undeveloped and would be maintained as open space.
TABLE 2-1
REQUESTED TRUST PARCELS
Assessor’s Parcel #

Size (acres)

1 042-07-101

0.99

2 042-07-102

0.44

3 042-07-105

0.01

4 042-07-108

2.64

5 042-07-112

0.26

6 042-07-113

0.80

7 042-07-114

0.38

8 042-09-108

0.24

9 042-09-110

0.35

10 No APN

3.24

Total Acreage

9.35

SOURCE: AES 2016.

PROPOSED ACTION
The Proposed Action consists of the fee simple conveyance of the approximately nine-acre project site into
federal trust status for the benefit of the Cher-Ae Heights Indian Community of the Trinidad Rancheria
(Tribe) in accordance with procedures set forth in 25 Code of Federal Regulations (CFR) §151.3. This trust
action would shift civil regulatory jurisdiction over the approximately nine-acre site from the State of
California, Humboldt County (County), and City of Trinidad (City) to the Tribe and the federal
government. The State, County, and City would continue to exercise criminal jurisdiction under Public
Law 280 (18 United States Code [USC] §1162) for the law enforcement activities identified under the
Tribal Law Order Act of 2010. While the pier would be included within the trust action, in accordance with
an agreement executed April 18, 2012 between the Tribe and the California Coastal Conservancy (CCC),
the Tribe would maintain public access to the Trinidad Pier and associated marine access and recreational
improvements until 2032. Federal laws, such as the Clean Water Act (CWA) and the Endangered Species
Act (ESA), would continue to apply to tribal trust lands.

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ALTERNATIVE A – PROPOSED PROJECT
The Tribe proposes to develop the Trinidad Harbor District. As components of the new Trinidad Harbor
District, the Tribe would designate the beaches and bluffs as protected open space, improve stormwater
quality, reduce stormwater flows generated along Bay Street, and construct a visitor center where the
existing tackle shop is located. Alternative A is further discussed below.

HARBOR DISTRICT
The Trinidad Harbor District would include all of the Tribe’s Harbor Businesses. The Trinidad Harbor
District Board of Directors would be comprised of Tribal members and staff that have current experience
with the Harbor Businesses. The board of the Trinidad Harbor District would develop a more cohesive
organization that markets, manages, and operates the businesses within the district more effectively. The
establishment of this district would provide the Tribe with means of meeting the purpose and need of the
proposed trust action.

OPEN SPACE COMPONENT
All existing open space within the project site (approximately five acres) would be preserved as open space
and the Tribe would maintain public access to the open space. The open space would include Trinidad
Little Head, all beach front, all Coastal Bluffs lands on the property, and current open space west of the
residence. Development under Alternative A would occur on existing disturbed lands constituting the
existing parking lot, storage area, and the tackle and gift shop.

BAY STREET STORMWATER IMPROVEMENTS
2.2 of the Attached (Figure 2-1). Design plans for the improved stormwater facilities are included as
Appendix A. To reduce stormwater flow four dry wells, two cisterns, and two rain gardens would be
installed around the Tribe’s Harbor Businesses and parking lot along Bay Street. In addition, rain gardens
would be developed as shown on Figure 2-1 to collect rainwater. To reduce flows from Bay Street into the
bay, the southeastern portion of the parking lot would be replaced with permeable pavers. Linear drains
would be installed throughout the parking lot to transfer runoff to a bioswale that runs along the northern
boundary of the parking lot before discharging onto the beach. The concrete rubble along the beach east of
the proposed visitor center would be removed (Figure 2-1) and replaced with rip rap. Minor excavation
would be required to develop the rain gardens, linear drains, bioswale, and the permeable pavement.

INTERPRETIVE VISITOR CENTER COMPONENT
The Tribe would develop a visitor center within the currently developed footprint between the boat launch
and Seascape Restaurant in the central portion of the site, as shown in Figure 2-2. Design plans are
included as Appendix B. The visitor center footprint would cover approximately 1,300 square feet and
would be located on previously disturbed lands that currently house storage units and the tackle and

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9.27 ac

0

30

Feet

60

Visitors Center 0.03 ac

INSTALL RAIN GARDEN #2

INSTALL DRY WELL
#2 ON DOWNSPOUTS

RESTROOM

INSTALL DRY WELL
#1 ON DOWNSPOUTS

INSTALL DRY WELL
#3 ON DOWNSPOUTS

TRINIDAD BAY

CISTERN #1
89 GAL.

UNDERGROUND
SEPTIC PUMP

SEWER
PIPES

Pie
r

Bay St

CISTERN #2
392 GAL.
PIER

RESIDENCE
INSTALL DRY WELL
#4 ON DOWNSPOUTS

E

Galindo St

Figure 2-1
Site Plan

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

SEASCAPE
RESTAURANT

INSTALL CONCRETE CURB
PLACE RIP RAP ON BANK
(1 TON ROCK)

E

LAUNCHER BEACH

INSTALL PERMEABLE PAVERS
INSTALL CONCRETE BLOCK MAT

INSTALL LINEAR DRAIN #7

INSTALL LINEAR DRAIN #6

INSTALL LINEAR DRAIN #5

INSTALL BIOSWALE

INSTALL LINEAR DRAIN #4

INSTALL LINEAR DRAIN #3

RESIDENCE

E

E

INSTALL LINEAR DRAIN #8

INSTALL SPEED HUMP #2
E

INSTALL RAIN GARDEN

INSTALL RETAINING WALL

E

E
E

INSTALL LINEAR DRAIN #2

E

E

E

INSTALL LINEAR DRAIN #1

E

PLANT INDIGENOUS PLANTS
NATIVE TO BEACH DUNES

E

E

SOURCE: Pacific Watershed Associates, 6/1/2016; Humboldt County Parcel GIS Data, 2013; DigitalGlobe aerial photograph, 5/28/2014; AES, 7/13/2016

¢

LEGEND

Property Boundary

!

NOR T H

Ð

Rd

E

se

E

ou
h th
Lig

E

E

E

E
E

E

E

E

E

E

E

E

E

E

E

E

E

RT

0

2.5

Feet

5

Project Site 0.03 ac

7.5

Figure 2-2
Interpretive Center Site Plan

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

H

SOURCE: TVCE, 11/4/2015; AES, 2/23/2016

¢

Ð

LEGEND

Property Boundary 9.27 ac

!
NO

2.0 Proposed Action and Alternatives

giftshop building. The visitor center would provide educational opportunities for tribal citizens and nontribal members of the public and would focus on regional resources including Tribal cultural resources. The
visitor center would include a seating area, reception area, two offices, a restroom, and a food preparation
area. Two public entrances would be provided at the western and southern portion of the building. Parking
for the visitor center would be provided by the existing parking lot along Bay Street. Lighting around the
building and in the parking lot would be downcast and minimized to ensure that effects to local marine life
are minimized, while remaining adequate for public safety and security. Site access would be obtained
from Lighthouse Road and Bay Street. The visitor center would result in the hiring of one full-timeequivalent employee (FTE) and would also house the existing Harbor Manager. The Tribe estimates
approximately five visitors a day are expected to patronize the visitor center during peak season.
Water Supply
Water would be supplied though the existing infrastructure connections to the City. Except for connections
from the visitor center to the existing system serving the Seascape Restaurant, no additional water
infrastructure is needed for Alternative A. Based on the addition of one FTE, the additional water demand
to the site would be de minimis compared to existing water users on the site (rental house, bait and gift
shop, and Seascape Restaurant). Visitors to the site would obtain water from the existing fountains near the
restrooms or from the Seascape Restaurant.
Wastewater Treatment and Disposal
Wastewater generated by the one toilet and from the two sinks within the visitor center would be treated by
the existing wastewater treatment system. The on-site system consists of a series of seven above ground
recirculating packed bed units located south of the public restroom/storage building and situated behind a
chain link fence. The on-site system utilizes engineered textile filter media, which works similarly to a sand
filter and produces treated effluent higher in quality than the California standard for secondary treated
wastewater (which can be discharged through land application). The seven tanks have the ability to treat up
to approximately 35,000 gallons per day (Orenco, 2016). A pump transfers the treated wastewater up to the
leach fields located along the northwestern slope of the hill near the western boundary of APN 04207108,
between the access drive to the vacation rental home and the western parking lot.
Grading and Drainage
Grading would be limited to the development footprint area of the visitor center as shown on the proposed
Site/Grading Plan (refer to Sheet C4 of Appendix B). The building would be constructed in manner
consistent with the California Building Code (CBC) applicable to the site, including seismic design criteria.
To improve drainage over existing conditions, a storm drainage inlet system would be installed west and
south of the visitor center to capture runoff from the building and from Bay Street. Three storm inlets

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2.0 Proposed Action and Alternatives

would discharge to the existing retention system located beneath the asphalt in front of Seascape
Restaurant.

PROJECT CONSTRUCTION
The project components would be constructed after the approximately nine-acre property has been placed
into federal trust. The new visitor center and accompanying parking lot improvements would be
constructed over a five to sixth month period, with an anticipated completion date of 2017. The stormwater
improvements would be constructed during the first phases of the visitor center development. Construction
would involve earthwork, placement of concrete foundations, steel and wood structural framing, masonry,
electrical and mechanical work, building finishing, and paving, among other construction trades. Prior to
finalization of the grading and development plans for the property, design-level geotechnical specifications
addressing the specific grading and development plans would be developed meeting seismic requirements
of the CBC. The specifications would include, but not be limited to, the following:


Site, building and facility-specific grading recommendations regarding site preparation, clearing
and grubbing.



