HomeMy WebLinkAbout04/11/2017 02 Comprehensive Plan 2040 Update with Planning Commission MembersBUSINESS OF THE CITY COUNCIL
YAKIMA, WASHINGTON
AGENDASTATEMENT
Item No. 2.
For Meeting of: April 11, 2017
ITEM TITLE: Comprehensive Plan 2040 Update with Planning Commission
Members
SUBMITTED BY: Joseph Calhoun, Planning Manager (509) 575-6042
Joan Davenport, AICP, Community Development Director
SUMMARY EXPLANATION:
1. Planning Commission Quarterly Report
2. Comprehensive Plan 2040 Update
a. Introduction, S E I S, Comment Period, Next Steps (Calhoun)
b. 2040 Comprehensive Plan Elements (Berk/Makers)
c. 2040 Transportation Systems Plan (Transpo)
d. Development Regulations (Calhoun)
e. Evening Open House (Calhoun)
Please bring your previously provided printed copies of the Supplemental Environmental Impact
Statement (2.a), 2040 Comprehensive Plan (2.b), Capital Facilities Plan (2.b), and 2040
Transportation Systems Plan (2.c), and to the meeting. Materials can be located here:
https://www.yakimawa.gov/services/planning/comprehensive-plan-update/
ITEM BUDGETED:
STRATEGIC PRIORITY: Neighborhood and Community Building
APPROVED FORV*
SUBMITTAL: City Manager
STAFF RECOMMENDATION:
BOARD/COMMITTEE RECOMMENDATION:
ATTACHMENTS:
Description
2.a 2.b 2040 Comp Plan Presentation
2.c Transportation Systems Plan Presentation
2.d de,,elopment regs
Upload Date
Type
4/3/2017
Presentation
4/3/2017
Presentation
4/6/2017
Coker Memo
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PlanningCITY OF YAKIMA
City of Yakima
Comprehensive Plan Unrlate
Joint City Council/Planning Commission Study Session
We a1le Iftdanmr
comprehensive plan 2040
April 11, 2017
/SwN. I " Va &wal
plan integral de la comunidad 2040
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We a1le Iftdanmr
comprehensive plan 2040
April 11, 2017
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plan integral de la comunidad 2040
Topics
Purpose of the update
Timeline and next steps
Element highlights
Yakima Urban Area
Comprehensive Plan 2025
December 2006
Final Adopted Version
400
Purpose of the Update
Required by the Growth Management Act (GMA)
Guides Yakima's physical development over 20 or
more years - 2040
.zstablishes land use plan that is implemented by
zoning and other programs
• Plans for Yakima's long term expected growth targets
in population (17.,167)., and jobs (8.,556)
Coordinates services and capital investments
Addresses community values, city functions
Provides a statement of policy
Required to receive state funding
Plan Elements
• Land Use
• Economic Development
• Housing
• Transportation
• Capital Facilities
• Utilities
• Parks and Recreation
• Natural Environment
• Energy
• Historic Preservation
Timeline and Next Steps
2015
• Public Participation Plan —
Identify process and key
stakeholders
• Create Comp Plan Specific
Webpage
• Consultant Selection
2016
• Council workshop — 2/23/16
• Visioning Open House
meeting and Community
Survey — 5/25/16
• Existing Conditions Report
• Establish Future Land Use
Designations and
Implementing Zones
• Draft element review by
Planning Commission
• Buildable Lands Analysis
• Environmental Scoping
DIRECTIONS: Please comment using words, drawings, and suggestions from the provided exampic
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City of Yakima Comprehensive Plan 2040
Welcome!
COMMUNITY VISION
OPEN HOUSE
2017
• Finalize draft elements and
Environmental Impact
Statement
• Invite public comment
(March 17 —May 16)
• Joint Planning
Commission/Council Study
Session (April 11)
• Public Open House (April 11)
• Planning Commission Hearing
(May 10)
• City Council Hearing (June 6)
FE -11 FR
F 11
SOM0.0
vahitim
Ciudad de Yakima
Actualization del Plan Integral de Yakima 2040
iEstas Invitado!
CASA ABI ERTA PARA LA VISION DE LA COM UNIDAD
CLIANDO: 23 DE FEBRERO, 2016 DE LAS 6 P.M. -8 P.M.
Presentation comienza a las 6:30 p.m.
DONDE: YAKIMA VALLEY TECHNICAL SKILLS CENTER -
1120 al Sur de la Calle 18, Yakima, WA 98901
E
Integrated Supplemental Environmental
,,1,;1;
■ 11
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1'N
Impact Statement (SEIS) We �2�«1�.,a
comprehensive plan 2040
SEIS is an informational document
Addresses potential effects of
projects and plans, including
Comprehensive Plan
Due to policy nature of plan, SEIS is
broad and covers 20 -year view
The SEIS builds on past City EIS
documents in 2006
Studies proposed growth and
policies
I
SEIS integrated with
Comprehensive Plan
• Avoids duplication
• Streamlines documents
• Coordinates public review
60 -day comment period on Draft
SEIS
Following public and agency
comments a Final SEIS will be
prepared
I
EM
Background Data
Terms
■ Vision: A community's best desired
future.
■ Value: A standard or judgment of what
is important for the community.
■ Goal: A broad, general statement of
the desired long-term future state or
outcome, toward which the Plan aims.
Goals indicate what ought to exist in a
community or what is desired to be
achieved in the future.
■ Policy: A principle, protocol, or
proposal for action that implements a
related goal. Decision -oriented
statements that guide the legislative or
administrative body while evaluating a
new project or proposed change in
ordinance.
■ Regulation: A rule or directive found in
City ordinances or the municipal code.
■ Program: Ongoing delivery of
municipal services to the public,
funded with the municipal budget, or
public investments guided by a capital
improvement strategy.
Population and Jobs — Target vs.
Capacity
Jobs 2012.2444 1 $,��
ZS,A94
MMM",1167Popwation 2015-20 044,817
10,040 20,000 30,004 40,000 50,004
■ Target ■ Capacity
Capacity by district
District
Capacity:Agriculture
New Homes New lobs
1
401
9,384
2
1,102
2,8oS
3
1,004
2,360
4
407
1,499
5
1,312
2,087
6
2,297
75
7
8,995
6,624
Citywide
15,518
24,837
Vacant
Potentiallnfill 22
I21
Agriculture
151
Underutilized ■.
141
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IIII III
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comprehensive plan
2040
City wide
buildable
lands by
type
500 1, _
827
767
0 Gross Acres 0 Net Acres
2,000 2,500 3,D00
2,758
2,403
Element Highlight — Land Use
Yekxne
Yakima Urban Area
/� I QYak me CityLmits Medlem Densdy Resldenhal_ Neighborhood Ccmmeraal_ CBD Core Commemai Comprehensive Plan
/Ifs Yakima Urban Growth Area High Density residential Large Convenience CelHer_ReponelCanmercial
Lar Density R-hic till P-resslmal Olfice Arterial Commercial _Industrial
Future Land Use
Old Plan
• 1:1 Future Land Use (FLU) and Zoning
• 10 FLU Designations
• Most changes go through a lengthy
amendment process
III LAND USE
Yakima Compreikensive Plan 2040
New Plan
• Streamlined Future Land Use (FLU)
and Zoning
• 7 FLU Designations
• More options for new development
lc
raii
p
s _
I ..n.w+ - •" "" C • Yapma G15
Oomber. 2016
The Generalized Future Land Use Map illustrates the combination of current land use, ourrent zoning, and future uses of each parcel of land within the City or Yakima. These categories have been wnsolicatetl W
better visualize mixed residential, neighborhood commercial and mixed commercial uses. The map category is necessary to provide certainty to the community members, residents, and property owner about
what type of land use will be located around them. And, where to expect future services, and development based on the goals, policies and objectives of this Plan 2040.
YAKIMA 2040
COMPREHENSIVE
PIAN UPDATE
Future Land Use
Categories
■ Central Business Core Commercial
Commercial Mixed Use
industrial
Low Density Residential
Mixed Residential
■ Community Mixed Use
■Regional Commemal
Yakima Council District
Yaklma City Limits
Urban Growth Area
N
A
0 Q5 1 L5 Miles
li it hili rl
Element Highlight — Economic
. (--nnl.onaonl.,e..nn....en.,.,.k Development
2017-2020 Economic Development
Strategic Plan
• Continuation of Cascade Mill Site
Goals — Important for LIFT Funding
• Support of Downtown Revitalization
efforts and Community Pride
initiatives
35,000 31,560
30,000
25,000
20,000 17,167 16,260
15,000 8,556
10,000
5,000 -
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
NEW JOBS CAPACITY
1L%
1
34%
2
12%
ECONOMIC DEVELOPMENT
Yakima Comprehensive Plan 2040
Element Highlight -Housing HOUSING
isYakima Comprehensive Plan 2040
• Goals and Policies promote a diversity
of housing choices
• Supportive of upper -floor downtown
residential
• New Goal — "Foster a caring
community that nurtures and
supports individuals, children, and
their families"
NEW HOMES CAPACITY
2
3
6% 4
2%
5
35,000 31,560 8/ rp�_
30,000
25,000
20,000 17,167 16,260 6
15,000 15% f
10,000 8,556 ig
J5,000 w
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
E
Element Highlight - Transportation
• Goals and Policies promote multi-
modal transportation
• I ntegrates with the 2040
Transportation Systems Plan
• Level of Service (LOS) analysis for key
intersections
• Project list based on 2040 Traffic
Forecasts and planned projects
• Maps for truck routes/freight
corridors; auto, bike/ped priority;
traffic volumes; etc.
35,000 31,560
30,000
25,000
20,000 17,167 16,260
15,000 8,556
10,000
5,000
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
Legend
Functional Classification
Principal Arterial
— Minor Arterial
or
—Futu-e Principal
.... Future Principal Arterial `v(
•••. Future Minor Arterial _
® City Traffic Signal
e"'I City Limits
UGA Boundary
Park / Open Space
111 1119 jjy
TRANSPORTATION
Yakima Comprehensive Pion 2040
---
— — r--=
gLLf
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� ■ l
0 J 0.5 Miles -
Roadway Functional ClaSSftation
City of Yakima 2040 Transportation Plan
0
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],V-, \, -,I I
DRAFT FIGURE
transpo r 4-2
10
Element Highlight —Capital �o e CAPITAL FACILRIES
Facilities Yakima Com"°'`nsi" Plan '°°°
• Inventory of city owned facilities —
water, sewer, fire, police, etc.
• Identifies project funding and
revenue sources
• Estimates future needs based on
growth targets
• Implements the Capital Facilities Plan
35,000 31,560
30,000
25,000
20,000 17,167 16,260
15,000 8,556
10,000
5,000 -
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
11
Capital Facility Plan Appendix CAPITAL FACILITIES
OYakima Plan _opo
• Plan for infrastructure and services
• Serve community today
• Support future growth
• Ensure facilities are in place or have funding
commitments
• Support growth at desired Levels of Service
• Coordinated with existing budget, system
plans, and departments
• Addresses 6 & 20 year periods
• Revenue analysis:
• Identifies dedicated capital funds in 6
and 20 years
• Shows other revenue sources are needed
(common to local governments today)
12
Element Highlight - Utilities
• Inventory of electricity, natural gas,
and telecommunications providers
• Goals and Policies that coordinate
future development with utility
providers
35,000 31,560
30,000
25,000
20,000 17,167
15,000
10,000
5,000
Population 2015-2040
■Capacity ■Target
16,260
8,556
Jobs 2012-2040
13
❑n 2040
2 _
_�lo+: J
Element Highlight -
Natural Environment
and Shorelines
• Updated mapping for Floodplains,
Wetlands and Streams, Wildlife,
Geologic Hazards, and Aquifers
• Goals and Policies consistent with
Best Available Science
• Incorporated Shoreline Element Goals
and Policies adopted in 2014 by City
of Yakima/Department of Ecology
35,000 31,560
30,000
25,000
20,000 17,167 16,260
15,000 8,556
10,000
5,000 -
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
NATURAL ENVIRONMENT' qP
�.� Yakima Comprehensive Plan 2040
y 60 _ 68
Exhibit 9-2. Floodplains — City of Yakima
SHORELINE
Yakima Comprehensive Plan 2040
YAKIMA 2o4o
b
COMPREHENSWE
it
PLAN UPDAM
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.c...a.quo'�..mr.v�,..n....uly.iar.r.,w�.n...y«a.. r.�. �inw•. u...,u�rrni....r i.. ru.�e --. ry..n fw..u..�r.x..'r.rws�4
Element Highlight - Energy f
• New Element — Optional under GMA
• Includes goals and policies that
encourage alternative energy sources
Geothermal heating
Liquid runs through
(solar, for
pipes sunk into the
earth and drays
wind, geothermal) new
warmth from the
constant
temperature there.
development and re -development
The heal is aped
into an indoor unit
projects
and dreulated
thrcugh the house.
outing warmer
months, the same
system helps
_
cod the house.
I I
35,000 31,560
30,000
25,000
20,000 17,167 16,260
15,000 8,556
10,000
5,000 -
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
ENERGY
Yakima Comprehensive Plan 2040
11111111111111F
16
Element Highlight — Historic
• Optional Element under GMA
• Includes goals and policies, consistent
with the Historic Preservation Plan,
that promote the awareness,
protection, and rehabilitation of
historic sites and structures
• Identifies potentially eligible
properties
35,000 31,560
30,000
25,000
20,000 17,167 16,260
15,000
8,556
10,000
5,000 -
Population 2015-2040 Jobs 2012-2040
■Capacity ■Target
Preservation
HISTORIC PRESERVATION
", Yakima Comprehensive Plan 2040
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Exhibit 12-2. Potentially Eligible Properties
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.�i. a,..MM.ud auwc1h-10ollpllnrpa 1111 .xm in}ar
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.nis nww.a •O.• F ra+rw.4 � "
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Legend
• 1A: potentially individually eligible to the National Register of Historic Places
• 1B: potentially contributing to a National Register of Historic Places eligible
historic district
• 1C: potentially eligible for local designation, but not to the National Register
• 1D: potentially contributing to a local historic district
• 2A: not eligible, with conditions
• 28: not eligible
Source: Artifacts Consulting Inc. 2016
Questions?
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Plaii'n`Ing
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comprehensive plan 2040
Yakima Urban Area
Comprehensive Plan
Adopted April 1997
Includes Amendments Thru 2003
PrMlb Aupu.12004
ot`Y1
Yakima Urban Area
Comprehensive Plan 2025
December 2006
Final Adopted Version
Yakima Urban
Area
Transportation
Plan Update,
2025
Adopted by Yakima City
Council
December 12, 20013
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Yakima Urban Arca Comprehensive & Transportation Plan
2012 Addendum
CITY OF YAKIMA
2040 TRANSPORTATION SYSTEM PLAN
Prepared for,
City of Yaldma
Prepared by;
Tra_,_nspo Group
transpogroup �r
WHAT TR NSPORTATION CAN BE
11738 118w Avenue NE, Suite 688
Kirkland, WA 98834-7128
Phone: 425-821-3665
Fax- 425-825-8434
w,vwlranspoyroun.com
15254A8
® 2817 Jaansgg Group
16
CITY OF YAKIMA
Transportation Element and
Transportation Systems Plan
Presented by
transpogroup �r
WHAT TRANSPORTATION CAN BE.
Transportation Element Objectives
• Meet requirements of the Growth Management Act
(GMA)
• Support overall Comprehensive Plan and City vision
• Integrate and prioritize transportation improvements
serving all modes
• Review level of service standards
• Update transportation funding analyses
and strategies
• Review and update transportation policies
Presented by
transpo r
LEVEL OF DETAIL
W
0
N
N
W
J
J
W
0
W
W
0
2
noz
Planning Process
Roadway/Intersection
Traffic Modeling
Pedestrian/Bicycle
Transit
Freight
Financing Strategies
' o ()03o
Evaluate existing (2014) Prepare travel Define multimodal Update Documentation and
transportation forecasts (2040) and improvement projects transportation environmental
systems conditions evaluate options policies review
and issues
Presented by
transpogroup �r
Balancing the Plan
Multimodal
Improvements
• Improve corridors
• Improve intersections
• Pedestrian, bicycle,
transit
• Maintenance &
preservation
Presented by
transpogroup �r
Concurrency/LOS
• Intersection -based LOS standard
• Measures adequacy of Finance
facilities/services
• Timing of facilities/services
• Existing/historical
transportation revenues
• Bonding
• Grants
• Developer mitigation
Travel Forecasts and Alternatives Evaluation
• Applied YVCOG model with updated land
use
• Intersections limit corridor capacity
• Forecast traffic growth focused in northeast
quadrant
• Emphasize vehicle mobility in key corridors
that connect to regional facilities
• Emphasize other modes in parallel corridors
Presented by
transpogroup �r
Travel Context Priorities
Modal priority by corridor
• Auto
L" -d
• Bike/Ped
• Shared„
Truck Routes I
gay°tea
cnr umis...k R.-
�
Truck Route Classification
Presented by
Travel Context Classification DRAFT FIGURE
transpogroup cJr a.... �,,. m� M, 4-3
DRAFT FIGURE
—,wo, yr 4-4
System Plans
Highway and Streets
Pedestrian System
Bicycle System
Presented by
transpogrcup rjr
.1
W,gh,vvat's a❑St
= System Plan
X1
DRAFT ria
4-5
LS Pede t Sy tem Plan
,,DRAFT
seueF
Pi n
,d Bicycle System Plan DRAFT
Transportation Improvement Projects
Project Types
LegendImp\
e
• Intersections
mems ..m emem
m �IYe-,a�,Pp�F
• Active Transportation
® RoatlwaY Imp p'remert
® N�Ro .
-
• Study
RaazNmy
• Roadway Improvement
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• New Roadway
Pa O,e S'.e
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Timeframe
1
kl-
• Short-Range (2015-2020)
=-
-
• Mid-Range (2021-2030)
• Long-Range (2031-2040)
_
Presented by
Transportation Improvement Projects
DRAFT FIGURE
ranspogroup 1`�ir
CdV of Yakima 2040 Transpartafian Plan
trenspogrwp'fr 4-9
Financing Program — Summary
2015 to 2040 (2015 Dollars)
Total Project Cost: $256.3 million
M
1W
New Roadway
86.1 m
Presented by
transpogrcup cjr
Roadway Improvements
75.5m
•
Intersection
72.7m
Active Transportation Study
20.1 m 1.9m
11
Patrick Lynch, AICP
Brent Turley, PE
425.821.3665
patrick.lynch@transpogroup.com
brent.turley@transpogroup.com
Transpo Group
2017 Development Regulations Update
City of Yakima
2017 GMA Updates
32
YMC Chapter 14.20.160 SUBDIVISION.......................................................................................................... 2
YMC Chapter 15.06 OFF STREET PARKING AND LOADING........................................................................... 2
YMC Chapter 15.27 CRITICAL AREAS............................................................................................................ 2
YMC Title 17 SHORELINES...........................................................................................................................44
The Yakima Municipal Code is current through Ordinance 2015-047, passed December 8, 2015.
Page 1/69
33
2017 Development Regulations Update
YMC Chapter 14.20.160 SUBDIVISION
14.20.160 Preliminary Plat -Expiration of approval -Extension -Conditions.
A. Approval of preliminary plats of proposed subdivisions shall expire €i,e year -s- in accordance with the timelines
below from the date of city council approval thereof. The council shall, upon written application of the subdivision
applicant at least 30 days prior to such expiration, grant an extension for a maximum period of one year upon a
showing that the applicant has attempted in good faith to submit the final plat within the five yeaf pefiedsubmission
timeline. The timeline to submit a final plat is as follows:
1. Seven (7) years if the date of preliminary plat approval is on or before December 31, 2014.
2. Five (5) years if the date of preliminary plat approval is on or after January 1, 2015.
3. Ten (10) years if the project is located within city limits, not subject to the shoreline management act, and
the preliminaa plat is approved on or before December 31, 2007.
YMC Chapter 15.06 OFF STREET PARKING AND LOADING
15.06.035 Electric Vehicle Charging Stations.
A. Electric Vehicle Charging Stations, as defined by RCW 36.70A.695(5), or as amended, shall be allowed as
follows, except for on resource lands or in critical areas:
1. An accessory use to an approved principal use in the B-1, B-2, HB, SCC, LCC, CBD, GC, M-1, M-2, RD,
and AS zoning districts.
2. As a right-of-way use permit in public parking lots and/or on -street public parking areas.
YMC Chapter 15.27 CRITICAL AREAS
Part Five. Fish and Wildlife Habitat aPA the St -ea CoFi4do - S ste Conservation Areas
Article IV. Wa+er Pepe Acne. Pep elopm^^* StaP aaFds ^^dBuffer Requirements
15.27.540 USO Gla%if4ea4iol4s
15.27.54 i Wa+e - depe , epA „sos
15.27.512 Water- e!a+e a ,
15.27.543 Nof . ,^.o . , epAe a uses.
15.27.5140 Vegetative buffers.
Article V. Land Modification Development Standards
15.27.51-51
Roads, railroads, and parking.
15.27.5162
Utility transmission lines and facilities.
15.27.51-73
MBank stabilization.
15.27.5184
Dredging and excavation.
15.27.5145
Filling.
15.27.52.816
Commercial mining of gravel.
15.27.5-217
Reclamation.
15.27.120 Purpose of chapter.
The purpose of this chapter is to establish a single, uniform system of procedures and standards for development
within designated critical areas outside of shoreline jurisdiction within the incorporated city of Yakima-affd4s-uflfln
gR,A4h are . (Ord. 2008-46 § 1 (part), 2008).
The Yakima Municipal Code is current through Ordinance 2015-047, passed December 8, 2015.
Page 2/69
34
2017 Development Regulations Update
15.27.130 Intent of chapter.
A. This chapter establishes policies, standards, and other provisions pertaining to development within designated
critical areas regulated under the provisions of the Growth Management Act (RCW 36.70A) and development
regulated under the National Flood Insurance Program. Flood hazard areas, fish and wildlife habitat conservation
areas, wetlands, geologically hazardous areas,and 1x'^*'—A. ^. ^^m^ s4e m ^ . 4dE)r^ aP ^ ; areas with a
critical recharging effect on aquifers used for potable water; � sh aPA .. ildl & h^b44 eoi4seFN,a4ioi4 areas; 4 ^,,,, nt ,
flooded ^ rA geolo foal 4ai�afdotis areas constitute the city of Yakima's critical areas pursuant to WAC 365-
190-030. These areas are of special concern to the people of the city of Yakima and the state of Washington because
they are environmentally sensitive lands, or hazardous areas, which comprise an important part of the state's natural
resource base. The policies, standards, and procedures of this chapter are intended to:
1. Preserve development options within designated critical areas where such development will result in the
level of "no net loss" of the functions and values of the critical areas;
2. Where appropriate, avoid uses and development which are incompatible with critical areas;
3. Prevent further degradation of critical areas unless the degradation has occurred beyond feasible
protection;
4. Conserve and protect essential or important natural resources;
5. Protect the public health, safety, and general welfare;
6. Further the goals and policies of the =7 Comprehensive Plan 204OYal4m^ ,, baa area eompfehe ^ pb9m;
7. Implement the goals and requirements of the Washington Growth Management Act (RCW 36.70A), and
the National Flood Insurance Program (CFR Title 42);
8. Recognize and protect private property rights; and
9. Provide development options for landowners of all existing lots to the greatest extent possible, through the
establishment of adjustment, reasonable use, and nonconforming use and facility provisions.
B. The policies, standards and procedures of this chapter are not intended to:
1. Regulate the operation and maintenance of existing, legally established uses and structures, including but
not limited to vegetative buffers on existing uses that have been reduced in width prior to the effective date of
this chapter;
2. Result in an unconstitutional regulatory taking of private property;
3. Require the restoration of degraded critical areas for properties in a degraded condition prior to the
effective date of this chapter, unless improvement of the buffer is needed for new development proposed on the
property;
4. Presume that regulatory tools are the only mechanism for protection; or
5. Prohibit the use of valid water rights. (Ord. 2008-46 § 1 (part), 2008).
15.27.140 Applicability.
A. The provisions of this chapter shall apply to any new development, construction, or use within the incorporated
portion of the city of Yakiesignated as a critical
area and upon any land mapped and designated as a special flood hazard area under the National Flood Insurance
Program. However, this chapter does not apply to the situations below, except that the flood hazard protection
provisions of Part Four of this chapter will continue to apply as determined by YMC 15.27.400 through 15.27.406:
The Yakima Municipal Code is current through Ordinance 2015-047, passed December 8, 2015.
Page 3/69
35
2017 Development Regulations Update
1. Within designated critical areas, there may exist lots, structures, and/or uses which were lawfully
established prior to the adoption of this chapter, as provided below, but which would be subsequently
prohibited, regulated, or restricted under this chapter. Such existing lots, structures, and/or uses shall be
classified as legally nonconforming uses.
2. It is the intent of this chapter to permit these pre-existing legally nonconforming uses and structures to
continue until such time as conformity is possible:
a. Critical areas on federally owned lands are not subject to the provisions of this chapter;
b. Minor, temporary, or transient activities (including those of a recreational nature) that do not alter the
environment or require a dedicated staging area, use area, or route (including temporary signs) are not
subject to this chapter;
c. Mining, as defined in YMC 15.27.200, which is carried out under a Washington Department of
Natural Resources reclamation permit is not subject to the geologically hazardous areas provisions of this
chapter for erosion hazard areas, oversteepened slope hazard areas, landslide hazard areas and suspected
geologic hazard areas. Other critical areas provisions continue to apply.
B. The adoption and amendment dates of the relevant regulations are provided below:
1. Critical areas ordinance adopted 1998;
2. Flood hazard ordinance adopted 1981; and
3. Other rules and regulations, including the city of Yakima subdivision ordinance (YMC Title 14), the city of
Yakima urban area zoning ordinance (YMC Title 15), and the buildings ordinance (YMC Title 11), shall
remain in full force and effect as they apply to a designated critical area. Wherever the requirements of this
chapter conflict with the requirements of the Yakima urban area zoning ordinance, the subdivision ordinance or
any other lawfully adopted municipal rules or regulations, the most restrictive standards shall apply. (Ord.
2008-46 § 1 (part), 2008).
15.27.200 Definitions generally.
Definitions listed in Part Two of this chapter shall be applied to the regulation, review, and administration of all
critical areas, including flood hazard areas, unless the definition itself identifies the term as applying to flood hazard
administration, in which case the definition only applies to that situation.
`Bank stabilization" means the construction or modification of bulkheads, retaining walls, dikes, levees, riprap,
breakwaters, jetties, groins, weirs, and other structures along a bank, for the purpose of controlling stream
undercutting or bank erosion.
"Breakwater" means a fixed or floating ^mein -water structure that protects the shefe-bank from the forces of
waves or currents.
"Bulkhead" means a vertical or nearly vertical erosion protection structure placed parallel to the show—bank
consisting of concrete, timber, steel, rock, or other permanent material not readily subject to erosion.
"Fill" means the addition of any material, such as (by way of illustration) earth, clay, sand, rock, gravel, concrete
rubble, rubble, wood chips, bark, or waste of any kind, which is placed, stored or dumped upon the surface of the
ground resulting in an increase in the natural surface elevation. The physical structure of a bankshefe stabilization
structure shall not be considered fill. However, fill placed behind the structure is considered fill. Stream bed
manipulation for irrigation diversions shall not be considered fill.
"Fish and wildlife habitat conservation'' means land management for maintaining populations of species in suitable
habitats within their natural geo apWe distribution so that the habitat available is sufficient to support viable
populations over the long term and isolated subpopulations are not created. This does not mean maintaining all
individuals of all species at all times, but it does mean not degrading or reducing populations or habitats so that they
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are no longer viable over the long term. Counties and cities should engage in cooperative planning and coordination
to help assure long term population viability.
"Fish and wildlife habitat conservation areas" are areas that serve a critical role in sustaining needed habitats and
species for the functional integrity of the ecosystem, and which, if altered, may reduce the likelihood that the species
will persist over the long term. These areas may include, but are not limited to, rare or vulnerable ecological
systems, communities, and habitat or habitat elements including seasonal ranges, breeding habitat, winter range, and
movement corridors: and areas with high relative population density or species richness. Counties and cities may
also designate locally important habitats and species. Fish and wildlife habitat conservation areas does not include
such artificial features or constructs as irrigation deliversystems, irrigation infrastructure, irrigation canals, or
drainage ditches that lie within the boundaries of, and are maintained by, a port district or an irrigation district or
compaM.
"Habitats of local importance" are designated as fish and wildlife habitat conservation areas based on a finding by
the city that they are locally important.
_44ydrologiealb, rvla+ed ef4ieal areas (14RGA)" iRePdde all those areas idepAiAed 44 Y44C 15.27.502, whiek are
impoi4apA aPA desepi,ing of pr-oteetioi4 by Hal+tr-e of their- N,altw for- the ftmetional pr-opefties fouPA 44 )444c= 15.27.
"Ordinary high water mark" means a mark on lakes and streams which can be found by examining the bed and
banks and ascertaining where the presence and action of waters are so common and usual, and so long continued in
ordinary years as to mark upon the soil or vegetation a character mafk upoi4 the so"istinct fromthat-of-the
abutting upland. Provided, that in any area where the ordinary high water line cannot be found, the ordinary high
water line is the elevation of the mean annual flood.
"Perennial stream" means a stream that flows year-round in normal water years.
"Priority habitat" means a habitat type with unique or significant value to one or more species. An area classified
and mapped as priority habitat must have one or more of the following attributes: comparatively high fish or
wildlife density, comparatively high fish or wildlife species diversity, fish spawning habitat, important wildlife
habitat, important fish or wildlife seasonal range, important fish or wildlife movement corridor, rearing and foraging
habitat, refuge, limited availability, high vulnerability to habitat alteration, unique or dependent species, or shellfish
bed. A priority habitat may be described by a unique vegetation type or by a dominant plant species that is of
primary importance to fish and wildlife. A priority habitat may also be described by a successional stage.
Alternatively, a priority habitat may consist of a specific habitat element (such as talus slopes, caves, or snags) of
key value to fish and wildlife. A priority habitat may contain priority and/or nonpriopAy fish and wildlife.
"Priority species" means species regw�protective measures and/or management guidelines to ensure their
persistence at genetically viable population levels. Priority species are those that meet any of the criteria listed
below:
A. Washington State (State) Listed or State Proposed Species. State -listed species are those native fish and
wildlife species legally designated as endangered (WAC 232-12-014), threatened (WAC 232-12-011), or
sensitive (WAC 232-12-011). State proposed species are those fish and wildlife species that will be reviewed
by WDFW (POL-M-6001) for possible listing as endangered, threatened, or sensitive according to the process
and criteria defined in WAC 232-12-297.
B. Vulnerable Aggregations. Vulnerable aggregations include those species or groups of animals susceptible to
significant population declines, within a specific area or statewide, by virtue of their inclination to congregate.
C. Species of Recreational, Commercial, and/or Tribal Importance. Native and nonnative fish, shellfish, and
wildlife species of recreational or commercial importance and recognized species used for tribal ceremonial and
subsistence purposes that are vulnerable to habitat loss or degradation.
D. Species listed under the federal Endangered Species Act as either proposed, threatened, or endangered.
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"R040FO" MeaHS R) FO 04abkSh the basie ftmetiopal pr-opefties listed 44 YMG 15.2:7.504 #wt have beei4 lost o
toxie to .1
of 44e per-Hlit-..
"Restore," "restoration" or "ecological restoration" means the reestablishment or upgrading of impaired functions,
such as those listed in YMC 15.27.504 that have been lost or destroyed through natural events or human activity.
This may be accomplished through measures including, but not limited to, revegetation, removal of intrusive
structures, and removal or treatment of toxic materials. Restoration does not imply a requirement for returning the
site to aboriginal or pre -European settlement conditions.
"Revetment" means a facing placed on a bank or bluff to protect a slope, embankment, or slier -e structure against
erosion by wave action or currents.
"Scour" means the removal of underwater material by waves and currents, especially at the base or toe of a s
bank stabilization or other in -water structure.
"Shoreline," as used in this chapter, means those water areas, the associated features, and the land areas that are
subject to the State Shoreline Management Act, as defined in RCW 90.58.030 and the city of Yakima's current
shoreline master program (4e4P44e*sYMC 17.01.090).
tIpAeFetAgRg, stream eF04014 OF law sh
"Species of local importance" are those species that are of local concern due to their population status or their
sensitivity to habitat alteration or that are game species.
" Stream eoFi4doF," as used 44 this ehapteF, meai4s featwes listed aPA deseFibed 44 Y44C 15.27.
"Vegetative buffer" or "buffer" means an area extending landward from the ordinary high water mark of a lake or
stream and/or from the edge of a wetland which is maintained or otherwise allowed to provide support for the
performance of the basic functional properties of a fish and wildlife habitat conservation area
wetland and other hydrologically related critical areas as set forth in YMC 15.27.504 and 15.27.603.
"Waters of the state" are all lakes, rivers, ponds, streams, inland waters, underground waters, salt waters, and all
other surface waters and watercourses within the jurisdiction of the state of Washington.
15.27.301 Critical area identification form and critical area report requirements.
.,,,,a 2 (MaFeh 2006 oF as "d4ed). (04 2004 4 6 i (raA) 2009)
15.27.303 Minor activities allowed without a permit or exemption.
D. Creation of private trails that are less than two feet wide that do not cross streams or wetlands that are less th
*-T e -and do not involve placement of fill or grubbing of vegetation;
G. Noxious weed control outside vegetative buffers identified in YMC 15.27.5141; and
15.27.304 Documented exemption—Procedural requirements.
F. The proponent of an exempt activity shall submit a written request for a documented exemption which states the
following:
1. Why the exemption is being sought.
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2. A project description that demonstrates the following:
a. The sequence of activities to be conducted;
b. The equipment to be used (hand or mechanical);
c. The best management practices to be used;
d. The efforts employed to minimize adverse impacts; and
e. Restoration for disturbed areas and mitigation for lost critical areas functions following the activity;
15.27.305 Documented exemptions for fish and wildlife habitat conservation
areas and wetlands.