Select grading procedures, remedial grading procedures, material suitability, and compaction
criteria.



Cut and fill slope stability analyses, recommended slope configurations and inclinations.



Evaluation of soil expansion and corrosion potential.



Building-specific foundation design parameters.



Site-specific seismic design parameters.



Lateral earth pressure parameters for retaining wall design, if any.



Pavement design specifications.

BEST MANAGEMENT PRACTICES AND CONSERVATION MEASURES
Air Quality
Generation of construction-related emissions is a short-term nuisance impact. The following BMPs,
required through contractual obligations, would be implemented to reduce these temporary construction
emissions.


The contractor will designate an on-site Air Quality Construction BMP Manager (AQCBM) who
will be responsible for directing compliance with the following BMPs for project construction
relating to heavy-duty equipment use:
o

All diesel-powered equipment shall be properly maintained and minimize idling time to 5
minutes when construction equipment is not in use, unless per engine manufacturer’s
specifications or for safety reasons more time is required.

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o


Engines shall be kept in good mechanical condition to minimize exhaust emissions.

The AQCBM will be responsible for directing compliance with the following BMPs for fugitive
dust control practices during project construction:
o
o

o
o
o
o
o

Spray exposed soil with water or other suppressant at least twice a day or as needed.
Minimize dust emissions during transport of fill material or soil by wetting down loads,
ensuring adequate freeboard (space from the top of the material to the top of the truck bed) on
trucks, and/or covering loads.
Promptly clean up spills of transported material on public roads.
Restrict traffic on site to reduce soil disturbance and the transport of material onto roadways.
Locate construction equipment and truck staging areas away from sensitive receptors as
practical and in consideration of potential effects on other resources.
Provide wheel washers to remove particulate matter that would otherwise be carried off site by
vehicles to decrease deposition of particulate matter on area roadways.
Cover dirt, gravel, and debris piles as needed to reduce dust and wind-blown debris.

Fire Protection
The following BMPs, required through contractual obligations, would be included as part of Alternative A
to minimize the risk of fire during construction:


Any construction equipment that normally includes a spark arrester would be equipped with an
arrester in good working order. This includes, but is not limited to, vehicles, heavy equipment, and
chainsaws.



During construction, staging areas, welding areas, or areas slated for development using sparkproducing equipment would be cleared of dried vegetation or other materials that could serve as fire
fuel. To the extent feasible, the contractor would keep these areas clear of combustible materials in
order to maintain a firebreak.



Structural fire protection would be provided through compliance with Uniform Fire Code
requirements for residences and commercial structures similar in size to the proposed clubhouse.
The Tribe will cooperate with the fire district by allowing routine inspections The Tribe would
ensure that appropriate water supply and pressure is available for emergency fire flows.
Typical fire flow allowances would be confirmed with the local Fire Marshall prior to construction
of any water storage tank.



Hazardous Materials
The following BMPs will be required through contractual obligations and would be included as part of
Alternative A to minimize the risk from use of hazardous materials during construction:


Personnel shall follow best management practices (BMPs) for filling and servicing construction
equipment and vehicles. To reduce the potential for accidental release, fuel, oil, and hydraulic

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fluids shall be transferred directly from a service truck to construction equipment and shall not be
stored on site.

2.3



Catch-pans shall be placed under equipment to catch potential spills during servicing.



Refueling shall be conducted only with approved pumps, hoses, and nozzles.



Vehicle engines shall be shut down during refueling and idling shall be kept to a minimum.



No smoking, open flames, or welding shall be allowed in refueling or service areas.



Refueling shall be performed away from bodies of water to prevent contamination of water in the
event of a leak or spill.



Service trucks shall be provided with fire extinguishers and spill containment equipment, such as
absorbents.



Should a spill contaminate soil, the soil shall be put into containers and disposed of in accordance
with local, state, and federal regulations.



All containers used to store hazardous materials shall be inspected at least once per week for signs
of leaking or failure. All maintenance, refueling, and storage areas shall be inspected monthly.



Hazardous materials must be stored in appropriate and approved containers in accordance with
applicable regulatory agency protocols.



Potentially hazardous materials, including fuels, shall be stored away from drainages, and
secondary containment shall be provided for all hazardous materials stored during construction and
operation.



In the event that contaminated soil and/or groundwater is encountered during construction related
earth-moving activities, all work shall be halted until a professional hazardous materials specialist
or other qualified individual assesses the extent of contamination. If contamination is determined to
be hazardous, representatives of the Tribe shall consult with the BIA and EPA to determine the
appropriate course of action, including development of a Sampling and Remediation Plan, if
necessary. Any and all contaminated soils that are determined to be hazardous shall be disposed of
in accordance with federal regulations.

ALTERNATIVE B – NO-ACTION ALTERNATIVE

Under the No-Action Alternative, the approximately nine-acre site would not be placed in trust for the
benefit of the Tribe and would not be developed as identified under Alternative A. Jurisdiction of the
property would remain within the City. Ultimately, the nine-acre site could be developed consistent with
the existing commercial and recreation land uses by the Tribe. However, for the purposes of the
environmental analysis in this EA, it is assumed that, due to the economic considerations for operating the
Harbor Properties by the Tribe, the property will continue to be utilized in its current state for recreation,
parking, restaurant, boating, and fishing with no additional facilities constructed under this alternative.
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2.0 Proposed Action and Alternatives

2.4

COMPARISON OF THE PROJECT ALTERNATIVES

ALTERNATIVE A
Alternative A would result in significant but mitigable environmental impacts in the following areas:


Land Resources



Water Resources



Biological Resources



Cultural Resources

Of the project alternatives evaluated in Section 4.0, Alternative A would best meet the Tribe’s objectives by
providing the Tribe with a Trinidad Harbor Visitor Center and recreational facilities for the benefit of the
Tribe and community while minimizing or eliminating adverse environmental impacts.

ALTERNATIVE B
While the No-Action alternative would not result in most of the environmental effects identified for
Alternative A, this alternative would not meet the Tribe’s objectives of exercising tribal sovereign authority
over the land and enhance the wellbeing of tribal resources; further the Tribe’s goal to reestablish its
original land base; further the Tribe’s goal to preserve the surrounding environment and cultural resources
for future generations; construct a visitor center; and form a tribal Trinidad Harbor District. The property
would continue to release contaminants from the impervious parking lots into Trinidad Bay during rain
events, potentially harming wildlife and sensitive ecosystems.

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SECTION 3.0
DESCRIPTION OF AFFECTED ENVIRONMENT
This section presents relevant information concerning existing resources and other values that may be
affected by the Project Alternatives. In accordance with the National Environmental Policy Act (NEPA)
and the Bureau of Indian Affairs’ (BIA’s) NEPA Guidebook (59 IAM 3-H), the existing conditions
described herein provide the baseline for determining the environmental effects identified in Section 4.0.
As used herewithin, the terms “project site” and “project parcels” both refer to the approximately nine acres
being requested by the Tribe for trust acquisition by the BIA. Accordingly, the term “proposed
development” refers to the proposed visitor center, roadway, and drainage improvements. Existing setting
descriptions are provided for the following resource and issue areas:














3.1

Land Resources
Water Resources
Air Quality and Greenhouse Gases
Biological Resources
Cultural Resources
Socioeconomic Conditions / Environmental Justice
Transportation and Circulation
Land Use
Agriculture
Public Services
Noise
Hazardous Materials
Visual Resources

LAND RESOURCES

The following section provides the existing topographical, geological and seismic, soil, and mineral
resource settings of the project parcels.

3.1.1 TOPOGRAPHY
The topography of the project site is influenced by the coastal beaches, dunes, and graded landscapes and
ranges from gentle slopes where the areas have been previous graded to steep and rugged bluffs. There are
also two coastal heads that project out into Trinidad Bay on the south central and south eastern portion of
the site. Overall, the northern, central, and eastern portions of the site slope south whereas the western
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3.0 Affected Environment

portion of the site slopes east to west, draining onto Trinidad State Beach. Slopes within the project site are
varied; the proposed development area has gentle slopes between 5 to 6 percent having been previously
disturbed during paving of the access roadways and parking serving the restaurant, pier, and beaches. The
elevations of the project site range from 0 to 55 feet above mean sea level (amsl).