E. Construction of a dock in a non -shoreline waterbodv for the use of a single-family or multiple -family residence;
K. A public or private project to improve fish or wildlife habitat or fish passage in a non -shoreline waterbodv, if:
15.27.307 Mitigation requirements.
D. If an alteration to a critical area is unavoidable, all adverse impacts to that critical area and its buffers shall be
mitigated for in accordance with an approved mitigation plan
,,a 2 (MaFeh 2006 , as pda+ed); and
E. Except as specified in YMC 15.27.605, N4mitigation shall be in-kind and on-site, whenever possible, and may
be out -of -kind and/or off-site when deemed appropriate by the administrative official or designee. (Ord. 2008-46 § 1
Article V. Critical Areas Reports
15.27.314 Critical areas report requirements.
M. Compensatory Mitigation Plans. When compensatory mitigation, as described in YMC 15.27.307, is proposed
for wetlands or fish and wildlife habitat conservation areas ^r s+,.ea ^h^ the applicant shall submit a
mitigation plan as part of the critical area report, which includes:
15.27.315 Supplemental report requirements for specific critical areas.
A. Fish and Wildlife Habitat Conservation Areas&r-ea ., GoR4d r^ When a critical areas report is required for a
fish and wildlife habitat conservation areMtr-e m ^ ..:d^r or- h dr-ologioal . rvla+ed ^^+i^^' are it shall include the
following:
3. A discussion of any federal, state or local management recommendations which have been developed for
the species or habitats in the area, and how they will be incorporated into the project.
B. Wetlands. When a critical areas report is required for wetlands, it shall include the following:
1. The exact location of a wetland's boundary and wetland rating as determined through the performance of a
field investigation by a qualified wetland professional applying the approved federal wetland delineation
manual and applicable regional supplementsWashi ^+^^ c+„+o We#ap,a ldenti foe ,tioi ,,,,,a r,&Hea ioi ",r^,,,,,,'
(Eeolog5, P44ea4iot4 No 96 °^` as required by RCW 36.70A.175 and the most recent version of the
Washington State Wetland Rating System for Eastern Washington;
E.— Critical Aquifer Recharge Areas. The approach of the City critical area regulations is to require a level of
study and analysis commensurate with potential risks to wellhead protection zones associated with particular sites
and particular proposals. At a minimum, all applicants shall review the history of the site and conduct a surface
reconnaissance. The purpose of a critical aquifer recharge area report is to evaluate the actual geologic conditions
and determine the site's proximity to or location within a wellhead protection zone, evaluate the safety and
appropriateness of proposed activities: and recommend appropriate construction practices, monitoring programs, and
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other mitigation measures required to ensure achievement of the purpose and intent of these regulations. The
information required by this report should be coordinated with the study and reporting requirements for any other
critical areas located on the site. A critical aquifer recharge area report shall be prepared by a qualified professional
who is a hydrogeologist, geologist, or engineer who is licensed in the State of Washington and who has experience
in preparing hydrogeologic assessments.
1. Level One Hydrological Assessment: At sites located within Wellhead Protection Zones 1 through 3
defined in Section 15.27.820.A.1, a critical aquifer recharge areas report shall contain a level one hydrological
assessment which includes the following site- and proposal -related information at a minimum:
a. Information regardingeog_logic and hydrogeologic characteristics of the site, including the
surface location of all critical aquifer recharge areas located on-site or immediately adjacent to the site, and
permeability of the unsaturated zone based on existing data.
b. Groundwater death. flow direction. and eradient based on available information
c. Currentiv available data on wells and Mrines within 1.300 feet of the broiect area
d. Location of other critical areas, including surface waters, within 1,300 feet of the project site.
e. Available historic water quality data for the area to be affected by the proposed activity.
f BMPs proposed to be utilized.
2.— Level Two Hydrogeologic Assessment.
a. A level two hydrogeologic assessment shall be required for any of the following= proposed
activities at sites located within Wellhead Protection Zones 1 through 3:
i. Activities that result in 5,000 square feet or more impervious site area.
ii. Activities that divert, alter, or reduce the flow of surface or groundwaters, including
dewatering or otherwise reduce the recharging of the aquifer.
iii. The storage, handling, treatment, use, production, recycling, or disposal of deleterious
substances or hazardous materials, other than household chemicals used according to the directions
specified on the packaging for domestic applications.
iv. The use of injection wells, including on-site septic systems, except those domestic septic
systems releasing less than 14,500 gallons of effluent per day and that are limited to a maximum
density of one system per one acre.
v. Any other activity determined by the Director of Community Development likely to have an
adverse impact on groundwater quality or quantity, or on the recharge of the aquifer.
b. A level two hydrogeologic assessment shall include the following site and proposal -related information
at a minimum, in addition to the requirements for a level one hydrogeological assessment:
i. Historic water quality and elevation data for the area to be affected by the proposed activity
compiled for at least the previous five-year period.
ii. Groundwater monitoringplanprovisions.
iii. Discussion of the effects of the proposed project on the groundwater quality and quantity,
including:
(a) Predictive evaluation of groundwater withdrawal effects on nearby wells and surface
water features.
(b) Predictive evaluation of contaminant transport based on potential releases to
groundwater.
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iv. Identification of the type and quantities of any deleterious substances or hazardous materials
that will be stored, handled, treated, used, produced, recycled, or disposed of on the site, including but
not limited to materials, such as elevator lift/hydraulic fluid, hazardous materials used during
construction, materials used by the building occupants, proposed storage and manufacturing uses, etc.
v. Proposed methods of storing any of the above substances, including containment methods to
be used during construction and/or use of the proposed facility.
vi. Proposed plan for implementing YMC 15.27.820. C.3.f, Protection Standards During
Construction.
vii. A spill plan that identifies equipment and/or structures that could fail, resulting in an impact.
Spill plans shall include provisions for regular inspection, repair, and replacement of structures and
equipment that could fail.
viii. A complete discussion of past environmental investigations, sampling, spills, or incidents that
may have resulted in or contributed to contaminated soil or groundwater at the site. Attach copies of
all historical and current reports, and sampling results.
15.27.317 Adjustment.
A. Classification Criteria. For projects not required to be processed under RCW Chapter 90.58 (Shoreline
Management Act) and Title 17 YMC (Shoreline Master Program Regulations), the administrative official or
designee is authorized to administratively adjust the development standards. Existing structures, parcel size,
property boundaries, and other constraints may preclude conformance with building setbacks and vegetative buffers.
Given such constraints, administrative adjustments may be authorized where the site plan and project design include
measures to ensure the protection and performance of the functional properties identified in YMC 15.27.504.
^ djustmeRts Vegetative buffer standards listed 4 Tables 2:7.5 ' aPA be reduced to the minimum
buffer width 4stedprovided in YMC 15.27.510 and 15.27.604. Reductions below the minimum may be considered
but require stricter criteria be met in subsection (C)(4) of this section. Adjustments to prohibited use limits are not
allowed.
C. Decision Criteria. Decisions on adjustment permits shall be based on the general decision criteria found in
YMC 15.27.3 11 together with the criteria below.
f. The use of buffer averaging or buffer enhancement plans by the applicant using native vegetation or
other measures to enhance the functions and values of the fish
and wildlife habitat conservation area or wetland.
3. When granting an adjustment, the administrative official or designee may require, but is not limited to, the
following alternative measures to protect the functions and values of the fish and wildlife habitat conservation
area or wetlandHR-GA:
a. Restoration of impaired channels and banks to conditions which support natural stream flows, fish
habitat, and other values;
b. Restoration, enhancement, and preservation of soil characteristics and the quantity and variety of
native vegetation;
c. Provisions for erosion control and the reduction and filtration of stormwater runoff e4rinto the fish and
wildlife habitat conservation area, wetland, or buffer;
d. Removal or alteration of existing manmade facilities associated with stream channels or drainage
ways which improve stream flow or exchange of surface waters;
e. Replacement of lost fish and wildlife habitat conservation area and wetland functions and
values.,.^,,.,, eeFi4der-f ,,.wes- ^ aH aefe�ar-aer-e basis ,,,,,a r-eplaeomef4 of lost .. etla & in accordance
with
Washi ,g4, o , State nags i ,,,,,a 2 (MaFeh 2006 ^ as plate)best available science;
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f. Conservation easements for key portions of fish and wildlife habitat conservation areas, wetland, or
buffers stream ^^�do fepe, �, and/or their inclusion within public or private conservation programs; or
g. Vegetative buffer averaging may be modified by averaging buffer widths. Buffer averaging is
preferred in the use of mitigation sequencing (YMC 15.27.307) over a reduction in the buffer standards.
4. The following additional criteria must be met to reduce the critical areas stream and wetland buffers fou
4 Tables 2:7.5 1 aP 2:7.5 2 below the minimum 4stedidentified in YMC 15.27.5 10 and 15.27.604 44 the
Fespeetive tables:
15.27.401 Principles.
Part Four recognizes the right and need ofd river and stream channels to periodically carry more than the normal
flow of water and establishes regulations to minimize loss of life and property, restrict uses and regulate structures
consistent with the degree of flood hazard. In advancing the above principles, the intent of Part Four is:
Article III. Floodway Fringe Uses
15.27.409 Permitted uses.
The following uses are permitted in the floodway fringe areas:
A Po..miffe Uses Any use permitted in the zoning district in accordance with this title, unless prohibited by
YMC 15.27.410, provided, that said use is in compliance with the flood hazard protection standards of YMC
15.27.407 and 15.27.408 and other applicable provisions of this chapter and will have a negligible effect upon the
floodwav in accordance with the floodwav encroachment Drovisions of YMC 15.27.412(B):
B. All new encroachments. including fill. new construction and other develoDment_ if certification by a registered
professional engineer is provided demonstrating through hydrologic and hydraulic analysis performed in accordance
with standard engineering practice that the effect of the subject encroachment together with the cumulative effects of
all similar potential encroachments shall not materially cause water to be diverted upland of the established
floodway fringe, cause erosion, obstruct the natural flow of water, reduce the carr ing capacity of the floodway, or
result in anv increase in flood levels during the occurrence of the base flood discharge:
C. All new encroachments. including fill. new construction and other develoDment. if:
1. The new encroachment is seDarated from the waterbodv by an existing Dublic roadwav or legal develobment.
2. The new encroachment is located in a residential zone with a densitv of greater than 1 unit Der acre
ED. Utility Transmission Lines. Utility transmission lines shall be permitted when consistent with this title and
where not otherwise inconsistent with Part Four of this chapter; except that when the primary purpose of such a
transmission line is to transfer bulk products or energy through a floodway fringe or special flood hazard area, such
transmission line shall conform to the following:
1. Electric transmission lines shall cross floodway fringe and special flood hazard areas by the most direct
route feasible. When support towers must be located within floodway fringe or special flood hazard areas, they
shall be placed to avoid high floodwater velocity and/or depth areas, and shall be adequately floodproofed.
2. Buried utility transmission lines transporting hazardous materials, including but not limited to crude and
refined petroleum products and natural gas, shall be buried a minimum of four feet. Such burial depth shall be
maintained within the floodway fringe or special flood hazard area to the maximum extent of potential channel
migration as determined by hydrologic analyses. All such hydrologic analyses shall conform to requirements of
YMC 15.27.411(4�D)(3).
3. Beyond the maximum extent of potential channel migration, utility transmission lines transporting
hazardous and nonhazardous materials shall be buried below existing natural and artificial drainage features.
4. Aboveground utility transmission lines, not including electric transmission lines, shall only be allowed for
the transportation of nonhazardous materials. In such cases, applicants must demonstrate that line placement
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will have no appreciable effect upon flood depth, velocity or passage. Such lines shall be adequately protected
from flood damage.
5. Aboveground utility transmission line appurtenant structures, including valves, pumping stations or other
control facilities, shall not be permitted in floodway fringe or special flood hazard areas except where no other
alternative is available, or in the event a floodway fringe or special flood hazard location is environmentally
preferable. This does not apply to domestic water and regional wastewater transmission pipes. In such instances,
aboveground structures shall be located so that no appreciable effect upon flood depth, velocity or passage is
created, and shall be adequately floodproofed. (Ord. 2008-46 § 1 (part), 2008).
E. Any use permitted in the zoning district in accordance with this title, unless prohibited by YMC 15.27.410, that
is unable to adhere to the standards contained in YMC 15.27.409(A -D) above may be permitted if a study is
prepared by a qualified professional, in accordance with YMC 15.27.314, that addresses whether the encroachment
would have an adverse impact on fish and wildlife and/or floodplain functions.
15.27.410 Prohibited uses.
The following uses are prohibited in the floodway fringe areas:
A. Any structure, including manufactured homes and the expansion of manufactured home/parks, designed for or to
be used for human habitation of a permanent nature (including temporary dwellings authorized by YMC 15.04.130
and 15.04.140) that does not meet the criteria in YMC 15.27.409(A -E):
B. Any encroachments, including fill, new construction and other development, unless certification by a registered
professional engineer is provided demonstrating through hydrologic and hydraulic analysis performed in accordance
with standard engineering practice that the effect of the subject encroachment together with the cumulative effects of
all similar potential encroachments shall not materially cause water to be diverted upland of the established
floodway fringe, cause erosion, obstruct the natural flow of water, reduce the carr ing capacity of the floodway, or
result in anv increase in flood levels during the occurrence of the base flood discharge:
C_Gopist - etio^ or Reconstruction of residential structures within the designated floodway fringe, except for:
1. Repairs, reconstruction, or improvements to a structure which do not increase the ground floor area: and
2. Repairs, reconstruction or improvements to a structure, the cost of which does not exceed flft percent of
the assessed value of the structure either:
a. Before the repair, reconstruction or improvement is started: or
b. If the structure has been damaged and is being restored, before the damage occurred.
3. Work done on structures to correct existing violations of existing health, sanitaa or safety codes, or to
structures identified as historic places, shall not be included in the fifthpercent.
4. If subsection B of this section is satisfied, all new construction and substantial improvements shall comply
with all applicable flood hazard reduction provisions of Part Four.
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Article IV. Floodway Uses
43
15.27.411 Permitted uses.
The following uses are permitted in the floodway areas:
A. Any use permitted in the zoning district in accordance with this title; provided, that said use is in compliance
with the flood hazard protection standards of YMC 15.27.407 and 15.27.408 and other applicable provisions of this
chapter and will have a negligible effect upon the floodway in accordance with the floodway encroachment
provisions of YMC 15.27.412(B). Pori,: 4euses nelu e:
AB. All new encroachments, including fill, new construction and other development %_if certification by a
registered professional engineer is provided demonstrating through hydrologic and hydraulic analysis performed in
accordance with standard engineering practice that the effect of the subject encroachment together with the
cumulative effects of all similar potential encroachments shall not materially cause water to be diverted from the
established floodway, cause erosion, obstruct the natural flow of water, reduce the carrying capacity of the
floodway, or result in any increase in flood levels during the occurrence of the base flood discharge;
9C. Surface mining; provided, that the applicant can provide clear evidence that such uses will not divert flood
flows causing channel -shift or erosion, accelerate or amplify the flooding of downstream flood hazard areas,
increase the flooding threat to upstream flood hazard areas, or in any other way threaten public or private properties.
When allowed, such removal shall comply with the provisions of this title;
ED. Utility transmission lines, unless otherwise prohibited by this chapter; except that when the primary purpose
of such a transmission line is to transfer bulk products or energy through a floodway en route to another destination,
as opposed to serving customers within a floodway, such transmission lines shall conform to the following:
1. All utility transmission lines shall cross floodways by the most direct route feasible, as opposed to
paralleling floodways;
2. Electric transmission lines shall span the floodway with support towers located in flood fringe areas or
beyond. Where floodway areas cannot be spanned due to excessive width, support towers shall be located to
avoid high floodwater velocity and/or depth areas, and shall be adequately floodproofed;
3. Buried utility transmission lines transporting hazardous and nonhazardous materials, including but not
limited to crude and refined petroleum products and natural gas, shall be buried a minimum of four feet below
the maximum established scour of the waterway, as calculated on the basis of hydrologic analyses. Such burial
depth shall be maintained horizontally within the hydraulic floodway to the maximum extent of potential
channel migration as determined by hydrologic analyses. In the event potential channel migration extends
beyond the hydraulic floodway, conditions imposed upon floodway fringe and special flood hazard areas shall
also govern placement. All hydrologic analyses are subject to acceptance by the city of Yakima, which shall
assume the conditions of a one -hundred -year frequency flood as verified by the U.S. Army Corps of Engineers,
and shall include on-site investigations and consideration of historical meander characteristics in addition to
other pertinent facts and data. mp as pAeF eoPAa ^me^* meehap; sm .. ; hii toe h dfa+ he
4. Beyond the maximum extent of potential channel migration, utility transmission lines transporting
hazardous and nonhazardous materials shall be buried below existing natural and artificial drainage features;
and
5. Aboveground utility transmission lines, not including electric transmission lines, shall only be allowed for
the transportation of nonhazardous materials where an existing or new bridge or other structure is available and
capable of supporting the line. When located on existing or new bridges or other structures with elevations
below the one -hundred -year flood level, the transmission line shall be placed on the downstream side and
protected from flood debris. In such instances, site-specific conditions and flood damage potential shall dictate
placement, design and protection throughout the floodway. Applicants must demonstrate that such
aboveground lines will have no appreciable effect upon flood depth, velocity or passage, and shall be
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adequately protected from flood damage. If the transmission line is to be buried except at the waterway
crossing, burial specifications shall be determined as in subsection (C)(3) of this section;
44E. Construction or reconstruction of residential structures only as authorized in YMC 15.27.412(E);
EF. Improvements to existing residential structures that are not substantial improvements per YMC 15.27.200,
provided the improvement complies with the requirement set forth in YMC 15.27.412(B);
FG. Water -dependent utilities and other installations which by their very nature must be in the floodway.
Examples of such uses are: dams for domestic/industrial water supply; wastewater treatment and collection systems;
stream crossings or wetlands; flood control and/or hydroelectric production; water diversion structures and facilities
for water supply; irrigation and/or fisheries enhancement; floodwater and drainage pumping plants and facilities;
hydroelectric generating facilities and appurtenant structures; and structures and nonstructural uses and practices;
provided, that the applicant shall provide evidence that a floodway location is necessary in view of the objectives of
the proposal; and provided further, that the proposal is consistent with other provisions of this chapterafdkes
shoo hHe masteF pFogfam In all instances of locating utilities and other installations in floodway locations, project
design must incorporate floodproofing and otherwise comply with subsection ED of this section; and,
G. Pikes a �♦e-appn. eaQe-e�Qecetbat:
H. Roads and bridges, subject to the regulations of subsections (C)(1) through (5) of this section. (Ord. 2008-46 §
1 (part), 2008).
15.27.412 Prohibited uses.
The following uses/developments are prohibited in the floodway:
A. Any structure, including manufactured homes, designed for or to be used for human habitation of a permanent
nature (including temporary dwellings authorized by YMC 15.04.130 and 15.04.140);
B. Any encroachments, including fill, new construction and other development,> ^'sunless certification by
a registered professional engineer is provided demonstrating through hydrologic and hydraulic analysis performed in
accordance with standard engineering practice that the effect of the subject encroachment together with the
cumulative effects of all similar potential encroachments shall not materially cause water to be diverted from the
established floodway, cause erosion, obstruct the natural flow of water, reduce the carrying capacity of the
floodway, or result in any increase in flood levels during the occurrence of the base flood discharge;
C. Aboveground utility transmission line appurtenant structures, including valves, pumping stations, or other
control facilities, shall not be permitted in the floodway, except for domestic water and regional wastewater facilities
where necessary;
D. Where a floodway has not been determined by preliminary Corps of Engineers' investigations or official
designation, a floodway shall be defined by qualified engineering work by the applicant on the basis of a verified
one -hundred -year flood event;
E. Construction or reconstruction of residential structures within designated floodways, except for:
1. Repairs, reconstruction, or improvements to a structure which do not increase the ground floor area; and
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2. Repairs, reconstruction or improvements to a structure, the cost of which does not exceed fifty percent of
the assessed value of the structure either:
a. Before the repair, reconstruction or improvement is started; or
b. If the structure has been damaged and is being restored, before the damage occurred.
3. Work done on structures to correct existing violations of existing health, sanitary or safety codes, or to
structures identified as historic places, shall not be included in the fifty percent.
4. If subsection B of this section is satisfied, all new construction and substantial improvements shall comply
with all applicable flood hazard reduction provisions of Part Four.
F. The construction or storage of any object subject to flotation or movement during flood level periods;
G. The following uses, due to their high degree of incompatibility with the purpose of establishing and
maintaining a functional floodway, are specifically prohibited:
1. The filling of wetlands, except as authorized under Part Five, Fish and Wildlife Habitat and the Stream
Corridor, and Part Six, Wetlands;
2. Solid waste landfills, dumps, junkyards, outdoor storage of vehicles, and/or materials; and
3. Damming or relocation of any watercourse that will result in any downstream increase in flood levels
during the occurrence of the base flood discharge (see YMC 15.27.509).
H. The construction of new dikes.
L The listing of prohibited uses in this section shall not be construed to alter the general rule of statutory
construction that any use not permitted is prohibited. (Ord. 2008-46 § 1 (part), 2008).
15.27.413 Nonconforming uses and facilities.
A. Within the special flood hazard areas established by this chapter or amendments thereto, there may exist
structures and uses of land and structures which were lawful before these sections were adopted or amended, but
which would be prohibited or restricted under the terms of Part Four of this chapter or future amendment.
B. It is the intent of YMC Chapter 15.19 to permit these lawful preexisting nonconformities to continue until they
are removed by economic forces or otherwise, but not to encourage their survival except in cases where continuance
thereof would not be contrary to the public health, safety or welfare, or the spirit of this chapter. (Ord. 2008-46 § 1
(part), 2008).
Part Five. Fish and Wildlife Habitat and the Stream Gar- dar- C- tem onservation Areas
Article L Introduction
15.27.500 Purpose and intent.
Policies and
standards to help conserve and protect fish and wildlife habitat conservation areas are designed to accomplish the
following:
A. Meet the requirements of the Growth Management Act (RCW 36.70A.172) regarding best available science;
G. Rrcvide a zero Ret loss of etla etiot4s-awes;
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13B. Pr -o ide pons ,.lo Require consideration of alternatives for necessary development, construction, and uses
within fish and wildlife habitat conservation areas a desigm+ed s4e m ^ .i4dor apA 4 o,.,,. dFologie ll. r-01— '
.:. ea
EC. Prevent decline in the quantity and quality of surface and subsurface waters;
FD. Conserve, restore, and protect fish and wildlife habitats, vegetation, and ecological relationships;
GE. Protect semsi ;.,e areas of the s4e m ^^� d^r fish and wildlife habitat conservation areas from the potential
negative effects of development through coordinated land use planning; and,
14F. Protect fish and wildlife habitat conservation areas -Tthrough voluntary agreements or government incentives;
pFov;de pFo+oetio,, of r^+,,. -.,l wetlapA r;,,,etio,,s ^,,,avalues-; a -M
use plawiiHg. (04 2004 46 § 1 (, aA) 2044)
15.27.501 Protection approach.
A.—To maintain fish and wildlife habitat, there must be adequate environmental conditions for reproduction,
foraging, resting, and dispersal of animals. Factors affecting both habitat and its quality include the presence
of essential resources such as food, water, cover Rest bu 1, iRg m^+^^^l^ and lack of disturbance and diseases. The
city of Yakima protects fish and wildlife habitat through:
1. Designation of fish and wildlife habitat conservation areasProtee4 of of habitat for- a"alie speeie^; and
2. Pr-owe+i^^ of habitat for- speeies loe +e Hear- the ^W+Application of development standards based on best
available science to proposed activity and development in or near fish and wildlife habitat conservation areas.
the pr-otee+;,.,, ^ .,..1, see4ioms of this ..1,.,..+o,- (04 2009 46 § 1 (,, aA) 2009)
Article H. Designation and Mapping
15.27.502 H d -^lagire ll related ^Mire^' area feat w^cDesignation.
P. All wetlap& as def4Hed 44 )44C 15.27.200;
R n..y igoo.d pr-oHe ffea ipAiea+ed 1.. U.S. Sol !' ofisefya+;.... Sef ; soil stwvey .data-; .,...d
F. A buffer- ffea for- a str-eam eham+el, laW, or- popA or- f+om the edge of awetlapA. (04 2009 46 § 1 (paA), 2009),
A. Designation: Fish and wildlife habitat conservation areas are those habitat areas outside of shoreline
jurisdiction that meet any of the criteria listed below.
1. Areas with which state and federal endangered. threatened. and sensitive sbecies have a brima
association,
2. Habitats and species of local importance:
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3. Naturally occurring ponds under 20 acres and their submerged aquatic beds that provide fish or wildlife
habitat,
4. Waters of the state, including any required buffers and associated Federal Emergency Management
Agency -mapped floodplain and floodways,
5. Lakes, ponds, streams, and rivers planted with game fish by a governmental or tribal entity, and
6. State natural area preserves, natural resource conservation areas, and state wildlife areas.
45.27.59i B. Habitat and habitats of local importance.
A-. I.
habitat wapApt&4014 or- 0440r- valtws MOW them impoi4af4 oi4 a loeal level. 14abit4s of loeal impoi4aRee may
ahefed, Rmy Feduee 44e likelihood that 44e speeieswill mainta44 apid r-epr-oduee over- the long All species
and habitats identified by WDFW's Priority Habitats and Species program that maybe found in the city of
Yakima are designated as fish and wildlife habitat conservation areas and afforded protection under this chapter.
2.B- Species and habitats of local importance may be identified for protection under this chapter. State or local
agencies, individuals or organization may identify and nominate for consideration specific species and habitats,
or a general habitat type, including streams, ponds or other features. Proponents shall have the burden of
presenting evidence concerning the criteria set forth below. The nomination shall be processed once a year
through the annual comprehensive plan amendment cycle.
Aad. The decision for changes to species and habitats of local importance shall consider:
ai. Concern due to population status;
hii. Sensitivity to habitat manipulation;
siii. Importance to the local community; and
div. Criteria used to identify state priority species, which include:
�iaj- State candidate species that are defined by "FW Policy M-6001 to include fish and
wildlife species that WDFW will review for possible listing as state endangered, threatened, or
sensitive;
b� Vulnerable aggregations, which includes those species or groups of animals susceptible to
significant population declines, within a specific area, by virtue of their inclination to aggregate;
Species of recreational, commercial, and/or tribal importance that are vulnerable; and
-� The economic impact both positive and negative to the applicant's property or surrounding
property. Economic impact is to be determined by a properly qualified individual or firm using
industry standards.
fib. Nominated habitats and habitats for species of local importance shall consider the following and
must include maps to illustrate the proposal:
ai. A seasonal range or habitat element which, if altered, may reduce the likelihood that the species
will maintain or reproduce over the long term;
bii. Areas of high relative density or species richness, breeding habitat, winter range, and movement
corridors;
siii. Habitat with limited availability or high vulnerability to alteration; and
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div. Whether these habitats are already identified and protected under the provisions of this or other
local ordinances or state or federal law.
Vic. Habitat management recommendations shall be included for use in the administration of this section
Q. Development Standards. Projects located within habitats of local importance or within 200 feet of species of
local importance, as designated in subsection A -B.1 and B.2 of this section, shall meet the stay aids below, r^*' or
comply with the applicable development standards in YMC 15.27.508 through 15.27.521, upAess ,eview is also
Heeded f r a h dFologieal . relate' eFi4ie ' are . In addition, P -projects shall be designated using management
recommendations established for the species or habitat by federal and state agencies, or those adopted for species
and habitats of local importance by the city of Yakima. The department shall consider the extent such
recommendations are used in its decision on the proposal, and may consider recommendations and advice from
agencies with expertise. (Ord. 2008-46 § 1 (part), 2008).
15.27.504 Functional properties.
A Str-e m^ lakes ropAs apA .. ^*' P Aquatic fish and wildlife habitat conservation areas require a sufficient
riparian area to support one or more of the following functional properties:
1. Stfeam bStabilizing banks ,
2. Providing a sufficient shade canopy to maintain water temperatures that support fish and their habitat;
3. Moderating the impact of stormwater runoff,
4. Filtering solids, nutrients and harmful substances;
5. Preventing SLsurface erosion;
6. Providing and maintaining migratory corridors for wildlife;
7. Supporting a diversity of wildlife habitats; or
8. Allowing for the natural occurrence of woody debris and organic matter to collect in the aquatic
environment.
15.27.505 Water typing system.
For purposes of this chapter, the city of Yakima hereby adopts the WAC 222-16-031 a st -^^m law apA po
Interim water typing system, for those features designated as critical areas in YMC 15.27.502, as follows:
A. Type 1 watersstr-eams are those waters, within their ordinary high water mark (OHWM), meeting the criteria as
"shorelines of the state" and "shorelines of statewide significance" under RCW Chapter 90.58. Other Wwaters
associated with Type 1 waters as ,aeARe,a 4 n C=W r, Vier- 90 .59 aro Hot inePdded are not considered Type 1
waters. Type 1 waters are regulated exclusively under Title 17 of the Yakima Municipal Code;
B. Type 2 waters means segments of natural waters which are not classified as Type 1 Water and have
a high fish, wildlife, or human use. These are segments of natural waters and periodically inundated areas of their
associated wetlands, which:
1. Are diverted for domestic use by more than 100 residential or camping units or by a public accommodation
facility licensed to serve more than 10 persons, where such diversion is determined by the department to be a
valid appropriation of water and only considered Type 2 Water upstream from the point of such diversion for
1,500 feet or until the drainage area is reduced by 50 percent, whichever is less:
2. Are diverted for use by federal, state, tribal or private fish hatcheries. Such waters shall be considered Type
2 Water upstream from the point of diversion for 1,500 feet, including tributaries if highly significant for
protection of downstream water quality. The department may allow additional harvest beyond the requirements
of Type 2 Water designation provided by the department of fish and wildlife, department of ecology, the
affected tribes and interested parties that:
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a. The management practices brobosed by the landowner will adeauately protect water aualitv for the fish
hatchery: and
b. Such additional harvest meets the requirements of the water type designation that would apply in the
absence of the hatchery:
c. Are within a federal, state, local or private campground having more than 30 camping units: Provided,
That the water shall not be considered to enter a campground until it reaches the boundary of the park lands
available for public use and comes within 100 feet of a camping unit.
d. Are used by fish for spawning, rearing or migration. Waters having the following characteristics are
presumed to have highly significant fish populations:
i. Stream segments having a defined channel 20 feet or greater within the bankfull width and having
a gradient of less than 4 percent.
ii. Lakes, ponds, or impoundments having a surface area of 1 acre or greater at seasonal low water: or
e. Are used by fish for off -channel habitat. These areas are critical to the maintenance of optimum
survival of fish. This habitat shall be identified based on the following criteria:
i. The site must be connected to a fish bearing stream and be accessible during some period of the
year, and
ii. The off -channel water must be accessible to fish through a drainage with less than a 5% gradient.
lakes aPA'oFpoPAs of loeal
" as listed
,- pe.Aix R of this title. � �
.. A
C. Type 3 stfemwwaters means segments of natural waters which are not classified as Type 1 or 2 Waters and
have a moderate to slight fish, wildlife, or human use. These are segments of natural waters and periodically
inundated areas of their associated wetlands which:
1. Are diverted for domestic use by more than 10 residential or camping units or by a public accommodation
facility licensed to serve more than 10 persons, where such diversion is determined by the department to be a
valid appropriation of water and the only practical water source for such users. Such waters shall be considered
to be Type 3 Water upstream from the point of such diversion for 1,500 feet or until the drainage area is reduced
by 50 percent, whichever is less,
2. Are used by fish for spawning, rearing or migration. The requirements for determining fish use are
described in the board manual section 13. If fish use has not been determined:
a. Waters having any of the following characteristics are presumed to have fish use:
i. Stream segments having a defined channel of feet oF efeaw-Fwith44 the h^„va,n .. i th 4 Westem
Washi„: oi4, ^r 3 feet or greater in width :, EsW+ «'^^hi^a^^:, and having a gradient of 16 percent
or less,
ii. Stream segments having a defined channel of feet ^ r^^t^r ..,4h4 the i..,nkft n ..,; ath
West^fH Wash444o , ^r 3 feet or greater within the bankfull width 4 gastefH Wa h444e ^, and having
a gradient greater than 16 percent and less than or equal to 20 percent, and having greater than -5�
44 ^„tFibt4;,4^ baso size 44 Westef Washii44e ^ e ,te,- tbam 175 acres contributing basin size
gastern Washig4e^, based on hydrographic boundaries,
iii. Ponds or impoundments having a surface area of less than 1 acre at seasonal low water and
having an outlet to a fish stream,
iv. Ponds of impoundments having a surface area greater than 0.5 acre at seasonal low water.
b. The department shall waive or modify the characteristics in (i) of this subsection where:
i. Waters have confirmed, long term, naturally occurring water quality parameters incapable of
supporting fish,
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ii. Snowmelt streams have short flow cycles that do not support successful life history phases of fish.
These streams typically have no flow in the winter months and discontinue flow by June 1; or
iii. Sufficient information about a geomorphic region is available to support a departure from the
characteristics in (i) of this subsection, as determined in consultation with the department of fish and
wildlife, department of ecology, affected tribes and interested parties.