3.1.2 GEOLOGIC SETTING AND SEISMICITY
The bedrock underlying the project site is primarily made up of Mesozoic-Paleozoic-Precambrian
Sedimentary and Metasedimentary Rocks, more specifically, the Franciscan Complex which comprises 54.0
percent of the Trinidad Watershed (County of Humboldt, 2012a). Primary seismic concerns in Humboldt
County (County) include ground shaking and rupture along existing fault traces. Secondary concerns
include liquefaction, settlement, landslides, and tsunamis. The County is a seismically active region.
Offshore, three major faults meet at what is known as the “triple junction.” These include the San Andreas,
the Mendocino fracture zone, and the southern end of the Cascade subduction zone. The faults separate the
Pacific plate, Gorda plate, and North American plate. The project site is located outside of a designated
Alquist-Priolo zone, which is an area determined by the California Geological Survey (CGS) to be a welldefined area with sufficiently active seismicity, according to mandates of the Alquist-Priolo Earthquake
Fault Zoning Act of 1972. These Alquist-Priolo zone areas are located along active faults that are
susceptible to the hazard of surface fault rupture. The nearest Alquist-Priolo zone is approximately 0.43
miles east of the project site along the Trinidad fault and extends northwest just north of Elk Head (Figure
3-1). With the distance to the Trinidad fault and based on the regional geology, the project site is located in
an area of California determined to have a high potential for ground shaking during a seismic event (DOC,
2003).

3.1.3 SOILS
Table 3-1 lists soils found on the project site and their respective properties. The project site is composed
primarily of Oxyaquic Udipsamments – Sonoma Complex soils, but small areas of Candymountain soils are
also present (Figure 3-2).
TABLE 3-1
SOIL PROPERTIES FOR SOILS ON THE PROJECT SITE
Soil Type
157 – Oxyaquic Udipsamments –
Somoa Complex
299 – Candymountain

Slope

Limitations

0-50%

Eroded

30-75%

Eroded

SOURCE: NRCS, 2016

The coastal bluffs in the northern and eastern portion of the project site are comprised of Candymountain
soils. The remainder of the project parcels are comprised of Oxyaquic Udipsamments – Somoa Complex
soils. Oxyaquic Udipsamments soils are typically comprised of unvegetated beaches with parent material
consisting of beach sand and gravel derived from mixed sources, typical of oceanic beaches. These are

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Mo

<100,000 - late Quaternary

ult

Bal d

a n fa

<15,000 - latest Quaternary

u nt
a in

< 750,000 years mid to late Quaternary

"

M
Lo st

Surpur Creek fault

LEGEND

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fau

Other Faults

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ne

Miles

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9
.1

ile

s

^"
_

"

oon
La g

<1.600,000 Quaternary

4
0.

"

3

ile
M

s

PROJECT SITE

6

M
Ri

Bald

ad
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nt

ne
zo

ou

lt
au

M

rf

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g

lt

e

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nf

on
tz
ul
fa

ga

on
go

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^

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PROJECT SITE

f
er
au
lt z

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on

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ad

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P A
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C

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zo

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ad
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ve
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n

tz
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tl
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on

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eS
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e
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lt z

s fau

SOURCE: USGS Earthquake Hazards Program, 2010; AES 11/19/2015

ne

au
lt

lt z o

Blu
ff f

E a to

on

Ta
ble

Trinidad Rancheria / 215569

Figure 3-1
Regional Fault Map

Azalea Way

Galindo St

Pa
c

if i c C

t

Edwards St

Van Wycke St

Bay St

Pier

R
se
ou
hth
Lig
d

LEGEND

!
N O R TH

¢

SOILS ON PROJECT SITE

Ð

Property Boundary

Feet

0

110

220

157 - Oxyaquic Udipsamments-Samoa complex, 0 to 50 percent slopes
299 - Candymountain, 30 to 75 percent slopes
596 - Flintrock-Highprairie complex, 15 to 75 percent slopes

SOURCE: USDA NRCS SSURGO Soils Data, 9/10/2015;
DigitalGlobe aerial photograph, 6/6/2013; AES, 2/25/2016

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

Figure 3-2
Project Site Soil Types

3.0 Affected Environment

typically moderately well drained soils with a very low runoff class and a high to very high capacity to
transmit water. Somoa soils typically comprise coastal dunes with parent material consisting of eolian and
marine sand derived from mixed sources. These are typically somewhat excessively drained soils with a
medium runoff class and a high to very high capacity to transmit water. Candymountain soils typically
comprise bluffs and marine terraces with parent material consisting of marine deposits from mixed sources.
These are typically well drained soils with a high runoff class and a moderately high to high capacity to
transmit water (NRCS, 2016).

3.1.4 MINERAL RESOURCES
The County has over 90 extraction sites that produce sand, gravel, metals, stone, and clay. Most mining
activity is sand and gravel extraction along the Mad River, Eel River-Van Duzen River complex, Willow
Creek, and Trinity River. There are over 30 permitted active hard rock quarries (County of Humboldt,
2012a). The nearest rock extraction site, Trinidad Quarry, is east of Highway 101 and greater than 1.5
miles northeast of the project parcels (USGS, 2015). No known mineral resources exist within the project
parcels.

3.2

WATER RESOURCES

The following section presents the existing surface water, drainage, flooding, water supply, groundwater,
and water quality settings of the project parcels.

3.2.1 SURFACE WATER, DRAINAGE, AND FLOODING
WATERSHEDS AND HYDROLOGY
The project site is situated within the Luffenholtz Creek-Frontal Pacific Ocean subwatershed of the
Trinidad Hydrologic Unit (HU). The Trinidad HU watershed lies immediately between the Redwood Creek
HU, approximately 16 miles to the north, and the Mad River HU, approximately 6 miles south of the
project parcels. Together, with the Eureka Plain HU, these major watersheds form the Mad-Redwood
basin, which comprises 617,426 acres within the County (Department of Conservation, 2014). Within the
Trinidad HU, Mill Creek flows to the west just north of the City and McConnahas Mill Creek flows west
bisecting the City and flowing adjacent to the north boundary of the Trinidad Rancheria. Luffenholtz Creek
is one of the main flowing water bodies in the watershed at over 12 miles in length and a starting elevation
of 269 feet, where it eventually flows and discharges into the Trinidad Bay of the Pacific Ocean
approximately 1.75 miles southeast of the project parcels. Mill Creek is the nearest inland waterbody,
which discharges to the Pacific Ocean approximately 0.3 miles north of the project parcels. However, the
project parcels are situated in Trinidad Harbor and based on the topography do not contribute hydraulically
to the surrounding watersheds.

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3.0 Affected Environment

City Water Supply
The City’s water system serves approximately 315 connections within its sphere of influence using surface
water as the source. The City has a domestic water right for supplies from Luffenholtz Creek, located
approximately a 1.5 miles south of the City. Originally, homes in the City had individual wells or were
served from an untreated water supply from Mill Creek (also referred to as Old Mill Creek). An infiltration
gallery and water treatment plant were constructed to supply the City with water from Luffeholtz Creek
when it became clear that Mill Creek could not meet long term needs.
The pumps located at the infiltration gallery that supply pressure to move water through treatment to the
storage tanks were inundated with sediment a few years back. The pumps were rehabilitated, but have never
worked as well as expected since their repair. The pumps should be capable of delivering 120 gallons per
minute (gpm), but only deliver about 100 gallons per minute. The City of Trinidad has an operations and
maintenance program that keeps the storage, treatment, and distribution systems in good condition. The
storage tanks are regularly inspected and the steel bands tightened to prevent water losses. The City
conducted leak detection testing on the distribution system in 2003 and tested all water meters in 2003.
Major leaks detected have been repaired, and poorly functioning water meters are being replaced as funds
become available (County of Humboldt, 2007).
DRAINAGE
Slopes on the project site range from 0 to 60 percent, with the proposed development area sloping to the
west at approximately 5 to 6 percent and the steepest slopes being the coastal bluffs. Runoff across the
parking surfaces is generated as sheet flow and follows the topography towards Trinidad Bay. This sheet
flow is not collected, but drains onto the beach near the old boat launch to the south of the proposed
development. Sheet flow from the coastal bluff immediately upslope of the proposed development area is
conveyed via natural drainages in the cliff. This water also drains onto the beach.
Pier Stormwater System
Stormwater generated on the pier is collected in a series of gutters and piping where it is treated in a
sedimentation chamber and filter system located adjacent to where the pier connects to land. All
stormwater runoff from the new pier is directed thru the filters and into the infiltration chambers. Filter
cartridges are removed and maintained once every two years as per the manufacturer’s recommendations.
The stormwater filter system treats runoff captured from the pier deck, thus eliminating potential sources of
contamination from pier-generated petroleum products and other pollutants that result from activities on the
pier. Treated stormwater is then diverted to subsurface percolation chambers located beneath the asphalt
directly adjacent to the Seascape Restaurant. The Tribe has implemented a Contingency Plan for Failure of
Stormwater Disposal System plan and a Maintenance and Monitoring of Stormwater Disposal System plan
to ensure adequate operation and maintenance of the stormwater system. Both plans and the storm drain
plan sheet are included as Appendix C. Currently, only stormwater generated on the newly refurbished pier
is collected and treated in the system.