11 per-owlial s+.o »).
D. Type 4 waters stfemwmeans all segments of natural waters within the bankfull width of defined channels that
are perennial nonfish habitat streams. Perennial streams are flowing waters that do not go dry any time of a year of
normal rainfall and include the intermittent dry portions of the perennial channel below the uppermost point of
perennial flow.
15.27.200, "iPtei ext stream
E. Type 5 waters means all segments of natural waters within the bankfull width of the defined channels that are
not Type 1, 2, 3, or 4 Waters. These are seasonal, nonfish habitat streams in which surface flow is not present for at
least some portion of the year and are not located downstream from any stream reach that is a Type 4 Water. Type 5
Waters must be bhvsicallv connected by an above-eround channel system to Tvlle 1. 2. 3. or 4 Waters.
F. Lakes and Ponds.
1. Lakes and ponds not designated as a shoreline that receive water from the OHWM of a Type 2, 3, or 4
stream shall have the same surface water type as the highest stream type from which the lake or pond receives
water.
2. Natural lakes and ponds, not designated as a shoreline, that do not receive water from the OHWM of a
Type 1, 2, 3, or 4 stream shall be Type 3 ponds.
15.27.507 Maps.
Certain fish and wildlife habitat aP h dr-ologioal F -el +e of -it^ ^^' onservation areas have been inventoried and are
depicted on a series of paper and electronic maps. The maps do not officially define the extent or characteristics of
specific critical areas, but rather the potential physical boundaries and characteristics. Maps may be both regulatory
and nonregulatory in nature as described below:
Article IV. Water- Dependene- Dei,elapment Standar- aPA Buffer Requirements
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a'T7
t� 2009)-.
45.27.544 Water- dependent uses.
The following p -o ; shall .,,,.,,.bto .,+e - .do,,.epAePA uses•
A. Stmetw-es shall be eltister-ed at loea4iopis oi4 44e water -'s edge 4m,ing the least impaot to the stiff-ke waler- —amd-
.-..,.,1 ,,.,,l.he f ..a4io....f the s,,, -f ..o . a4er- (ll, -.d 2004 46 § l (,, aft 2009)
45.27.542 Water- uses.
B. Stmetw-es apA use areas s491 not be loea+ed withii4 the vegetative b4fer- speeiAed 44 Y44C 15.2:7.514 exe�
45.27.513 Nan water- ai4ented uses.
A. Stmetw-es affd use areas shall be set baek so as not to be lo ea+ed withii4 the vegetalA,e btt&r- speeiAed 44 )444-C-
1 car
epistir-e 44efe will not be pefmaffef4 daffmge or- loss ofthe vegetatA,e bttff-er-. (04 2009 46 § 1 (paA), 2009).
15.27.4510 Vegetative buffers.
The establishment of a vegetative buffer system is necessary to protect the functions and values of
h dFol,.,.ioal . ol.,+o.d ..,-4iea et,,,,,a,,f ,,,,,a fnip4wmm btt Fs f^r streams, lakes7—and ponds, ,,p . ,o.l, pAs
are-
hsted4p,�Tables 27.5-1 ^^d 1. Buffers associated with wetlands are listed in YMC 15.27.604.
A. Vegetative buffers shall be measured from the ordinary high water mark for streams, lakes, and ponds-a*d
49m the edge of the w e*la The width of the buffer shall be determined according to the stream oF wetia^'water
type. Buffer width maybe reduced through an adjustment permit process (YMC 15.27.317) using one of the
following methods-:
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1. Where a legally established road or railway crosses a critical area buffer, the administrative official or
designee may approve a modification of the minimum required buffer width to the waterward edge of the
improved road if a study submitted by the applicant and prepared by a qualified professional demonstrates that
the part of the buffer on the upland side of the road sought to be reduced:
a. Does not provide additional protection of the waterbody, and
b. Provides insignificant biological, geological or hydrological buffer functions relating to the waterward
portion of the buffer adjacent to the waterbody.
If the imbroved roadwav corridor is wider than twentv feet. a studv is not reauired.
2. Buffer averaging to improve stream protection may be permitted when all of the following conditions are
met:
a. The buffer has significant differences in characteristics that affect its habitat functions.
b. The buffer is increased adjacent to the higher -functioning area of habitat or more sensitive portion of
the stream and decreased adjacent to the lower -functioning or less sensitive portion as demonstrated by a
critical areas report from a qualified professional.
c. The total area of the buffer after averaging is equal to the area required without averaging.
d. The buffer at its narrowest point is never less than three-quarters of the required width.
3. Buffer averaging to allow reasonable use of a parcel may be permitted when all of the following are met:
a. There are no feasible alternatives to the site design that could be accomplished without buffer
averaging.
b. The averaged buffer will not result in degradation of the stream's functions and values as
demonstrated by a critical areas report from a qualified professional.
c. The total buffer area after averaging is equal to the area required without averaging.
d. The buffer at its narrowest point is never less than three-quarters of the required width
'A'44 a smalleF buff -OF.
.:k
EB. The minimum buffer widths listed in Tables 27.5-1 api are the lowest possible buffer widths allowed
by means of the adjustment process. Adjustments below the minimum buffer width must meet additional approval
criteria as provided in YMC 15.27.317(C)(4).
D. The adequacy of these standard buffer widths presumes the existence of a relatively intact native vegetative
community within the buffer zone that is deemed adequate to protect the identified critical area.
1. If the vegetation is degraded, then revegetation may be considered with any adjustment to the buffer width.
2. Where the use is being intensified, a degraded buffer may be revegetated to maintain the standard width
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Table 27.5-1
Water Type
Buffer Width—standard/(minimum adjustment)
Type 1 shoreline streams, lakes,
and ponds
444WSee Table 09.030-1 in YMC 17.09.030.P.
Type 2 s4eams laWs rA
P&Rdsor 3
75'*2--5}/ 5( 6 25,1
Type 3 stFe ms (ro.o
laWs, aPA poHdsor 4
Type 4 and 5str-eams
T Te c st -oams (ephe,,,ofal)
No d 4fe - stap,a.fds T pe c st -oams are Hot r-egWaled as
st,-oams btA may be pr-oteete d , ...do,- g ..1....;oal d,.,-�af dohs -
.doe of epA r ,1.,4;oi4s No A 1;...,b
Type 4 Wetla Type 2 Wetla Type 2 Wetla Type 4 Wetla
Article V. Land Modification Development Standards
15.27.5511 Roads, railroads, and parking.
The following provisions shall apply to the location and construction of roads, railroads, and parking within a
designated ish and wildlife habitat conservation area:
A. Roads and railroads shall not be located within a fish and wildlife habitat conservation area deli gate,a stream
eoa4doFtixcept where it is necessary to cross the eoFi4doFtiritical area or where existing development, topography,
and other conditions preclude locations outside the ritical area;
1. Construction of roadways across stream corridors shall be by the most direct route possible having the least
impact to the fish and wildlife habitat conservation area ,
2. Roadways that must run parallel to streams or wetlands shall be along routes having the greatest possible
distance from stream or wetland and the least impact;
3. Roadways within the fish and wildlife habitat conservation area or its buffer s4ea ^^�d^r shall not
hydrologically obstruct, cut off or isolate stream corridor features, unless it is clearly unavoidable;
B. Material excavated from the roadway area to achieve the design grade shall be used as fill where necessary to
maintain grade or shall be transported outside the fish and wildlife habitat conservation area^', eaff. ,.,.....:,d,.,.;
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C. Necessary fill to elevate roadways shall not impede the normal flow of floodwaters or cause displacement that
would increase the elevation of flood waters such that it would cause properties not in the floodplain to be flood -
prone;
D. Spoil, construction waste, and other debris shall not be used as road fill or buried within the fish and wildlife
habitat conservation area ,
15.27.5162 Utility transmission lines and facilities.
The following provisions shall apply to the location, construction, and installation of utility transmission lines (such
as those for wastewater, water, communication, natural gas) within a designated h dr-ologioal r -el +e or-i4ieal fish
and wildlife habitat conservation area:
15.27.51-73 Bank a stabilization.
The following provisions shall apply to show—bank stabilization projects located outside of shoreline jurisdiction:
A. MBank stabilization projects shall be allowed only where there is evidence of erosion which clearly
threatens existing property, structures, or facilities, and which stabilization will not jeopardize other upstream or
downstream properties;
B. Stabilization projects shall be developed under the supervision of, or in consultation with, agencies or
professionals with appropriate expertise;
C. Stabilization projects shall be confined to the minimum protective measures necessary to protect the threatened
property;
D. The use of fill to restore lost land may accompany stabilization work, provided the resultant shefe-bank does
not extend beyond theo�ordinary high water mark, finished grades are consistent with abutting
properties, a restoration plan is approved for the area, and the fill material is in compliance with YMC 15.27.519;
E. Stabilization projects shall use design, material, and construction alternatives that do not require high or
continuous maintenance, and which prevent or minimize the need for subsequent stabilization of the shore's other
segments;
F. Alternative Preferences. Vegetation, berms, bioengineering techniques, and other nonstructural alternatives
which preserve the natural character of the shefe-bank shall be preferred over riprap, concrete revetments,
bulkheads, breakwaters, and other structural stabilization, while riprap, rock or other natural materials shall be
preferred over concrete revetments, bulkheads, breakwaters and other structural stabilization;
G. Applications to constructor enlarge dikes or levees shall meet the requirements of YMC 15.27.411(G);
H. Revetments and bulkheads shall be no higher than necessary to protect and stabilize the sbank;
1. Breakwaters shall be constructed of floating or open -pile designs rather than fill, riprap, or other solid
construction methods; and
I All new flood control projects shall define maintenance responsibilities and a funding source for operations,
maintenance and repairs for the life of the project. (Ord. 2008-46 § 1 (part), 2008).
15.27.5184 Dredging and excavation.
The following provisions shall apply to dredging and excavation within a designated h dr-010gioal relate''
or-i6ealaa uatic fish and wildlife habitat conservation area outside of shoreline jurisdiction:
E 9,,U4es aeFoss shor-e ap .. etlap' e -e-^Access to accomplish dredging or excavation shall be confined to the
minimum area necessary to gain entry and shall be confined to locations with the least potential for site disturbance
and damage.
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G. Dredge spoils are also considered fill, and shall not be deposited within the stfewa-waterbody except where
such deposit is in accordance with approved procedures intended to preserve or enhance wildlife habitat, natural
drainage, or other naturally occurring conditions. (Ord. 2008-46 § 1 (part), 2008).
15.27.5115 Filling.
The following provisions shall apply to filling activities within a designated h dr-ologioal Riated ^44iea fish and
wildlife habitat conservation area outside of shoreline jurisdiction:
A. Fill within surface waters or wetlands shall be allowed only where necessary in conjunction with water -
dependent uses or an approved Relawatioi4 mitigation or restoration plan under YMC 15.27.307, 15.27.521, or
appr-oved eompemsa4oi�,,,,;+igatioi4 pi.,,, ,,,, e - Y 4C 15.27.604.
B. Fill for the purpose of increasing elevation may be permitted if it can be accomplished in a manner consistent
with this chapter's policies.
C. Fill shall be the minimum necessary to accomplish the use or purpose and shall be confined to areas having the
least impact to the fish and wildlife habitat conservation are —stfe m eoR4&r. Other alternatives should be preferred
over fill to elevate new homes in the floodplain, such as increasing foundation height or zero -rise methods such as
piers, posts, columns, or other methods.
G. Fill and finished surface material shall require low maintenance, provide high resistance to erosion, and prevent
or control the migration of sediments and other material from the fill area to surrounding w,.+er, sha fe, -��
we waterbodies, unless the Washington Department of Fish and Wildlife indicates other options are preferred.
L Fill should not obstruct, cut off, or isolate strv^m eoR4dor f ^, , esaguatic fish and wildlife habitat conservation
areas. (Ord. 2008-46 § 1 (part), 2008).
15.27.53916 Commercial mining of gravel.
The following provisions shall apply to the commercial mining of gravel within a designated h dFologioal rel +e
fish and wildlife habitat conservation area outside of shoreline jurisdiction:
A. Prior to the authorization of a commercial gravel mining operation, the project proponent shall provide maps to
scale which illustrate the following:
1. The extent to which gravel excavation and processing will affect or modify existing -fish and wildlife
habitat conservation areasstrv^m ^^�d^r features, including existing riparian vegetation;
B. Wherever feasible, the operations and any subsequent use or uses shall not cause permanent impairment or loss
of ritical area functions and values. Mitigation shall
be provided consistent with YMC 15.27.307, 15.27.521, or 15.27.604f r the f a4*e' ^ replaeomef4 at eEra l - ^l„o
Wetla,,a Miti.a4io,4 4 W.,si,iag4oi State Pai4s i .,,,,a 2 (Mafah 2006 , as "dated).
D. Except where authorized by the city of Yakima in consultation with the State Department of Fish and Wildlife
and Department of Ecology, the following shall apply:
1. The excavation zone for the removal of gravels shall be located a minimum of one hundred feet upland
from the ordinary high water mark (OHWM) of the strv^m ehapAw4a waterbody.
15.27.52417 Restorationelanhafien.
The following guidelines shall apply to the restoration of disturbed sites resulting from development
activities within a desigHated h dFologioal rvlato,a �ish and wildlife habitat conservation area:
B. Large-scale projects that extend over several months shall be phased to allow restoration of areas
where work or operations have been completed;
C. D e�Restoration shall be scheduled to address precipitation, meltwater runoff, the growing season, and
other seasonal variables that influence restoration and recovery;
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E. Where existing development and construction prevent return of a site to its natural condition, sites may be
finished to conditions comparable to surrounding properties provided suitable protective measures are used to
prevent s4e m ^^�d^r degradation of fish and wildlife habitat conservation areas;
F. Cut -and -fill slopes shall be stabilized at, or at less than, the normal angle of repose for the materials involved;
and
G. For the replacement or enhancement of vegetation within fish and wildlife habitat conservation areas and their
..,required vegetative buffers Hal+tfalb, oeouff ng, native plant species shall be used
, unless a showing of good
cause acceptable to the administrative official or designee is provided. Should good cause be shown, then self -
maintaining or low -maintenance plant species compatible with the native vegetation shall be used in place of non-
native and high -maintenance species. (Ord. 2008-46 § 1 (part), 2008).
Part Six. Wetlands
15.27.601 Designating and mapping.
A. Wetlap& are all areas meeting 04e def4H4iot4 for- we0apAs as def4Hed 44 Y44C 15.27.200 apA are hereby
desiga4ed e4tie ' areas whi& are sttbjeet to 44s e4aptor exeept 04e f llo ing-Metlands shall be delineated used the
procedures outlines in the approved federal wetland delineation manual and applicable regional supplements.
B. Wetlands are all areas meeting the definition of wetlands as defined in YMC 15.27.200 and are hereby
designated critical areas which are subject to this chapter, except the following:
1. Irrigation systems that create an artificial wetland; and
2. Areas where changes in irrigation practices have caused wetland areas to dry up.
BC. The approximate location and extent of wetlands are shown on maps maintained by the city of Yakima. These
maps may include information from the National Wetlands Inventory produced by the U.S. Fish and Wildlife
Service and are to be used as a guide for the city of Yakima. (Ord. 2008-46 § 1 (part), 2008).
15.27.602 Protection approach.
Wetlands will be protected using the protection approach for h dr-ologioal r la+e' ^^*i^^' ^r^^^fish and wildlife
habitat conservation areas found in YMC 15.27.501. Wetlands and their functions will be protected using the
standards found in Part Four. (Ord. 2008-46 § 1 (part), 2008).
15.27.603 Wetland functions and rating.
B. Wetlands shall be rated based on categories that reflect the functions and values of each wetland and shall be
based on the criteria provided in the Washington State Wetland Rating System for Eastern Washington, revised
October 2014 (Ecology Publication No. 14-06-03004 06 15, or as revised) which are summarized
below:
1. Category I wetlands are more sei4sitA,e to dist , ,.anee that ..,ost etlap ; rvla4;. o,. , ,,, iss u ed; ^ a
elass foe as Ga+egoF r.
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d. Bo -,s -those that 1) represent a unique or rare wetland type: or 2) are more sensitive to disturbance than
most wetlands: or 3) are relatively undisturbed and contain ecological attributes that are impossible to replace
in a human lifetime: or 4) provide a high level of functions. Risk of any degradation to these wetlands must be
avoided because their functions and values are too difficult to replace. Generally, these wetlands are not
common and make up a small percentage of the wetlands in the region.
2. Category II wetlands are difficult, but not impossible, to replace and provide high levels of some functions.
e. Forested we lard^.These wetlands occur more commonly than Category 1 wetlands, but still need a
relatively high level of protection.
3. Category III wetlands are .
Ga+e .oF rrr .. etl.,p& inel,,.de,
b. Assoeiated veFml pools.wetlands with a moderate level of functions and can often be adequately replaced
with a well-planned mitigation project. These wetlands generally have been disturbed in some ways and are
often less diverse or more isolated from other natural resources in the landscape than Category II wetlands.