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3.0 Affected Environment

FLOODING
The Federal Emergency Management Agency (FEMA) is responsible for predicting the potential for
flooding in most areas. FEMA routinely performs this function through the update and issuance of Flood
Insurance Rate Maps (FIRM), which depict various levels of predicted inundation. FEMA has not
completed an analysis of flood hazards in Trinidad; as such, a FEMA flood map is unavailable. Areas
immediately northwest of Trinidad including the Trinidad State Beach are zoned D on FEMA flood hazard
maps. Directly north of Trinidad along the Mill Creek’s crossing of Highway 101, a small area of Zone A
is identified. Zone D is reserved for areas where there is a possible but undetermined flood hazard. Zone A
is reserved for areas within the hazard of a 100-year flood (FEMA, 2016).
Areas subject to flood hazards are generally located along the Mill Creek corridor and its associated
ravines. Flood hazard concerns associated with development along the Mill Creek corridor and ravine have
been reduced by the City via a general plan amendment to not allow construction along the corridor. In
general, flooding hazard in the Trinidad area is very slight with the exception of just north of the City and
on the southern boundary where water features are located. The only waterways are small streams flowing
into the ocean and those are typical of high stream banks not subject to frequent flooding. Flooding on
Luffenholtz Creek has affected the City water pumps at times. Within the City, some ponding may occur
due to poorly drained soils. According to the Plate No. 3B in the City’s General Plan, the area just south of
Bay Street (which borders the subject property) is indicated to experience flooding. However, due to the
previous grading conducted at the project site and topography of the upland portions of the City adjacent to
the project parcels, the potential for flooding on the project site is minimal.

3.2.2 GROUNDWATER
The County has 4 main groundwater basins and 10 minor basins. The total potential groundwater yoeld
within the County is approximately 100,000 acre feet. The project site is located in the Big Lagoon Area
minor groundwater basin, which is approximately 34,000 acres (County of Humboldt, 2012b). These
watersheds are within the Coast Ranges geologic province and are mainly composed of highly unstable and
easily eroded rock which contributes to the high amounts of sedimentation in the features streams (County
of Humboldt, 2012b). Outside of the beach areas, depth to groundwater ranges from 20 to 39 inches
(NRCS, 2016). There are no groundwater wells within the project parcels.

3.2.3 WATER QUALITY
SURFACE WATER
The Clean Water Act (CWA) (33 USC 1251-1376), as amended by the Water Quality Act of 1987, is the
major federal legislation governing water quality. The objective of the CWA is “to restore and maintain the
chemical, physical, and biological integrity of the Nation’s waters.” The U.S. Environmental Protection
Agency (USEPA) is delegated as the authoritative body under the CWA. Important sections of the CWA
applicable to the Proposed Action are as follows:
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



Sections 303 and 304 provide for water quality standards, criteria, and guidelines. Section 303(d)
requires states to identify impaired water bodies and develop total maximum daily loads (TMDLs)
for the contaminant(s) of concern.
Section 402 establishes the National Pollutant Discharge Elimination System (NPDES), a
permitting system for the discharge of any pollutant (except for dredged or fill material) into waters
of the U.S. Each NPDES permit contains limits on pollutant concentrations of wastes discharged to
surface waters to prevent degradation of water quality and protect beneficial uses.

Antidegradation Policy
The federal antidegradation policy (40 CFR Part 131.6) is designed to protect water quality and water
resources. The policy directs states to adopt a statewide policy that includes the following primary
provisions: (1) existing instream uses and the water quality necessary to protect those uses shall be
maintained and protected; (2) where existing water quality is better than necessary to support fishing and
swimming conditions, that quality shall be maintained and protected unless the state finds that allowing
lower water quality is necessary for important local economic or social development; and (3) where highquality waters constitute an outstanding national resource, such as waters of national and state parks,
wildlife refuges, and waters of exceptional recreational or ecological significance, that water quality shall
be maintained and protected. Each state must also develop procedures to implement its anti-degradation
policy through water quality management processes. Each state’s anti-degradation policy must include
implementation methods consistent with the provisions outlined in 40 CFR 131.12 (USEPA, 1994).
Complying with the anti-degradation provision of the CWA, the North Coast Regional Water Quality
Control Board (NCRWQCB) has established general water quality objectives for all inland surface waters
under State jurisdiction to protect designated beneficial uses. The Water Quality Control Plan for the North
Coast Region (Basin Plan) outlines these surface water quality objectives. Table 3-2 lists the specific water
quality objects outlined in the Basin Plan by parameter for surface waters under State jurisdiction within the
surrounding watersheds. The Basin Plan does not currently list water quality objectives for the Trinidad
Hydraulic Unit.
The State Water Resources Control Board, in compliance with Section 303 of the Clean Water Act (CWA),
has prepared a list of impaired water bodies in California. Impaired water bodies occur where industrial
and technological waste limits or other legal mechanisms for pollution control are not enough to meet water
quality standards. The list includes a priority schedule for the development of TMDLs for each
contaminant or “stressor” impacting the water body. The Trinidad Bay is not listed on the 303(d) list for
impaired water bodies; however, Trinidad State Beach is listed for impairment of one or more beneficial
uses due to indicator bacteria (Table 3-3).

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TABLE 3-2
GENERAL WATER QUALITY OBJECTIVES FOR THE EEL RIVER
Specific
Conductance
(micro-ohm)

Total
Dissolved
Solids (mg/L)

Dissolved Oxygen
(mg/L)

90%
Upper
Limit1

50%
Upper
Limit2

90%
Upper
Limit1

50%
Upper
Limit2

Min

90%
Upper
Limit1

50%
Upper
Limit2

Min

Max

50%
Upper
Limit2

90%
Upper
Limit1

50%
Upper
Limit2

Redwood
Creek

2203

1253

1153

753

7.0

7.5

10.0

8.5

6.5

None

None

None

Mad River

3003

1503

1603

903

7.0

7.5

10.0

8.5

6.5

None

None

None

Waterbody

Hardness
(mg/L)

pH

Boron
(mg/L)

1

50% upper and lower limits represent the 50 percentile values of the monthly means for a calendar year. 50% or more of the
monthly means must be less than or equal to an upper limit and greater than or equal to a lower limit.
2 90% upper and lower limits represent the 90 percentile values for a calendar year. 90% or more of the values must be less than or
equal to an upper limit and greater than or equal to a lower limit.
3 Does not apply to estuarine areas.
SOURCE: NCRWQCB, 2011a

TABLE 3-3
2010 CLEAN WATER ACT SECTION 303(D) LIST
Location
Trinidad State
Beach

Pollutants/
Stressors
Indicator Bacteria

Potential Sources

TMDL Status

Unknown

TMDL
developed (Category 5a)

TMDL
Completion
Proposed
2019

SOURCE: NCRWQCB, 2011b

GROUNDWATER
The Basin Plan also specifies water quality objectives for groundwater in the north coast. Objectives for
groundwater are listed in Table 3-4.
TABLE 3-4
WATER QUALITY OBJECTIVES FOR GROUNDWATER
Tastes and
Odors
Cannot exceed
concentrations
that cause
nuisance or
adversely affect
beneficial uses

Bacteria1

Radioactivity1

Chemical Constituents1

Cannot exceed 1.1
MPN/100mL
Or
1 colony/100mL

Cannot exceed
California Code of
Regulations, Title 22,
Division 4, Chapter
15, Article 5, Section
64443, Table 4 and
listed in Table 3-2 of
the Basin Plan

Cannot exceed limits specified
in California Code of
Regulations, Title 22, Division
4, Chapter 15, Article 4,
Section 64435 Tables 2 and 3,
and Section 64444.5 (Table 5)
and listed in Table 3-2 of the
Basin Plan

1 Domestic or municipal sources only.
SOURCE: NCRWQCB, 2011a.

In order to protect drinking water supplies and under the mandate of the Safe Drinking Water Act, USEPA
defines National Primary Drinking Water Regulations (primary standards). These are legally enforceable
standards that apply to public water systems. These standards are established to protect human health by

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limiting the levels of contaminants in drinking water. The USEPA also defines National Secondary
Drinking Water Regulations (secondary standards). Water is supplied to facilities within the project site by
the City. The vacation rental and Seascape restaurant’s wastewater is treated by above ground treatment
tanks with disposal via a leach field.

3.3

AIR QUALITY AND GREENHOUSE GAS

The following describes existing air quality conditions, including greenhouse gases (GHG) that occur
within the project site and general vicinity.

3.3.1 REGULATORY SETTING
CLEAN AIR ACT
The Federal Clean Air Act (CAA) was enacted for the purposes of protecting and enhancing the quality of
the nation’s air resources to benefit public health, welfare, and productivity. Basic components of the CAA
and its amendments include national ambient air quality standards (NAAQS) for major air pollutants and
state implementation plans (SIPs) to ensure country-wide NAAQS compliance. Regulation of air pollution
is achieved through both the NAAQS and emissions limitations for individual sources of air pollutants
established through permitting requirements. The USEPA is the federal agency responsible for identifying
criteria air pollutants (CAPs) for which NAAQS are established, updating and revising the NAAQS, and
approving and overseeing SIPs as they relate to compliance with the CAA. The USEPA has identified six
CAPs that are both common indicators of regional air quality and detrimental to human health. The six
CAPs are ozoneFDUERQPRQR[LGH &2 SDUWLFXODWHPDWWHU PLFURQVDQGPLFURQVLQGLDPHWHU
(PM10 and PM2.5)), nitrogen dioxide (NO2), sulfur dioxide (SO2), and lead. The NAAQS, appropriate
metrics, and violation criteria for the six CAPs are presented in Table 3-5.
Federal General Conformity
Under the General Conformity Rule of the CAA, recently updated in 2010, the lead agency with respect to a
federal action is required to demonstrate that a proposed federal action conforms to the applicable SIP(s)
before the action is taken. There are two phases to a demonstration of general conformity:
1) The Conformity Review process, which entails an initial review of the federal action to assess
whether a full conformity determination is necessary, and
2) The Conformity Determination process, which requires that a proposed federal action be
demonstrated to conform to the applicable SIP(s).
The Conformity Review requires the lead agency to compare estimated emissions attributable to the federal
action to the applicable general conformity de minimis threshold(s) for all CAPs for which the applicable air
basin or region is in nonattainment for the applicable NAAQS. If the emission estimate(s) from step one is
below the applicable de minimis threshold(s), then a General Conformity Determination is not required

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under the CAA (40 CFR Part 93). If emission estimates are greater than de minimis levels, the lead agency
must conduct a Conformity Determination.
TABLE 3-5
NATIONAL AMBIENT AIR QUALITY STANDARDS
Pollutant

Averaging Time

Ozone (O3) a

Primary NAAQS

Secondary NAAQS

1 hour

0.12 ppm

0.12 ppm

8 hour

0.08 ppm

0.08 ppm

1 hour
8 hour

35 ppm
9.0 ppm

NA
NA

Nitrogen Dioxide (NO2)

1 hour
Annual Mean

100 ppb
0.053 ppm

NA
0.053 ppm

Sulfur Dioxide (SO2)

1 hour

75 ppb

NA

3 hour

NA

0.05 ppm

24 hour

150 Pg/m3

150 Pg/m3

24 hour
Annual Mean

35 Pg/m3
12 Pg/m3

35 Pg/m3
15 Pg/m3

Quarterly Average

0.15 Pg/m3

0.15 Pg/m3

Carbon Monoxide (CO)

Respirable Particulate Matter (PM10)
Fine Particulate Matter (PM2.5)

Lead (Pb)

Note: a) Standard for existing ozone non-attainment area only
Source: EPA, 2011

Federal Class I Areas
Title 1, Part C of the CAA was established, in part, to preserve, protect, and enhance the air quality in
national parks, national wilderness areas, national monuments, national seashores, and other areas of special
national or regional natural, recreational, scenic, or historic value. The CAA designates all international
parks, national wilderness areas, and memorial parks larger than 5,000 acres and national parks larger than
6,000 acres as “Class I areas.” The CAA prevents significant deterioration of air quality in Class I areas
under the Prevention of Significant Deterioration (PSD) program. The PSD Program protects Class I areas
by allowing only a small increment of air quality deterioration in these areas by requiring assessment of
potential impacts on air quality related values of Class I areas. There are no federal Class I areas within or
adjacent to the project site; refer to Section 3.3.4 for further discussion.
Federal Hazardous Air Pollutant Program
Title III of the CAA requires the USEPA to promulgate National Emissions Standards for Hazardous Air
Pollutants (NESHAPs). The NESHAPs may differ between regional sources and area sources of hazardous
air pollutants (HAPs). Major sources are defined as stationary sources with potential to emit more than 10
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tpy of any HAP or more than 25 tpy of any combination of HAPs (all other non-major sources are
considered area sources under the NESHAPs program). HAPs are a specific group of airborne chemicals
designated by the USEPA. Sources of HAPs include industrial processes such as petroleum refining and
chrome plating operations, commercial operations such as gasoline stations and dry cleaners, and motor
vehicle exhaust. Cars and trucks release at least 40 different HAPs. The most important, in terms of health
risk, is diesel particulate matter (DPM), benzene, formaldehyde, 1,3-butadiene, and acetaldehyde.
HAPs are less pervasive in the urban atmosphere than CAPs, but are linked to short-term (acute) or longterm (chronic or carcinogenic) adverse human health effects. There are hundreds of different types of
HAPs, with varying degrees of toxicity. Currently, there are over 188 HAPs listed by the USEPA.
The majority of the estimated health risk from HAPs can be attributed to relatively few compounds, the
most important being DPM (CARB, 2005). Diesel engines emit a complex mixture of air pollutants,
composed of gaseous and solid material. The visible emissions in diesel exhaust are particulate matter that
includes carbon. Diesel exhaust also contains a variety of harmful gases and over 40 other cancer-causing
substances.
CLIMATE CHANGE
Federal
In 2002, President George W. Bush established a national policy goal of reducing the GHG emission
intensity (tons of GHG emissions per million dollars of gross domestic product) of the U.S. economy by
18% by 2012. No binding reductions were associated with the goal. Rather, the USEPA administers a
variety of voluntary programs and partnerships with GHG emitters, in which the USEPA partners with
industries producing and utilizing GHGs to reduce associated emissions.
Clean Air Act
In Massachusetts et al. vs. Environmental Protection Agency et al. (April 2, 2007), the US Supreme Court
ruled that the CAA authorizes the USEPA to regulate CO2 emissions from new motor vehicles. The Court
did not mandate that the USEPA enact regulations to reduce GHG emissions, but found that the only
instances where the USEPA could avoid taking action were if it found that GHGs do not contribute to
climate change or if it offered a “reasonable explanation” for not determining that GHGs contribute to
climate change. On December 15, 2009, the USEPA issued a final endangerment and cause finding (74 FR
66496), stating that high atmospheric levels of GHGs “are the unambiguous result of human emissions, and
are very likely the cause of the observed increase in average temperatures and other climatic changes.” The
USEPA further found that “atmospheric concentrations of GHG endanger public health and welfare within
the meaning of Section 202 of the Clean Air Act.” The finding itself does not impose any requirements on
industry or other entities.
U.S. Environmental Protection Agency
On December 7, 2009, USEPA Administrator Lisa Jackson signed a Final Action, under Section 202(a) of
the CAA, finding that six key well-mixed GHG constitute a threat to public health and welfare, and that the

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combined emissions from motor vehicles cause and contribute to the climate change problem. The
following are the most recent regulatory actions taken by the USEPA:


On July 23, 2009, the USEPA published a final “rule which proposes to establish the criteria for
including sources or sites in a Registry of Recoverable Waste Energy Sources (Registry),” as
required by the Energy Independence and Security Act of 2007. Waste energy can be used to
produce clean electricity. The clean electricity produced by waste energy would reduce the need
for non-renewable forms of electricity production, thus reducing GHG emissions.



On September 15, 2009, the USEPA and the Department of Transportation’s National Highway
Traffic Safety Administration (NHTSA) proposed a new national program that would reduce GHG
emissions and improve fuel economy for all new cars and trucks sold in the United States. The
USEPA proposed the first national GHG emissions standards under the Clean Air Act, and NHTSA
proposed an increase in the Corporate Average Fuel Economy (CAFE) standards under the Energy
Policy and Conservation Act.



In response to the FY2008 Consolidated Appropriations Act (H.R. 2764; Public Law 110–161), the
USEPA issued the Final Mandatory Reporting of Greenhouse Gases Rule. Signed by the
Administrator on September 22, 2009, the rule requires that suppliers of fossil fuels and industrial
GHGs, manufacturers of vehicles and engines outside of the light duty sector, and facilities that
emit 25,000 metric tons or more of GHGs per year to submit annual reports to the USEPA. The
rule is intended to collect accurate and timely emissions data to guide future policy decisions on
climate change.



On September 30, 2009, the USEPA proposed new thresholds for GHGs that define when CAA
permits under the New Source Review and title V operating permits programs would be required.



In December, 2014 The CEQ Chair released a memorandum, Revised Draft NEPA Guidance on
Consideration of the Effects of Climate Change and Greenhouse Gas Emissions. The
memorandum provides guidance on how project-related GHG emission should be analyzed in
NEPA documents. The Revised Draft Guidance provides that a NEPA climate change analysis
shall provide quantification and mitigation to reduce GHG emissions. The guidance also provides
that 25,000 metric tons of GHG emissions per year may be a helpful guideline to assist lead
agencies in making informed decisions on climate change impacts resulting from a project subject
to NEPA. The guidance notes that the 25,000 metric tons is not an indicator of a threshold of
significant effects, but rather, it is an indicator of a minimum level of GHG emissions that may
warrant some description in the appropriate NEPA analysis for agency actions involving emissions
of GHGs.

3.3.2 PROJECT AREA AND VICINITY
The project site is located in the North Coast Air Basin (NCAB), which extends for 250 miles from Sonoma
County in the south to the Oregon border in the north and east through Trinity County. The climate of the

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NCAB is influenced by two major topographic units: the Klamath Mountains and the Coast Range
provinces. Both provinces are marked by large areas of rugged, mountainous terrain. The coastal plains,
which are part of the Coast Range province, constitute less than 10 percent of the area of the NCAB but
contain the major industrial and population centers. The project site is located on the edge of the coastal
plain in the foothills of the Klamath Mountains.

3.3.3 REGIONAL AIR QUALITY
NAAQS DESIGNATIONS
As shown in Table 3-6, the NCAB is in attainment or is unclassified for all CAPs under the current
NAAQS designation.
TABLE 3-6
NCAB ATTAINMENT STATUS
Pollutant

NAAQS

Ozone

Attainment/ Unclassified

PM10

Attainment/ Unclassified

PM2.5

Attainment/ Unclassified

CO

Attainment/ Unclassified

NO2

Attainment/ Unclassified

SO2

Attainment

Lead

Attainment/ Unclassified

SOURCE: NCUAQMD, 2015.