4. Category IV wetlands have the lowest levels of functions, seoFin - less thai4 thift poipAs :,, the EWW c
Ga+egoF Al .. etlap& and are often heavily disturbed. aPA are * apAs that shot .d be able to be
These are wetlands that should be able to be replaced and, in some cases, improved. However,
experience has shown that replacement cannot be guaranteed in any specific case. These wetlands may provide
some important functions and also need to be protected.
C. Wetlands shall be rated as they exist on the day of project application submission. Information regarding the
original condition of illegally modified wetlands that eairxetcannot be discerned from aerial photographs or other
reliable information sources shall use the highest appropriate points value within each missing data field of the
Washington State Wetland Rating System for Eastern Washington: 2014 UpdateE nRS rating sheet to complete
the rating. (Ord. 2008-46 § 1 (part), 2008).
15.27.604 Wetland Buffers
A. Buffer Requirements. The following buffer widths have been established in accordance with the best available
science. They are based on the category of wetland and the habitat score as determined by a qualified professional
using the Washington State Wetland Rating System for Eastern Washington: 2014 Update (Ecology Publication
414-06-030, or as revised). The adjacent land use intensity is assumed to be high
1. For wetlands that score 5 points or more for habitat function, the buffers in Table 27.6-1 can be used if both
of the following criteria are met:
a. A relatively undisturbed, vegetated corridor at least 100 feet wide is protected between the wetland and
any other Priority Habitats as defined by the Washington State Department of Fish and Wildlife
(http://wdfw.wa.gov/hab/Thshabs.htm).
The corridor must be protected for the entire distance between the wetland and the Priority Habitat by
some type of legal protection such as a conservation easement.
Presence or absence of a nearby habitat must be confirmed by a qualified biologist. If no option for
providing a corridor is available, Table 27.6-1 may be used with the required measures in Table 27.6-2
alone.
b. The measures in Table 27.6-2 are implemented, where applicable, to minimize the impacts of the
adjacent land uses.
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2. For wetlands that score 3-4 habitat points, only the measures in Table 27.6-2 are required for the use of
Table 27.6-1.
3. If an applicant chooses not to apply the mitigation measures in Table 27.6-2, or is unable to provide a
protected corridor where available, then Table 27.6-3 shall be used.
4. The buffer widths in Table 27.6-1 and 27.6-3 assume that the buffer is vegetated with a native plant
community appropriate for the ecoregion. If the existing buffer is unvegetated, sparsely vegetated, or vegetated
with invasive species that do not perform needed functions, the buffer should either be planted to create the
appropriate plant community or the buffer should be widened to ensure that adequate functions of the buffer are
provided.
Table 27.6-1: Wetland Buffer Requirements if Table 27.6-2 is implemented and corridor provided
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Buffer Width (feet)based
on habitat score
Wetland Cate o
3-4
5
6-7
8-9
Category 1: Based on total
75
90
120
150
score
holy 1: Forested
75
90
120
150
Category 1: Bogs and
Wetlands of High
Conservation Value
190
Category 1: Alkali
150
Category IL Based on total
75
90
120
150
score
Category IL Vernal Pool
150
holy IL Forested
75
90 120
150
Category III (all
60
90 120
150
Category IV (all)
40
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Table 27.6-2: Required measures to minimize impacts to wetlands
Disturbance
Required Measures to Minimize Impacts
Lights
. Direct lights away from wetland
Noise
. Locate activity that generates noise away from wetland
• If warranted, enhance existing buffer with native vegetation for plantings adjacent
8-9
to noise source
• For activities that generate relatively continuous, potentially disruptive noise, such
100
as certain heave industry or mining, establish an additional 10 -feet heavily
vegetated buffer strip immediately adjacent to the outer wetland buffer.
Toxic Runoff
. Route all new, untreated runoff away from wetland while ensuring wetland is not
dory 1: Forested
dewatered
• Establish covenants limiting use of pesticides within 150 -feet of wetland
130
• Apply integrated pest management
Stormwater
. Retrofit stormwater detention and treatment for roads and existing adjacent
Runoff
development
• Prevent channelized flow from lawns that directly enters the buffer
200
• Use Low Intensity Development techniques
Changes in water
e Infiltrate or treat, detain, and disperse into buffer new runoff from impervious
regime
surfaces and new lawns.
Pets and human
e Use privacy fencing OR plan dense vegetation to delineate buffer edge and to
disturbance
discourage disturbance using vegetation appropriate for the ecoregion
• Place wetland and its buffer in a separate tract or protect with a conservation
130 180
easement
Dust
• Use best management practices to control dust
Table 27.6-3: Wetland Buffer Requirements if Table 27.6-2 is NOT implemented and corridor NOT provided
5. Increased Wetland Buffer Area Width Buffer widths shall be increased on a case by -case basis as
determined by the administrative official when a larger buffer is necessary to protect wetland functions and
values. This determination shall be supported by appropriate documentation showing that it is reasonably
related to brotection of the functions and values of the wetland. This documentation shall include. but not be
limited to, the following criteria
a. The wetland is used by a state or federally listed plant or animal species, or has unusual nesting or
resting sites such as heron rookeries or raptor nesting trees: or
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Buffer Width (feet)based on habitat score
Wetland Cate o
3-4
5
6-7
8-9
Category 1: Based on total
100
130
180
200
score
dory 1: Forested
100
130
180
200
Category 1: Bogs and
Wetlands of High
Conservation Value
250
Category 1: Alkali
200
Category IL Based on total
100
130
180
200
score
Category IL Vernal Pool
200
dory IL Forested
100
130 180
200
Category III (alll
80
130 180
200
Category IV (all)
50
5. Increased Wetland Buffer Area Width Buffer widths shall be increased on a case by -case basis as
determined by the administrative official when a larger buffer is necessary to protect wetland functions and
values. This determination shall be supported by appropriate documentation showing that it is reasonably
related to brotection of the functions and values of the wetland. This documentation shall include. but not be
limited to, the following criteria
a. The wetland is used by a state or federally listed plant or animal species, or has unusual nesting or
resting sites such as heron rookeries or raptor nesting trees: or
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b. The adjacent land is susceptible to severe erosion, and erosion -control measures will not effectively
prevent adverse wetland impacts: or
c. The adjacent land has minimal vegetative cover or slopes greater than 30 percent.
6. Buffer averaging to improve wetland protection may be permitted when all of the following conditions are
met:
a. The wetland has significant differences in characteristics that affect its habitat functions, such as a
wetland with a forested component adjacent to a degraded emergent component or a "dual -rated" wetland
with a Category 1 area adjacent to a lower -rated area.
b. The buffer is increased adjacent to the higher -functioning area of habitat or more -sensitive portion of
the wetland and decreased adjacent to the lower -functioning or less -sensitive portion as demonstrated by a
critical areas report from a qualified wetland professional.
c. The total area of the buffer after averaging is equal to the area required without averaging.
d. The buffer at its narrowest point is never less than either 3/4 of the required width or 75 -feet for
Category I and II, 50 -feet for Category III, and 25 -feet for Category IV, whichever is greater.
7. Averaging to allow reasonable use of a parcel may be permitted when all of the following are met:
a. There are no feasible alternatives to the site design that could be accomplished without buffer
averaging.
b. The averaged buffer will not result in degradation of the wetland's functions and values as
demonstrated by a critical areas report from a qualified wetland professional.
c. The total buffer area of the buffer after averaging is equal to the area without averaging.
d. The buffer at its narrowest point is never less than either 3/4 of the required width or 75 -feet for
Category I and II, 50 -feet for Category III, and 25 -feet for Category IV, whichever is greater.
B. To facilitate long-range planning using a landscape approach, the Administrative Official may identify and pre-
assess wetlands using the rating system and establish appropriate wetland buffer widths for such wetlands. The
Administrative Official will prepare maps of wetlands that have been pre -assessed in ibis manner.
C. Measurement of Wetland Buffers. All buffers shall be measured perpendicular from the wetland boundary as
surveyed in the field. The buffer for a wetland created, restored, or enhanced as compensation for approved wetland
alterations shall be the same as the buffer required for the category of the created, restored, or enhanced wetland.
Buffers must be fully vegetated in order to be included in buffer area calculations. Lawns, walkways, drivewus, ad
other mowed or paved areas will not be considered buffers or included in buffer area calculations.
D. Buffers on Mitigation Sites. All wetland mitigation sites shall have buffers consistent with the buffer
requirements of this Chapter. Buffers shall be based on the expected or target category of the proposed wetland
mitigation site.
E. Buffer Maintenance. Except as otherwise specified or allowed in accordance with this chapter, wetland buffers
shall be retained in an undisturbed or enhanced condition. In the case of compensatory mitigation sites, removal of
invasive non-native weeds is required for the duration of the mitigation bond, YMC § 15.27.605(10)(b)(i)(10).
F. Impacts to Buffers. Requirements for the compensation for impacts to buffers are outlined in YMC §
15.27.605.
G. Overlapping Critical Area Buffers. If buffers for two contiguous critical areas overlap (such as buffers for a
stream and a wetland), the wider buffer applies.
H. Allowed Buffer Uses. The following uses may be allowed within a wetland buffer in accordance with the
review procedures of this Chapter, provided they are not prohibited by any other applicable law and they are
conducted in a manner so as to minimize impacts to the buffer and adjacent wetland:
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1. Conservation and Restoration Activities. Conservation or restoration activities aimed at protecting the soil,
water, vegetation, or wildlife.
2. Passive recreation. Passive recreation facilities designed and in accordance with an approved critical area
report, including:
a. Walkways and trails, provided that those pathways are limited to minor crossings having no adverse
impact on water quality. They should be generally parallel to the perimeter of the wetland, located only in
the outer twenty-five percent (25%) of the wetland buffer area, and located to avoid removal of significant
trees. They should be limited to pervious surfaces no more than five (5) feet in width for pedestrian use
only. Raised boardwalks utilizing non -treated pilings may be acceptable.
b. Wildlife -viewing structures.
3. Educational and scientific research activities
4. Normal and routine maintenance and repair of any existing public or private facilities within an existing
right-of-way, provided that the maintenance or repair does not increase the footprint or use of the facility or
right-of-wa.
5. The harvesting of wild crops in a manner that is not injurious to natural reproduction of such crops,
chemical applications, or alteration of the wetland by changing existing topography, water conditions, or water
sources.
6. Drilling for utilities/utility corridors under a buffer, with entrance/exit portals located completely outside of
the wetland buffer boundary, provided that the drilling does not interrupt the ground water connection to the
wetland or percolation of surface water down through the soil column. Specific studies by a hydrologist are
necessary to determine whether the ground water connection to the wetland or percolation of surface water
down through the soil column is disturbed.
7. Enhancement of a wetland buffer through the removal of non-native invasive plant species. Removal of
invasive plant species shall be restricted to hand removal. All removed plant material shall be taken away from
the site and appropriately disposed of. Plants that appear on the Washington State Noxious Weed Control Board
list of noxious weeds must be handled and disposed of according to a noxious weed control plan appropriate for
that species. Revegetation with appropriate native species at natural densities is allowed in conjunction with
removal of invasive plant species.
8. Repair and maintenance of non -conforming uses or structures, where legally established within the buffer,
provided they do not increase their degree of nonconformity.
1. Signs and Fencing of Wetlands and Buffers.
1. Temporary markers. The outer perimeter of the wetland buffer and the clearing limits identified by a
approved permit or authorization shall be marked in the field with temporary "clearing limits" fencing in such a
way as to ensure that no unauthorized intrusion will occur. The marking is subject to inspection by the
Administrative Official prior to the commencement of permitted activities. This temporary marking shall be
maintained throughout construction and shall not be removed until permanent signs, if required, are in place.
2. Permanent signs. As a condition of aM permit or authorization issued pursuant to this chapter, the
Administrative Official may require the applicant to install permanent signs along the boundary of a wetland or
buffer.
a. Permanent signs shall be made of an enamel -coated metal face and attached to a metal post or other
non -treated material of equal durability. Sims must be posted at an interval of one (1) every 50 -feet, or one
(1) per lot if the lot is less than 50 -feet wide, and must be maintained by the property owner in perpetuity.
The signs shall be worded as follows or with alternative language approved by the Administrative Official:
Protected Wetland Area
Do Not Disturb
Contact the Citv of Yakima
Regarding Uses, Restrictions, and Opportunities for Stewardship
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b. The provisions of Subsection (a) may be modified as necessary to assure protection of sensitive features
or wildlife.
3. Fencing.
a. The applicant shall be required to install a permanent fence around the wetland or buffer when
domestic grazing animals are present or may be introduced on site.
b. Fencing installed as part of a proposed activity, or as required in this Subsection, shall be designed so
as not to interfere with species mitigation, including fish runs, and shall be constructed in a manner that
minimizes impacts to the wetland and associated habitat.
15.27.605 Compensatory Mitigation requirements:
A. Mitigation Sequencing. Before impacting any wetland or its buffer, an applicant shall demonstrate that the
following actions have been taken. Actions are listed in the order of preference:
1. Avoid the impact altogether by not taking a certain action or parts of an action.
2. Minimize impacts by limiting the degree or magnitude of the action and its implementation, b., ung
appropriate technology, or by taking affirmative steps to avoid or reduce impacts.
3. Rectify the impact by repairing, rehabilitating, or restoring the affected environment.
4. Reduce or eliminate the impact over time by preservation and maintenance operations.
5. Compensate for the impact by replacing, enhancing, or providing substitute resources or environments.
6. Monitor the required compensation and take remedial or corrective measures when necessary.
B. Requirements for Compensatory Mitigation:
1. Compensatory mitigation for alterations to wetlands shall be used only for impacts that cannot be avoided
or minimized and shall achieve equivalent or greater biologic functions. Compensatory mitigation plans shall be
consistent with Wetland Mitigation in Washington State Part 2: Developing Mitigation Plans Version 1,
(Ecology Publication #06-06-011b, Olympia, WA, March 2006 or as revised), and Selecting Wetland Mitigation
Sites Using a Watershed Approach (Eastern Washington) (Publication #10-06-07, November 2010).
2. Mitigation ratios may also be determined using the credit/debit tool describe in "Calculating Credits and
Debits for CompensatoryMitigation in Wetlands ofEastern Washington: Final Report (Ecology Publication
#11-06-045, August 2012), consistent with subsection 8 of this Chapter.
3. Compensating for Lost or Affected Functions. Compensatory mitigation shall address the functions
affected by the proposed project, with an intention to achieve functional equivalency or improvement of
functions. The goal shall be for the compensatory mitigation to provide similar wetland functions as those lost,
except when either:
a. The lost wetland provides minimal functions, and the proposed compensatory mitigation action(s) will
provide equal or greater functions or will provide functions shown to be limiting within a watershed
through a formal Washington state watershed assessment plan or protocol, or
b. Out -of -kind replacement of wetland type or functions will best meet watershed goals formally
identified by the City, such as replacement of historically diminished wetland types.
C. Approaches to Compensatory Mitigation. Mitigation for lost or diminished wetland and buffer functions shall
rely on the approaches listed below.
1. Wetland mitigation banks. Credits from a certified wetland mitigation bank may be used to compensate for
impacts located within the service area specified in the mitigation bank instrument. Use of credits from a
wetland mitigation bank certified under Chapter 173-700 WAC is allowed if:
a. The approval authority determines that it would provide appropriate compensation for the
proposed impacts: and
b. The impact site is located in the service area of the bank.
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c. The proposed use of credits is consistent with the terms and conditions of the certified
mitigation bank instrument.
d. Replacement ratios for projects using bank credits is consistent with replacement ratios specified in the
certified mitigation bank instrument.
2. In -Lieu Fee Mitigation: Credits from an approved in -lieu -fee program may be used when all of the
following apply:
a. The approval authority determines that it would provide environmentally appropriate
compensation for the proposed impacts.
b. The proposed use of credits is consistent with the terms and conditions of the approved in -
lieu -fee program instrument.
c. Projects using in -lieu -fee credits shall have debits associated with the proposed impacts calculated by
the applicant's qualified wetland professional using the credit assessment method specified in the approved
instrument for the in -lieu -fee program.
d. The impacts are located within the service area specified in the approved in -lieu -fee instrument.
3. Permittee -responsible mitigation. In this situation, the permittee performs the mitigation after the permit is
issued and is ultimately responsible for implementation and success of the mitigation. Permittee -responsible
mitigation may occur at the site of the permitted impacts or at an off-site location within the same watershed.
Permittee -responsible mitigation shall be used only if the applicant's qualified wetland professional
demonstrates to the approval authority's satisfaction that the proposed approach is ecologically preferable to use
of a bank or IL,F program, consistent with the criteria in this section.
D. Types of Compensatory Mitigation. Mitigation for lost or diminished wetland and buffer functions shall rely
on a type listed below in order of preference. A lower -preference form of mitigation shall be used only if the
applicant's qualified wetland professional demonstrates to the approval authority's satisfaction that all higher -ranked
types of mitigation are not viable, consistent with the criteria in this section.