POLLUTANTS OF CONCERN
Pollutants of concern are CAPs that are present in quantities exceeding the NAAQS in the applicable air
basin or region and air pollutants that are not designated as CAPs, such as CAP precursors (NOx and ROG),
yet can be temporarily present in high concentrations in a localized region of the SCCAB. No CAPs exceed
the NAAQS in NCAB and no CAP precursors would be temporarily present in high concentration in the
NCAB. Therefore, pollutants of concerns are not present in the NCAB.
HAZARDOUS AIR POLLUTANTS
The current operations at the project site do not meet the definition of a major source for HAPs. Operations
often involve idling diesel vehicles associated with the commercial fishing operations of the pier and result
in releases of DPM.

3.3.4 FEDERAL CLASS I AREAS
The nearest federal Class I area, Redwood Creek National Park, is located approximately 10 miles east of
the project site.
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3.3.5 GREENHOUSE GASES
The extent to which human activities affect global climate change is a subject of considerable scientific
debate. It is anticipated that the average global temperature could rise 0.6 to 4.0 oC (1.08 to 7.18 oF)
between the years 2000 and 2100 (IPCC, 2007). The Intergovernmental Panel on Climate Change (IPCC)
Fourth Assessment Report identifies anthropogenic GHGs as a contributing factor to changes in the Earth’s
climate (IPCC, 2007). To err on the side of caution, the analysis in this EA assumes anthropogenic GHGs
are in fact contributing to global climate change.
The Humboldt County Climate Action Plan includes a GHG inventory and establishes an emission
reduction target. The Climate Action Plan also identifies numerous goals and policies aimed at reducing
GHG emissions. These goals and policies are to be incorporated into the County of Humboldt General Plan
(County of Humboldt, 2012c).
Primary sources of GHG emissions in the region include vehicles, trucks, airplanes, mills, ships, canneries,
and electricity generation facilities. However, there are many other sources of GHG emissions in the
region.

3.3.6 SENSITIVE RECEPTORS
Sensitive receptors are facilities that house or attract children, the elderly, and people with illnesses or
others who are especially sensitive to the effects of air pollutants. Hospitals, schools, convalescent
facilities, and residential areas are examples of sensitive receptors.
The project site vicinity is characterized by low-density residential uses. One existing single family
residence (vacation rental) is present on the project site and is therefore the nearest sensitive receptor.
Construction would occur adjacent to this residence. The nearest off-site residence is located adjacent to
the northeastern boundary of the project site. The nearest school (Trinidad Elementary School) is located
approximately 0.4 miles northeast of the project site. There are no other types of sensitive receptors in the
vicinity of the project site.

3.4

BIOLOGICAL RESOURCES

The following describes existing biological resource conditions, including habitat conditions and listed
species that occur within the project site and general vicinity.
Existing biological resources were evaluated through a review of pertinent literature, consultation of
relevant databases, and biological field surveys to document habitat types and the potential occurrence for
federally listed species on the approximately nine-acre project site. Biological field assessments were
conducted by AES staff on November 19 and 20, 2015.

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3.4.1 REGULATORY SETTING
FEDERAL ENDANGERED SPECIES ACT
The USFWS and the National Marine Fisheries Service (NMFS) implement the Federal Endangered
Species Act of 1973 (FESA) (16 USC 1531 et seq.). Threatened and endangered species on the federal list
(50 CFR 17.11 and 17.12) are protected from “take” (direct or indirect harm), unless a Section 10 Permit is
granted or a Biological Opinion with incidental take provisions is rendered. Pursuant to the requirements of
FESA, an agency reviewing a proposed project within its jurisdiction must determine whether any federally
listed species may be present in the project area and determine whether the proposed project will have a
potentially significant impact upon such species. Under FESA, habitat loss is considered to be an impact to
the species. In addition, the agency must determine whether a project is likely to jeopardize the existence of
species or habitat for species proposed to be listed under FESA (16 USC 1536[3], [4]). USFWS also
designates species of concern. Species of concern receive attention from federal agencies during
environmental review, although they are not otherwise protected under FESA. Project-related impacts to
such species would also be considered significant and would require mitigation.
WATERS OF THE U.S.
Any person, firm, or agency planning to alter or work in navigable waters of the U.S., including the
discharge of dredged or fill material, must first obtain authorization from the United States Army Corps of
Engineers (USACE). Permits, licenses, variances, or similar authorization may also be required by other
federal, state and local statutes. Section 10 of the Rivers and Harbors Act of 1899 prohibits the obstruction
or alteration of navigable waters of the United States without a permit from the Corps of Engineers (33
U.S.C. 403). Section 301 of the Federal Water Pollution Control Act and Amendments of 1972 (Clean
Water Act or CWA) prohibits the discharge of pollutants, including dredged or fill material, into waters of
the United States without a Section 404 permit from USACE (33 U.S.C. 1344). Water Quality Certification
(a CWA Section 401 permit) may be required by the USEPA before other permits are issued.
MIGRATORY BIRD TREATY ACT
Most bird species, especially those that are breeding, migratory, or of limited distribution, are protected
under federal and state regulations. Under the Migratory Bird Treaty Act of 1918 (16 USC 703-711),
migratory bird species, and their nests and eggs, that are on the federal list (50 CFR 10.13) are protected
from injury or death, and project-related disturbances must be reduced or eliminated during the nesting
cycle.

3.4.2 ENVIRONMENTAL SETTING
The project site has a maritime climate regime with warm, temperate summers and cool, wet winters. The
vicinity of the project site is a rural residential area to the east-northeast, one residence to the adjacent west,
surrounding open space, coastal bluffs, and coastal shorelines. The terrain on the project site is rolling hills
with the parking lot being relatively flat. The remaining property ranges from hilly with low elevation

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changes to coastal bluffs with extreme elevation changes. The predominant geological features are the
Trinidad Head to the west, the Trinidad Bay to the west-southwest, and Little Head to the east. The area of
the City is characterized by steep coastline. Within the developed area of the City, the topography is
relatively flat with the coastal bluffs being the most dramatic changes in topography.
VEGETATIVE COMMUNITIES
Vegetative communities are assemblages of plant species that occur together in the same area that are
defined by species composition and relative abundance. Vegetation communities were classified using the
California Department of Fish and Wildlife (CDFW) Terrestrial Natural Communities of California system,
or “Holland type.” Habitat types occurring within the project site include ruderal/developed and coastal
scrub. These habitats are located within a close vicinity of urban residential and open spaces associated
with coastal bluffs and shoreline. A habitat map of the project site is presented as Figure 3-3.
Ruderal/Developed
Most of the project site consists of ruderal/developed land (Figure 3-3). Bay Street is a paved street that
connects to the site’s parking lot. Buildings and infrastructure are located on the site as described in
Section 2. Native vegetation surrounds the site and borders the site’s impervious surfaces.
Northern Coastal Scrub
Most of the undeveloped portions of the property are characterized by northern coastal scrub. Northern
coastal scrub is characterized by low shrubs in dense patches. Usually occurring on windy, exposed sites
with shallow and rocky soils. The most dominating species include Cascara (Frangula purshiana), Blue
Blossom (Ceonothus thyrsiflorus), Twinberry (Lonicera involucrate), and Silk Tassel (Garrya elliptica).
Associated native species include Douglas Iris (Iris douglasiana), Sticky Monkey Flower (Mimulus
aurantiacus), Evergreen Huckleberry (Vaccinium ovatum), Bracken Fern (Pteridium aquilinum var.
pubescens), Bee Plant (Scrophularia californica), and Wild Cucumber (Marah oreganum). Northern coastal
bluff scrub is less abundant and usually only occurs where there is high salt content, constant high winds,
and poor soil conditions. All flora is similar to Northern Coastal Scrub, however, many species are dwarfed
and highly influenced by high winds and salinity of the ocean. Common native species include Coyote
Brush (Baccharis pilularis), Salal (Gaultheria shallon), Leather Fern (Polypodium scouleri), Beach
Strawberry (Fragaria chiloensis), Pacific Stonecrop (Sedum spathulifolium), Ocean bluff blue grass (Poa
unilateralis), California Bentgrass (Agrostis densiflorus), and Alumroot (Heuchera micrantha).
WILDLIFE
A variety of wildlife utilize the habitats that occur on or near the project site. Species observed or identified
by physical evidence during the November 19 and 20, 2015 site visit include: black oyster catcher
(Haematopus bachmani), turkey vulture (Cathartes aura), mourning dove (Zenaida macroura), California
gull (Larus californicus), Swainson’s thrush (Catharus ustulatus), American robin (Turdus migratorius),
double-crested cormorant (Phalacrocorax auritus), and harbor seal (Phoca vitulina).

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Ewing St

Azale a Way

Galindo St

Pacific Ct

Edwards St

Property Boundary
Van Wycke St

Ba
y

St

Pie r

h
Lig
tho
us
eR
d

LEGEND
Property Boundary 9.38 ac
HABITAT TYPES
Coastal Scrub
Ruderal/Developed
Shoreline/Beach

¢

Ð

N O R TH

!

Feet

0

125

250

SOURCE: Humboldt County Parcel GIS Data, 2013;
DigitalGlobe aerial photograph, 6/6/2013; AES, 4/21/2016

Trinidad Rancheria Fee-to-Trust and Interpretive Visitor Center Project EA / 215569

Figure 3-3
Habitat Types

3.0 Affected Environment

MIGRATORY BIRD HABITAT
Although the project site does not contain suitable habitat for nesting birds, there is a potential for migratory
birds to occur directly adjacent to the project parcels on the shoreline and on the coastal bluffs.
POTENTIAL WATERS OF THE U.S.
There are no surface water features, outside of the ocean, that are present within the boundaries of the
project parcels that have the potential to be classified as waters of the U.S. or wetlands.

3.4.3 SPECIAL-STATUS SPECIES
For the purposes of this assessment, “special status” is defined to be species that are of management
concern to federal resource agencies and include those species that are:



Listed as endangered, threatened, or candidate for listing under the Federal Endangered Species
Act; or
Designated as species of concern or species of local concern by USFWS.

A list of special-status plant and animal species that have potential to occur on the project site was compiled
based on a review of pertinent literature, a reconnaissance-level site assessment, informal consultation with
the USFWS, and the results of a California Natural Diversity Data Base (CNDDB) query (Appendix D).
Based upon the review of regionally occurring special-status species and their habitat requirements and the
results of the field assessment, the project site and/or surrounding vicinity represents potential habitat for
one special-status plant species and three special-status animal species. The name, regulatory status, habitat
requirements, and period of identification for potentially occurring special-status species are identified in
Table 3-7.
WESTERN LILY
The western lily is a perennial herb that grows from a bulb. The species typically grows in bogs, freshwater
marshes, coastal scrub or prairie, or gaps in coniferous forest. It often grows in association with such
species as sundew (Drosera spp.), California rose-bay (Rhododendron marcrophyllum), California
huckleberry (Vaccinium ovatum), Labrador tea (Ledum groenlandicum), and red alder (Alnus rubra).
Populations are found within six miles of the coast and from near sea level to 320 feet amsl in elevation.
The western lily blooms from June through July (Hickman, 1993; CNPS, 2016). No western lilies were
observed during the December site visit. Since western lily often grows in association with other species
that were observed adjacent and to the west of the vacation rental, western lily has the potential to occur on
the project site.

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TABLE 3-7
POTENTIALLY OCCURRING FEDERAL SPECIAL-STATUS SPECIES
SCIENTIFIC NAME
COMMON NAME

FEDERAL
STATUS

PLANTS
Lilium occidentale
western lily

ANIMALS
Birds
Brachyramphus
marmoratus
Marbled Murrelet
Charadrius
alexandrinus nivosus
Western Snowy Plover
Mammals
Eumetopias jubatus
Steller Sea Lion

PERIOD OF
IDENTIFICATION

DISTRIBUTION

HABITAT REQUIREMENTS

FE

From Coos Bay in
Oregon to
Humboldt Bay in
California.

Bogs and fens, coastal bluff scrub, coastal
prairie, coastal scrub, freshwater marshes and
swamps, and openings within North Coast
coniferous forest habitat.

June - July

FT

From San
Francisco Bay to
Southern Alaska
From Mexico to
Southern
Washington

Breeding requires north coast conifer old
forests while foraging habitat requires shallow
shoreline and tidal pools.
Tidal pools and shallow tidal marshes, coastal
shoreline with or without shrubs.

Year-round

North Pacific from
Japan to Central
California

Rocky shores and haul-out areas in coastal
areas.

FT

FT

Year-round

NOTES: FEDERAL STATUS CODES: (U.S. Fish and Wildlife Service or National Marine Fisheries Service)
FE = Listed as Endangered by the Federal Government
FT = Listed as Threatened by the Federal Government
SOURCE: USFWS, 2016.

MARBLED MURRELET
The marbled murrelet is a small seabird found in the north pacific. It nests in old growth forests and
forages in shallow shoreline and tidal pools. They range from the San Francisco Bay area to Southern
Alaska along the Pacific coastline. Breeding habitat requirements include north coast conifer old growth
forests. Foraging habitats include shallow shoreline and tidal pools with bare beaches and some rocky
outcroppings in shallow bays. Although breeding habitat is not located on or adjacent to the proposed
project site, potential foraging habitat is located directly adjacent to the site and therefore marbled murrelet
as the potential to occur on the project site.
WESTERN SNOWY PLOVER
The western snowy plover is a small shorebird near the size of a sparrow. During the breeding season,
March through September, plovers are present on shores, peninsulas, islands, bays, estuaries, and rivers of
the Pacific coast, especially beaches and shores with plenty of wrack (debris). Breeding on the California
Coast occurs between March and June. Although the prime habitat for snowy plover has been designated in
on the shoreline of San Luis Obispo and Santa Barbara Counties, snowy plover have the potential to occur
on the project site.
STELLER SEA LION (EUMETOPIAS JUBATUS) (EASTERN DPS)
Steller sea lions are found around the rim of the North Pacific Oceana and in the Bering Sea. This includes
Northern California, Oregon, Washington, Canada, and Alaska along with some spotted in Japan. Like all
eared seals, Steller sea lions hunt at sea and return to shore to rest, breed, and give birth. Steller sea lions

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can be found in rookeries and haul-outs. Rookeries are the breeding colonies where reproduction occurs.
Haul-outs are where animal rest on shore but no reproduction occurs on haul-outs. Breeding season occurs
between June and July. Due do potential rookeries and haul-outs on or near the project site, the Steller sea
lion has the potential to occur.

3.5

CULTURAL RESOURCES

Archaeological studies of the project site were conducted in 2011 by Donald Verwayen of the Humboldt
State University Cultural Resources Facility for the reconstruction of the Trinidad Pier and by AES in
November 2015; the Verwayen report is included as Appendix E under a separately bound cover due to the
sensitive nature of the material addressed. Verwayen’s study included both a field survey and literature
search to identify and evaluate potential prehistoric and historic resources. The AES effort included a field
verification of the Verwayen results and a Native American contact program. Historic-era archaeological
resources, built resources, a paleontological deposit, and several Traditional Cultural Properties were
identified during these efforts.

3.5.1 REGULATORY SETTING
NATIONAL REGISTER OF HISTORIC PLACES
The eligibility of a resource for listing in the NRHP is determined by evaluating the resource using criteria
defined in 36 CFR 60.4 as follows: The quality of significance in American history, architecture,
archaeology, and culture is present in districts, sites, buildings, structures, and objects of state and local
importance that possess integrity of location, design, setting, materials, workmanship, feeling, association,
and:
A. That are associated with events that have made a significant contribution to the broad patterns of
our history;
B. That are associated with the lives of persons significant in our past;
C. That embody the distinctive characteristics of a type, period, or method of construction, or that
represent the work of a master, or that possess high artistic values, or that represent a significant
and distinguishable entity whose components may lack individual distinction; or
D. That have yielded, or may be likely to yield, information important to prehistory or history.
Sites younger than 50 years, unless of exceptional importance, are not eligible for listing in the NRHP.
In addition to meeting at least one of the criteria listed above, the property must also retain enough integrity
to enable it to convey its historic significance. The National Register recognizes seven aspects or qualities
that, in various combinations, define integrity. These seven elements of integrity are: location, design,
setting, materials, workmanship, feeling, and association. To retain integrity a property will always possess
several, and usually most, of these aspects.

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While most historic buildings and many historic archaeological properties are significant because of their
association with important events, people, or styles (criteria A, B, and C), the significance of most
prehistoric and some historic-period archaeological properties is usually assessed under criterion D. This
criterion stresses the importance of the information contained in an archaeological site, rather than its
intrinsic value as a surviving example of a type or its historical association with an important person or
event. It places importance not on physical appearance but rather on information potential.
NATIONAL HISTORIC PRESERVATION ACT
Section 106 of the National Historic Preservation Act (NHPA) as amended, and its implementing
regulations found in 36 CFR Part 800, require federal agencies to identify cultural resources that may be
affected by actions involving federal lands, funds, or permitting. The significance of the resources must be
evaluated using established criteria outlined in 36 CFR 60.4, as described below.
If a resource is determined to be a historic property, Section 106 of the NHPA requires that effects of the
federal undertaking on the resource be determined. A historic property is defined as:
…any prehistoric or historic district, site, building, structure or object included in, or eligible for inclusion
in the National Register of Historic Places, including artifacts, records, and material remains related to
such a property (NHPA Sec. 301[5])…
Section 106 of the NHPA prescribes specific criteria for determining whether a project would adversely
affect a historic property, as defined in 36 CFR 800.5. An impact is considered adverse when prehistoric or
historic archaeological sites, structures, or objects that are listed, or eligible for listing, in the NRHP are
subjected to the following:








Physical destruction of or damage to all or part of the property;
Alteration of a property;
Removal of the property from its historic location;
Change of the character of the property’s use or of physical features within the property’s setting
that contribute to its historic significance;
Introduction of visual, atmospheric, or audible elements that diminish the integrity of the property’s
significant historic features;
Neglect of a property that causes its deterioration; and
Transfer, lease, or sale of the property out of federal control without adequate and legally
enforceable restrictions or conditions to ensure long-term preservation of the property’s historic
significance.