1. Restoration: The manipulation of the physical, chemical, or biological characteristics of a site with the goal
of returning natural or historic functions to a former or degraded wetland. For the purpose of tracking net gains
in wetland acres, restoration is divided into:
a. Re-establishment The manipulation of the physical, chemical, or biological characteristics of
a site with the goal of returning natural or historic functions to a former wetland. Re-establishment results
in a gain in wetland acres (and functions). Activities could include removing fill material, plugging
ditches, or breaking drain tiles.
b. Rehabilitation: The manipulation of the physical, chemical, or biological characteristics of a site with
the goal of repairing natural or historic functions of a degraded wetland. Rehabilitation results in a gain in
wetland function but does not result in a gain in wetland acres. Activities could involve breaching_ a dike to
reconnect wetlands to a floodplain or return tidal influence to a wetland.
2. Establishment (Creation): The manipulation of the physical, chemical, or biological characteristics of a site
to develop a wetland on an upland or deepwater site where a wetland did not previously exist. Establishment
results in a gain in wetland acres. Activities typically involve excavation of upland soils to elevations that will
produce a wetland hydroperiod, create hydric soils, and support the growth of hydrophytic plant species.
If a site is not available for wetland restoration to compensate for expected wetland and/or buffer impacts, the
approval authority may authorize creation of a wetland and buffer upon demonstration by the applicant's
qualified wetland professional that:
a. The hydrology and soil conditions at the proposed mitigation site are conducive for
sustaining the proposed wetland and that creation of a wetland at the site will not likely cause hydrologic
problems elsewhere,
b. Adjacent land uses and site conditions do not jeopardize the viability of the proposed
wetland and buffer (e.g., due to the presence of invasive plants or noxious weeds, stormwater runoff, noise,
light, or other impacts): and
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c. The proposed wetland and buffer will eventually be self-sustaining with little or no long-term
maintenance.
3. Enhancement. The manipulation of the physical, chemical, or biological characteristics of a wetland site to
heighten, intensify, or improve specific function(s) or to change the growth stage or composition of the
vegetation present. Enhancement is undertaken for specified purposes such as water quality improvement,
flood water retention, or wildlife habitat. Enhancement results in a change in some wetland functions and can
lead to a decline in other wetland functions, but does not result in a gain in wetland acres. Activities typically
consist of planting vegetation, controlling non-native or invasive species, modifying site elevations or the
proportion of open water to influence hydroperiods, or some combination of these activities. Applicants
proposing to enhance wetlands or associated buffers shall demonstrate how the proposed enhancement will
increase the wetland's/buffer's functions, how this increase in function will adequately compensate for the
impacts, and how existing wetland functions at the mitigation site will be protected.
4. Protection/Maintenance (Preservation). Removing a threat to, or preventing the decline of, wetland
conditions by an action in or near a wetland. This includes the purchase of land or easements, or rept
water control structures or fences. This term also includes activities commonly associated with the term
preservation. Preservation does not result in a gain of wetland acres. Permanent protection of a Category I or II
wetland and associated buffer at risk of degradation can be used only if:
a. The approval authority determines that the proposed preservation is the best mitigation option:
b. The proposed preservation site is under threat of undesirable ecological change due to permitted,
planned, or likely actions that will not be adequately mitigated under existing regulations,
c. The area proposed for preservation is of high quality or critical for the health of the watershed or basin
due to its location. Some of the following features may be indicative of high-quality sites:
i. Category I or II wetland rating (using the wetland rating system for wtslemEastern
Washington)
ii. Rare or irreplaceable wetland type (for example, bogs, mature forested wetlands,
estuarine wetlands) or aquatic habitat that is rare or a limited resource in the area,
iii. The presence of habitat for priority or locally important wildlife species, or also list has
provides biological and/or hydrological connectivity;
iv. Provides biological and/or h, d�gical connectivity;
v. Priority sites in an adopted watershed plan.
d. Permanent preservation of the wetland and buffer will be provided through a conservation
easement or tract held by an appropriate natural land resource manager, such as a land trust.
e. The approval authority may approve other legal and administrative mechanisms in lieu of a
conservation easement if it determines they are adequate to protect the site.
f Ratios for preservation in combination with other forms of mitigation generally range from 10:1 to
20:1, as determined on a case-by-case basis, depending on the quality of the wetlands being impacted and
the quality of the wetlands being preserved. Ratios for preservation as the sole means of mitigation
generally start at 20:1.
E. Location of Compensatory Mitigation. Compensatory mitigation actions shall generally be conducted within
the same sub -drainage basin and on the site of the alteration except when the applicant candemonstrate that
off-site mitigation is ecologically preferable. The following criteria will be evaluated when determining whether the
proposal is ecologically_ preferable. When considering off-site mitigation, preference should be given to using
alternative mitigation, such as a mitigation bank, an in -lieu -fee program, or advance mitigation.
1. There are no reasonable opportunities on site or within the sub -drainage basin (e.g., on-site options would
require elimination of high -functioning upland habitat), or opportunities on site or within the sub -drainage basin
do not have a high likelihood of success based on a determination of the capacity of the site to compensate for
the impacts. Considerations should include: anticipated replacement ratios for wetland mitigation, buffer
conditions and proposed widths, available water to maintain anticipated hydrogeomorphic classes of wetlands
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when restored, proposed flood storage capacity, and potential to mitigate riparian fish and wildlife impacts
(such as connectivity
2. On-site mitigation would require elimination of high-quality upland habitat.
3. Off-site mitigation has a greater likelihood of providing equal or improved wetland functions than the
altered wetland.
4. Off-site locations shall be in the same sub -drainage basin unless:
a. Established watershed goals for water quality, flood storage or conveyance, habitat, or other
wetland functions have been established by the City and strongly justify location of mitigation at another
site, or
b. Credits from a state -certified wetland mitigation bank are used as compensation, and the use
of credits is consistent with the terms of the certified bank instrument,
c. Fees are paid to an approved in -lieu fee program to compensate for the impacts.
d. The design for the compensatory mitigation project needs to be appropriate for its location (i.e.,
position in the landscape). Therefore, compensatory mitigation should not result in the creation,
restoration, or enhancement of an atypical wetland.
F. Timing of Compensatory Mitigation.
1. It is preferred that compensatory mitigation projects be completed prior to activities that will disturb
wetlands. At the least, compensatory mitigation shall be completed immediately following disturbance and
prior to use or occupancy of the action or development. Construction of mitigation projects shall be timed to
reduce impacts to existing fisheries, wildlife, and flora.
2. The Administrator may authorize a one-time temporary delay in completing construction or installation of
the compensatory mitigation when the applicant provides a written explanation from a qualified wetland
professional as to the rationale for the delay. An appropriate rationale would include identification of the
environmental conditions that could produce a high probability of failure or significant construction difficulties
(e.g., project delay lapses past a fisheries window, or installing plants should be delayed until the dormant
season to ensure greater survival of installed materials). The delay shall not create or perpetuate hazardous
conditions or environmental damage or degradation, and the delay shall not be injurious to the health, safety, or
general welfare of the public. The request for the temporary delay must include a written justification that
documents the environmental constraints that preclude implementation of the compensatory mitigation plan.
The justification must be verified and approved by the City.
G. Wetland Mitigation Ratios:
Category and Tvue of
Creation or
Rehabilitation
Enhancement
Wetland
Re-establishment
Category L Bog, Natural
Not considered possible
Case by Case
Case by Case
Heritage Site
dory L Mature
Forested
6_1
12:1
24:1
dory L Based on
functions
4_1
8_1
16:1
dory 11
3:1
6:1
12:1
dory III
2:1
4:1
8:1
dory IV
1.5:1
3:1
6:1
Ratios for rehabilitation and enhancement may be reduced when combined with 1:1 replacement through creation or re-establishment. See Table
lb. Wetland Mitigation in Washington State—Part 1: AgencyPolicies and Guidance --Version 1, (Ecology Publication #06-06-011a, 013mpia,
WA, March 2006 or as revised). See also Paragraph DA for more information on using preservation as compensation.
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H. Credit/Debit Method. To more fully protect functions and values, and as an alternative to the mitigation ratios
found in the joint guidance "Wetland Mitigation in Washington State Parts land -IF (Ecology Publication #06-06-
0I1a b, Olympia, WA, March, 2006), the administrator may allow mitigation based on the "credit/debit" method
developed by the Department of Ecology in "Calculating Credits and Debits for Compensatory Mitigation in
Wetlands ofEastern Washington: Final Reporf (Ecology Publication #11-06-015, August 2012, or as revised).
L Compensatory Mitigation Plan. When a project involves wetland and/or buffer impacts, a compensatory
mitigation plan prepared by a qualified professional shall be required, meeting the following minimum standards:
1. Wetland Critical Area Report. A critical area report for wetlands must accompany or be included
in the compensatory mitigation plan and include the minimum parameters identified in YMC 15.27.3 14 and
15.27.315.B.
2. Compensatory Mitigation Report. The report must include a written report and plan sheets that must
contain, at a minimum, the following elements. Full guidance can be found in Wetland Mitigation in
Washington State Part 2: Developing Mitigation Plans (Version 1) (Ecology Publication #06-06-01 lb,
Olympia, WA, March 2006 or as revised).
a. The written report must contain, at a minimum:
i. The name and contact information of the applicant: the name, qualifications, and contact
information for the primary author(s) of the compensatory mitigation report, a description of the
proposal: a summary of the impacts and proposed compensation concept: identification of all the local,
state, and/or federal wetland -related permit(s) required for the project: and a vicinity map for the
project.
ii. Description of how the project design has been modified to avoid, minimize, or reduce
adverse impacts to wetlands.
iii. Description of the existing wetland and buffer areas proposed to be impacted. Include
acreage (or square footage), water regime, vegetation, soils, landscape position, surrounding lands
uses, and functions. Also describe impacts in terms of acreage by Cowardin classification,
hydrogeomorphic classification, and wetland rating, based on Wetland Ratings, YMC 15.27.603.
iv. Description of the compensatory mitigation site, including location and rationale for
selection. Include an assessment of existing conditions: acreage (or square footage) of wetlands and
uplands, water regime, sources of water, vegetation, soils, landscape position, surrounding land uses,
and functions. -Estimate future conditions in this location if the compensation actions are NOT
undertaken (i.e., how would this site progress through natural succession?).
v. Surface and subsurface hydrologic conditions, including an analysis of existing and proposed
hydrologic regimes for enhanced, created, or restored compensatory mitigation areas. Include
illustrations of how data for existing hydrologic conditions were used to determine the estimates of
future hydrologic conditions
vi. A description of the proposed actions for compensation of wetland and upland areas
affected by the project. Include overall goals of the proposed mitigation, including a description of the
targeted functions, hydrogeomorphic classification, and categories of wetlands.
vii. A description of the proposed mitigation construction activities and timing of activities.
viii. Performance standards (measurable standards for vears Dost -installation) for upland and
wetland communities, a monitoring schedule, and a maintenance schedule and actions proposed by
year.
ix. A discussion of ongoing management practices that will protect wetlands after the
development project has been implemented, including proposed monitoring and maintenance programs
(for remaining wetlands and compensatory mitigation wetlands).
x. A bond estimate for the entire compensatory mitigation project, including the following elements:
site preparation, plant materials, construction materials, installation oversight, maintenance twice per
,year for up to five (5) years, annual monitoring field work and reporting, and contingency actions for a
maximum of the total required number of years for monitoring.
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A Proof of establishment of Notice on Title for the wetlands and buffers on the project site,
including the compensatory mitigation areas.
b. The scaled plan sheets for the compensatory mitigation must contain, at a minimum:
i. Surveyed edges of the existing wetland and buffers, proposed areas of wetland and/or
buffer impacts, location of proposed wetland and/or buffer compensation actions.
ii. Existing topogMphy, ground -proofed, at two -foot contour intervals in the zone of the proposed
compensation actions if aM gig activity is proposed to create the compensation area(s). Also
existing cross-sections of on-site wetland areas that are proposed to be impacted, and cross-section(s)
(estimated one -foot intervals) for the proposed areas of wetland or buffer compensation.
iii. Conditions expected from the proposed actions on site, including future
hydrogeomorphic types, vegetation community types by dominant species (wetland and upland), and
future water regimes.
iv. Required wetland buffers for existing wetlands and proposed compensation areas. Also,
identify any zones where buffers are proposed to be reduced or enlarged outside of the standards
identified in this Chapter.
v. A planting plan for the compensation area, including all species by proposed community type and
water regime, size and type of plant material to be installed, spacing of plants, typical clustering
patterns, total number of each species by community type, and timing of installation.
3. Buffer Mitigation Ratios. Impacts to buffers shall be mitigated at a minimum 1:1 ratio. Compensatory
buffer mitigation shall replace those buffer functions lost from development.
4. Protection of the Mitigation Site. The area where the mitigation occurred and any associated buffer shall be
located in a critical area tract or a conservation easement consistent with YMC 15.27 Part six.
5. Monitoring. Mitigation monitoring shall be required for a period necessary to establish that performance
standards have been met, but not for a period less than five ,years. If a scrub -shrub or forested vegetation
community is proposed, monitoring may be required for ten years or more. The project mitigation plan shall
include monitoring elements that ensure certainty of success for the project's natural resource values and
functions. If the mitigation goals are not obtained within the initial five -,year period, the applicant remains
responsible for restoration of the natural resource values and functions until the mitigation goals agreed to in the
mitigation plan are achieved.
6. Advance Mitigation. Mitigation for projects with pre -identified impacts to wetlands may be constructed in
advance of the impacts if the mitigation is implemented according to federal rules, state policy on advance
mitigation, and state water quality regulations consistent with -Interagency Regulatory Guide: Advance
Permittee -Responsible Mitigation (Ecology Publication #12-06-015, Olympia, WA, December 2012).
7. Alternative Mitigation Plans. The administrative official or designee may approve alternative
wetland mitigation plans that are based on best available science, such as priority restoration plans that achieve
restoration goals identified in the SMP. Alternative mitigation proposals must provide an equivalent or better
level of protection of wetland functions and values than would be provided by the strict application of this
chapter. The administrative official or designee shall consider the following for
approval of an alternative mitigation proposal:
a. The proposal uses a watershed approach consistent with Selecting Wetland Mitigation Sites Using
a Watershed Approach (Eastern Washington) (Ecology Publication #10-06-07, November 2010).
b. Creation or enhancement of a larger system of natural areas and open space is preferable to the
preservation of many individual habitat areas.
c. Mitigation according to Se-EYMC 15.27.605(D) is not feasible due to site constraints such as
parcel size, stream type, wetland category, or geologic hazards.
d. There is clear potential for success of the proposed mitigation at the proposed mitigation site.
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e. The plan shall contain clear and measurable standards for achieving compliance with the specific
provisions of the plan. A monitoring plan shall, at a minimum, meet the provisions in Se z'YMC
15.27.605(�l
f. The plan shall be reviewed and approved as part of overall approval of the proposed use.
g. A wetland of a different type may be justified based on regional needs or functions and values, the
replacement ratios may not be reduced or eliminated unless the reduction results in a preferred
environmental alternative.
h. Mitigation guarantees shall meet the minimum requirements as outlined in geeti&RYNIC 15.27.
8605(�l (2)(a)(viii
i. Qualified professionals in each of the critical areas addressed shall prepare the plan.
J. The City may consult with agencies with expertise and jurisdiction over the critical areas during the
review to assist with analysis and identification of appropriate performance measures that adequately
safeguard critical areas.
Part Seven. Geologically Hazardous Areas
15.27.701 Mapping and designation.
A. Geologically hazardous areas are areas that are susceptible to one or more of the following, based on WAC
365-190-080(4)(b) through (h):
1. Erosion hazards;
2. Landslide hazards, which include:
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a. Oversteepened slopes;
b. Alluvial fan/flash flooding;
c. Avalanche; and
d. Stfeam Channel migration zones and stream undercutting;
3. Seismic hazards (referred to below as earthquake hazards); and
4. Volcanic hazards.
C. The approximate location and extent of geologically hazardous areas are shown on the city's critical area map
titled "Geologically Hazardous Areas of the City of Yakima." The following geologically hazardous areas have been
mapped and classified using the criteria found in WAC 365-190-120
15.27.702 Geologically hazardous areas protection approach.
The geologically hazardous areas protection approach can be met by following the guidelines below and by
implementing the appropriate sections of the Building Code as adopted in YMC Title 11.
A. Erosion Hazard Areas. Protection measures for erosion hazard areas will be accomplished by implementing the
regulatory standards for erosion and drainage control required under YMC Title 11, building code. YMC Title 11
requirements can be met by the application of the Best Management Practices (BMPs) in the Stormwater
ManggementManualfor Eastern Washington StoFm ateF '�^fma (�B9Ecoloy publication number 04-10-076, or
most recent version); equivalent manual adopted by the city of Yakima; or any other approved manual deemed
appropriate by the administrative official.