If the historic property will be adversely affected by development, then prudent and feasible measures to
avoid or reduce adverse impacts must be taken. The State Historic Preservation Officer (SHPO) must be
provided an opportunity to review and comment on these measures prior to project implementation.

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TRADITIONAL CULTURAL PROPERTIES
The 1992 amendments to the NHPA allowed for a new designation of a traditional cultural property (TCP).
The amendment established "Properties of traditional religious and cultural importance to an Indian tribe or
Native Hawaiian organization" may be determined eligible for inclusion in the NRHP (Section 101(d)(6) of
the NHPA. Accordingly, a tribal TCP can only be significant and eligible for listing on the NRHP if it
meets two criteria: 1) rooted in that community’s history; and 2) are important in maintaining the
continuing cultural identity of the community”.

3.5.2 METHODOLOGY
RECORDS AND LITERATURE SEARCH
Background research for the Proposed Action and Project were taken from the Verwayen report, which also
covered the entire APE for the Proposed Action and Proposed Project. The records search and literature
review for this study were completed: (1) to determine whether known cultural resources had been recorded
within or adjacent to the study area; (2) to determine whether known resources have been reported in
archaeological, ethnographic, and historical documents and literature; and (3) to assess the likelihood of
unrecorded cultural resources based on the distribution of nearby archaeological sites in relation to their
environmental setting.
The following inventory and databases were included in the review: National Register of Historic Places,
California Register of Historical Resources, California Inventory of Historic Resources, California
Historical Landmarks, California Historic Highway Bridge Inventory, Humboldt Room of the Humboldt
State University Library, County Recorder’s Office at the Humboldt County Court House, and historic
maps.
Verwayen’s record search results included only one ethnographic resource, the Yurok village site of Tsurai
on Trinidad Bay (CA-HUM-169), east of the Proposed Action APE, and a fossil locality on the western end
of the Proposed Action APE. Twenty-one cultural resource surveys have been completed within the record
search area, three shipwrecks have been noted in Trinidad Bay, and a single historical resource, a logging
skid road associated with the Smith and Dougherty Trinidad Mill Company, is nearby but not eligible for
listing on the NRHP.
Verwayen’s 2011 cultural survey recorded eight resources, Around Chicken Hawk’s Place, a TCP on
Trinidad Bay that includes several individual loci; remnants of a whale skidway; the Trinidad Pier; the mid19th century Trinidad Dump, a multi component site that included historic debris and prehistoric lithic
artifacts and trade beads; Muggay’s Grave; Tibbett’s Grave; a marine railway, and a soapstone quarry. Two
of these were determined to be eligible for the NRHP: Around Chicken Hawk’s Place under Criterion A for
its association with events that have made a significant contribution to the broad patterns of history; and
Criterion B for association with the lives of persons significant in our past. The whale skidway was found

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eligible under Criterion C as it embodies the distinctive characteristics of type, period, or method of
construction, or that represent the work of a master, or that possess high artistic values, or that represent a
significant and distinguishable entity whose components may lack individual distinction.
Two of the Around Chicken Hawk’s Place TCP loci are within the Proposed Action APE. These are
Chicken Hawk’s House on Little Head and Chicken Hawk’s Boat, on the small peninsula east of Little
Head. The whale skidway, Trinidad Pier, the marine railway, the dump, Tibbett’s and Muggay’s graves,
the soapstone quarry, and the paleontological deposit are also all within the Proposed Action APE.
Charlane Gross, M.A., RPA and AES Staff Archaeologist, conducted a cultural resources field survey of the
project site on November 19-20. The portions of the APE that were accessible were limited. The APE
largely consisted of paved parking areas, steep, heavily vegetated embankments, the pier, or inaccessible
geographic features such as Little Head/Chicken Hawk’s House and Chicken Hawk’s Boat. The only areas
truly accessible for archaeological review were located west and northwest of the Seascape Restaurant and
the beaches on either side of Trinidad Pier; these areas were surveyed using transects 5-10 meters apart.
The two grave sites, soapstone quarry, and mid-19th century dump were either covered by dense vegetation
or gone, as no evidence for any of these sites could be found. No new resources were identified.
NATIVE AMERICAN CONSULTATION
Verwayen (2011) contacted the Native American Heritage Commission (NAHC) and attempted to contact
the individuals listed by the NAHC in 2011 with no specific results. A new search request was sent to the
NAHC on November 5, 2015 by AES. Results were received on November 24, 2015 and are appended to
Verwayen report and are included in Appendix E. Letters were sent to those individuals identified by the
NAHC on November 30, 2015. To date, no responses have been received. A consultation log is included
in Appendix E.

3.5.3 EXISTING FIELD CONDITIONS
The area where the stormwater improvements would be developed and the visitor’s center would be placed
are already developed, with a combination of asphalt, shipping containers, sheds, utility boxes, sewer
manholes, fire hydrants, and barricade posts, thoroughly disturbing any potential buried cultural resources.
None of the physical resources or TCP elements are within Bay Street, the parking lot, or the visitor’s
center footprints, and none should be affected by project construction.

3.6

SOCIOECONOMIC CONDITIONS / ENVIRONMENTAL JUSTICE

The following section provides the existing socioeconomic conditions and regional setting to evaluate
environmental justice considerations for the project parcels.

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3.6.1 TRINIDAD, HUMBOLDT COUNTY
POPULATION
The City had a population of approximately 236 people (Table 3-8) (U.S. Census 2014a) according to 5year estimates for population. Humboldt County had a population estimate of approximately 14,876 people
whereas the State of California had a population of 38,066,920. Trinidad’s population is approximately
0.18 percent of the population of Humboldt County, and approximately 0.0006 percent of California’s
population. Over the next 20 years, the County’s population is expected to grow from approximately
134,876 to approximately 139,780 (California Department of Finance, 2016.)
TABLE 3-8
TRINIDAD, HUMBOLDT COUNTY, CALIFORNIA DEMOGRAPHICS
Trinidad
Humboldt County

2009-2014 5-Year Estimates1
236
134,876

California

38,066,920

SOURCE: U.S. Census, 2014a
1Total populations

EMPLOYMENT
The labor force in Trinidad is approximately 149 people of which 143 are employed (Table 3-9). The labor
force in the County is approximately 66,449 people of which 58,868 are employed. The unemployment
rate for Trinidad is 3.4 percent whereas Humboldt County is 11.3 percent (0.3 percent over the State of
California.)
TABLE 3-9
TRINIDAD, HUMBOLDT COUNTY, CALIFORNIA EMPLOYMENT
In Labor Force1
Employed
Unemployment Rate

Trinidad
149
143
3.4%

Humboldt County
66,449
58868
11.3%

California
19,098,427
16,883,249
11.0%

SOURCE: U.S. Census, 2014b
116 years and over population

3.6.2 CHER-AE HEIGHTS INDIAN COMMUNITY OF TRINIDAD RANCHERIA
Statistics for the Tribe were obtained from the Bureau of Indian Affairs’ American Indian Population and
Labor Force Estimate Report, 2005 (Table 3-10; note that the 2013 report does not provide the
socioeconomic statistics of the Tribe).

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TABLE 3-10
CHER-AE HEIGHTS INDIAN COMMUNITY OF TRINIDAD RANCHERIA ESTIMATES
Total
Tribal Enrollment
171
American Indians on or near Reservation
231
Under age 16
43
Age 16 through 64
131
Over age 64
12
Available for work
128
Unavailable for work
15
Employed in Public Sector Positions
11
Employed in Private Sector Positions
72
Employed but Below the Poverty Line
0
SOURCE: BIA, 2005.

3.6.3 ENVIRONMENTAL JUSTICE FOR MINORITY AND LOW INCOME POPULATIONS
On February 11, 1994, President Clinton issued Executive Order 12898, “Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income Populations,” and an accompanying
Presidential Memorandum to focus federal attention on the environmental and human health conditions in
minority communities and low-income communities. The Executive Order, as amended, directs federal
agencies to develop an Environmental Justice Strategy that identifies and addresses disproportionately high
human health or environmental effects of their programs, policies, and activities on minority populations
and low-income populations. Compliance with this Executive Order has been incorporated into the NEPA
compliance requirements of the BIA for the Proposed Action.
The City is located within the census block group 060230102002 with a population of 650 people. The
total population that is reported as “low income” is approximately 30 percent (195 people) which is five
percent lower than the State estimation of low income population (EPA, 2016).
The County is approximately 18.4 percent minority (Table 3-11). In the County, American Indians make
up 5.74 percent of the population, including members of the Tribe.
TABLE 3-11
HUMBOLDT COUNTY RACE/INCOME PROFILE
Total
Race/Ethnic Population 2010
White
Hispanic
American Indian
Multi-Race
Asian
Black
Pacific Islander
Household Median Income 2007-2011
Poverty Status (All Ages)

134,623
104,373
13,211
6,9

[Text truncated at 120,000 characters. The full text is on the page linked above.]

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Source: Frix Law Library, https://www.frixlaw.com/law-library/documents/tribal%3Acher-ae_heights%3A10eb985573888d56. Public record. Not legal advice.