D. Stream Undercutting Hazard Areas. Protection measures for stream undercutting hazard areas will be
accomplished by critical areas review for flood hazards, and streams, and shafeline jttfisdie4ie .
15.27.703 Development review procedure for geologically hazardous areas.
B. Developments that receive an affirmative determination of hazard by the administrative official under
subsection A of this section must conduct a geologic hazard report as provided in YMC 15.27.315(C), which may be
part of a geotechnical report required below.
1. If the geologic hazard report determines that no hazard exists or that the project area lies outside the
hazard, then no geologic hazard review is needed.
2. The administrative official is authorized to waive further geologic hazard review for oversteepened slopes
on the basis that the hazards identified by the geologic hazard report will be adequately mitigated through
conditions applied to the isstt nee of a grading or construction permit.
Part Eight. Critical Aquifer Recharge Areas (CARA)
15.27.810 Maps and Reference Documentsping.
A. Mapping Methodology. The CARA is depicted in the map titled "Critical Aquifer Recharge Areas of the City
of Yakima" located within the city of Yakima's 2006 2017 Ufbaii AreaComprehensive Plan 20152040. The CARA
map was developed through a geographic information system (GIS) analysis using the methodology outlined in the
"Critical Aquifer Recharge Areas Guidance Document f ..i the Esta l sari. ,p. e
GF4ieal Affaif4 Ree ,,,.,.o Area n,dip ,, ees" (n,,,.r a4io1 No. 9:7 34Yorgan 2005). The approximate location and
extent of critical aquifer recharge areas are depicted on the above-mentioned map, and are to be used solely as a
guide for the city. The CARA map estimates areas of moderate, high, and extreme susceptibility to contamination,
as well as wellhead protection areas. In characterizing the hydrogeologic susceptibility of these recharge areas with
regard to contamination, the following physical characteristics were utilized:
B. Guidance Documents. The latest guidance documents shall be consulted when updating CARA maps:
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1. U.S. Department of Agriculture Soil Survey
hltp:Hwebsoilsurvey.sc.egov.usda.gov/App/WebSoilSurvey.aspx
2. Washington Department of Health Group A and B Maps:
ha2s://fortress.wa.gov/doli/ch/aaps/SWAP/l*ndex.htnil
3. Soil Survey of Yakima County Area, Washington (report only):
hltp:Hnrcs.usda.gov/lntemet/FSE MANUS CRIPTS/washinZon/yakimaWA 1985/vakimaWA 1985-Lpdf
4. City of Yakima Wellhead Protection Plan: http://www.yakimacolMly.us/669/City-of-Yakima-Wellhead-
Protection-Plan
5.—Hydrogeologic Framework of Sedimentary Deposits in Six Structural Basins, Yakima River Basin,
Washington: http://pubs.usgs.gov/sir/2006/5116/pdf/sir20065116.pdf and Yakima Basin plate
http://pubs.us-s.gov/sir/2006/5116/pdf/sir20065116 plate4.pdf
15.27.820 Protection approach.
A. Classification and Rating of Critical Aquifer Recharge Areas. To promote consistent application of the
standards and requirements of this section, Critical Aquifer Recharge Areas within the City shall be rated or
classified according to their characteristics, function and value, and/or their sensitivity to disturbance.
1. Critical Aquifer Recharge Areas Classification. Critical aquifer recharge areas are those areas with a
critical recharging effect on aquifers used for potable water. Wellhead protection involves the management of
activities that have a potential to degrade the quality of groundwater produced by a supply well. The City is
classified into four wellhead protection zones that are based on proximity to and travel time of groundwater to
Group A and Group B water source wells within the City limits, and are designated using guidance from the
Washington Department of Health Wellhead Protection Program pursuant to Chapter 246-290 WAC.
a. Wellhead Protection Zone 1 represents the land area overlying the six-month time -of -travel zone
of any Group A water source well and/or land area overlying any Group B wellhead protection area.
b. Wellhead Protection Zone 2 represents the land area that overlies the one -,year time -of -travel zone
of any Group A water source well, excluding the land area contained within Wellhead Protection Zone 1.
c. Wellhead Protection Zone 3 represents the land area that overlies the five -,year and ten-year time -
of -travel zones of any Group A water source well, excluding the land area contained within Wellhead
Protection Zones 1 or 2.
d. Wellhead Protection Zone 4 represents all the remaining land area in the City not included in
Wellhead Protection Zones 1, 2, or 3.
2, Classification of wellhead protection zones shall be determined in accordance with the City's Wellhead
Protection Plan and the Washington State Department of Health, Office of Drinking Water, Source Water
Assessment Program (SWAP) Mapping Application, which designates time of travel and wellhead protection
zones that correspond to Zones 1 through 4, noted in subsection 1 above.
B. Prohibited Activities in Wellhead Protection Zones.
1. Land uses or activities for new development or redevelopment that pose a significant hazard to the
City's groundwater resources, resulting from storing, handling, treating, using, producing, recycling, or
disposing of hazardous materials or other deleterious substances, shall be prohibited in Wellhead Protection
Zones 1 and 2. These land uses and activities include, but are not limited to:
a. Large on-site sewage systems, as defined in WAC Chapter 246-272A;
b. Hazardous liquid pipelines as defined in RCW Chapter 81.88,
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c. Solid waste landfills or transfer stations, including hazardous or dangerous waste, municipal solid
waste, special waste, wood waste, and inert and demolition waste,
d. Liquid petroleum refining, reprocessing, and storage,
e. Bulk storage facilities,
f Hard rock and sand and gravel mining, unless located within the mineral resource designation,
g. The storage or distribution of gasoline treated with the additive methyl tertiary butyl ether;
h. Hazardous waste treatment, storage, and disposal facilities except those defined under permit by
rule for industrial wastewater treatment processes per WAC 173-303-802(5)(a),
i. Chemical manufacturing, including but not limited to, organic and inorganic chemicals, plastics
and resins, phannaceuticals, cleaning compounds, paints and lacquers, and agricultural chemicals:
J. Da cleaning establishments using the solvent perchloroethylene or similarly toxic compounds:
k. Primary and secondary metal industries that manufacture, produce, smelt, or refine ferrous and
nonferrous metals from molten materials,
1. Wood treatment facilities that allow any portion of the treatment process to occur over permeable
surfaces (both natural and manmade):
m. Mobile fleet fueling operations,
n. Class I, Class III, Class IV, and the following types of Class V wells: 5A7, 5F01, 5D03, 5F04,
5W09, 5W10, 5W11, 5W31, 5X13, 5X14, 5X15, 5W20, 5X28, and 5N24 as regulated under RCW Chapter
90.48 and WAC Chapters 173-200 and 173-218, as amended:
o. Permanent dewatering of the aquifer for new projects and redevelopment,
p. Facilities that store, process, or dispose of radioactive substances: and
g. Irrigation with gxaywater or reclaimed water.
2. Other land uses and activities that the City determines would pose a significant groundwater hazard to
Group A and Group B groundwater supplies within the City limits, or would significantly reduce the recharge to
aquifers currently or potentially used as a potable water source.
C. Wellhead Protection Zone Performance Standards.
1. Activities may only be permitted in a critical aquifer recharge area if the applicant can show that the
proposed activity will not cause contaminants to enter the aquifer and that the proposed activity will not
adversely affect the recharging of the aquifer.
2. Any uses or activities which involve storing, handling, treating, using producing, recycling, or
disposing of hazardous materials or other deleterious substances shall comply with the following standards that
apply to the wellhead protection zone in which they are located. Residential uses of hazardous materials or
deleterious substances are exempt from the following standards.
3. If a property is located in more than one wellhead protection zone, the Director of Community
Development shall determine which standards shall aply based on an assessment evaluation of the risk posed
by the facility or activity. The assessment evaluation shall include, but not be limited to:- (a) the location, type,
and quantity of the hazardous materials or deleterious substances on the property: (b) the geographic and
geologic characteristics of the site: and (c) the type and location of infiltration on the site.
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4. Development within Wellhead Protection Zones 1 or 2, and any facility or activity existing as of
adoption of this Title within which hazardous materials or other deleterious substances are present, shall
implement the following relevant performance standards:
a. Secondary Containment.
i. The owner or operator of any facility or activity shall provide secondary containment for
hazardous materials or other deleterious substances in aggregate quantities equal to or greater than 20
gallons liquid or 200 pounds solid or in quantities specified in the Yakima Fire Code, YMC Chapter
10.05, whichever is smaller.
ii. Hazardous materials stored in tanks that are subject to regulation by the Washington State
Department of Ecology (Ecology) under WAC Chapter 173-360, Underground Storage Tank
Regulations, are exempt from the secondary containment requirements of this section, provided that
documentation is provided to demonstrate compliance with those regulations.
b. Vehicle Fueling, Maintenance, and Storage Areas. Fleet and automotive service station fueling,
equipment maintenance, and vehicle washing areas shall have a containment system for collecting and
treating all runoff from such areas and preventing release of fuels, oils, lubricants, and other automotive
fluids into soil, surface water, or groundwater. Appropriate emergency response equipment and spill kits
shall be kept on-site during transfer, handling, treatment, use, production, recycling, or disposal of
hazardous materials or other deleterious substances.
c. Loading and Unloading Areas. Secondary containment or equivalent Best Management Practices
(BMPs), as approved by the Director of Public Works, shall be required at loading and unloading areas that
store, handle, treat, use, produce, recycle, or dispose of hazardous materials or other deleterious substances
in aggregate quantities equal to or greater than 20 gallons liquid or 200 pounds solid.
d. Stormwater Infiltration Systems. Design and construction of new stormwater infiltration Vstems
must address site-specific risks of releases posed by all hazardous materials on-site. These risks may be
mitigated by physical design means or equivalent BMPs in accordance with an approved Hazardous
Materials Management Plan. Design and construction of said stormwater infiltration systems shall also be
in accordance with YMC Chapter 7.83 and the latest edition of the Stormwater Management Manual for
Eastern Washington, approved local equivalent, or another technical stormwater manual approved by
Ecology, and shall be certified for compliance with the requirements of this section by a professional
engineer or engineering geologist registered in the State of Washington.
e. The record and construction details of any well regulated under Chapter 173-160 WAC,
Construction and Maintenance of Wells, and any well excluded per WAC 173-160-010(2) that is
constructed or decommissioned in Zones 1 and 2, shall be provided to the Department of Community
Development within 60 days of well completion or decommissioning.
f. Protection Standards During Construction. The following standards shall apply to construction
activities occurring where construction vehicles will be refueled on-site and/or the quantity of hazardous
materials that will be stored, dispensed, used, or handled on the construction site is in aggregate quantities
equal to or greater than 20 gallons liquid or 200 pounds solid, exclusive of the quantity of hazardous
materials contained in fuel or fluid reservoirs of construction vehicles. As part of the City's project
permitting process, the City may require any or all of the following items:
i. A development agreement,
ii. Detailed monitoring and construction standards:
iii. Designation of a person on-site during operating hours who is responsible for supervising the
use, storage, and handling of hazardous materials and who has appropriate knowledge and training to
take mitigating actions necessary in the event of fire or spill,
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iv. Hazardous material storage, dispensing, refueling areas, and use and handling areas shall be
provided with secondary containment adequate to contain the maximum release from the largest
volume container of hazardous substances stored at the construction site,
v. Practices and procedures to ensure that hazardous materials left on-site when the site is
unsupervised are inaccessible to the public. Locked storage sheds, locked fencing, locked fuel tanks
on construction vehicles, or other techniques may be used if they will preclude access,
vi. Practices and procedures to ensure that construction vehicles and stationary equipment that
are found to be leaking fuel, hydraulic fluid, and/or other hazardous materials will be removed
immediately or repaired on-site immediately. The vehicle or equipment may be repaired in place,
provided the leakage is completely contained,
vii. Practices and procedures to ensure that storage and dispensing of flammable and
combustible liquids from tanks, containers, and tank trucks into the fuel and fluid reservoirs of
construction vehicles or stationary equipment on the construction site are in accordance with the
Yakima Fire Code, YMC Chapter 10.05, and
viii. Practices and procedures, and/or on-site materials adequate to ensure the immediate
containment and cleanup of any release of hazardous substances stored at the construction site. On-site
cleanup materials may suffice for smaller spills whereas cleanup of larger spills may require a
subcontract with a qualified cleanup contractor. Releases shall immediately be contained, cleaned up,
and reported if required under state or federal law. Contaminated soil, water, and other materials shall
be disposed of according to state and local requirements.
g. Fill Materials. Fill material shall comply with the standards in YMC Chapter 7.82 and the
following:
i. Fill material shall not contain concentrations of contaminants that exceed cleanup standards
for soil specified in WAC 173-340-740, Model Toxics Control Act, regardless of whether all or part of
the contamination is due to natural background levels at the fill source site. Where the detection limit
(lower limit at which a chemical can be detected by a specified laboratory procedure) for a particular
soil contaminant exceeds the cleanup standard for soil specified in WAC 173-340-740, the detection
limit shall be the standard for fill material quality.
ii. Fill materials in quantities greater than 10 cubic yards placed directly on or in the ground in
excess of six months shall meet the following requirements:
1. A fill material source statement shall be provided to the Department of Community
Development and shall be reviewed and accepted by the Department prior to stockpiling or
rig imported fill materials at the site. The source statement shall be issued by a professional
engineer, geologist, engineering geologist or hydrogeologist licensed in the State of Washington
demonstrating the source's compliance with standards of the Model Toxics Control Act. The
source statement shall be required for each different source location from which fill will be
obtained.
2. Analytical results demonstrating that fill materials do not exceed cleanup standards
specified in WAC 173-340-740 may be used in lieu of a fill material source statement, provided
the regulated facility submits a sampling plan to, and which is approved by, the Director of
Community Development. The regulated facility must then adhere to the approved sampling plan,
and maintain analytical data on-site and available for inspection for a minimum of five years from
the date that the fill was accepted.
iii. The Department of Community Development may accept a fill material source statement that
does not include results of sampling and analysis of imported fill if it determines that adequate
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information is provided indicating that the source location is free of contamination. Such information
may include, but is not limited to:
1. Results of field testing of earth materials to be imported to the site with instruments
capable of detecting the presence of contaminants: or
2. Results of previous sampling and analysis of earth materials to be imported to the
site.
iv. A fill material source statement is not required if documents confirm that imported fill will be
obtained from a Washington State Department of Transportation approved source.
v. The Director of Community Development shall have the authority to require corrective
measures regarding noncompliant fill materials, including independent sampling and analysis, if the
property owner or operator fails to accomplish such measures in a timely manner. The property owner
or operator shall be responsible for any costs incurred by the City in the conduct of such activities.
h. Cathodic Protection Wells. Cathodic protection wells shall be constructed such that the following
do not occur.
i. Vertical cross -connection of aquifers normally separated by confining units,
ii. Migration of contaminated surface water along improperly sealed well borings or casings:
iii. Introduction of electrolytes or related solutions into the subsurface, and
iv. Any of the above conditions caused by improperly abandoned cathodic protection wells that
are no longer in use.
i. Underground Hydraulic Elevator Cylinders. All underground hydraulic elevator pressure
cylinders shall be encased in an outer plastic casing constructed of Schedule 40 or thicker -wall
polyethylene or polyvinyl chloride pipe, or equivalent The plastic casing shall be capped at the bottom,
and all joints shall be solvent- or heat -welded to ensure water tightness. The neck of the plastic casing shall
provide a means of inspection to monitor the annulus between the pressurized hydraulic elevator cylinder
and the protective plastic casing.
j. Best Management Practices (BMPs). All development or redevelopment shall implement
BMPs for water quality and quantity, as approved by the Director of Community Development, such as
biofiltration swales and use of oil -water separators, BMPs appropriate to the particular use proposed,
clustered development, and limited impervious surfaces.
5. Development within Wellhead Protection Zone 3 shall implement appropriate BMPs and comply with
the performance standards for vehicle fueling, maintenance, and storage areas: loading and unloading areas,
well construction and operation: fill materials: cathodic protection wells: and underground hydraulic elevator
cylinders in applicable subsections in C.4 of this section.
6. Development within Wellhead Protection Zone 4 shall implement BMPs for water quality and
guanti1y.
7. An incremental environmental improvement to a system protective of groundwater shall not alter,
expand, or intensify an existing legal nonconformance, but may proceed without having to meet the following
City codes:
a. Restrictions associated with critical areas and critical area buffers, if the footprint of the
original system protective of groundwater is located within the same critical area buffer, and it can be
demonstrated through BAS that there will be no significant adverse impacts to the critical area and its
buffer,
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b. AM requirement to bring all or aM portion of the facility or the development it serves up to
current building, fire, or land use codes that is triggered by the value or design of the incremental
environmental improvement to a system protective of groundwater: and
c. The incremental improvement shall not qualify as a redevelopment that would otherwise be
prohibited by Title 15 YMC.
YMC Title 17 SHORELINES
17.01.090 Definitions.
"Fill" means the addition of soil, sand, rock, gravel, sediment, earth retaining structure, or other material to an area
waterward of the OHWM, in wetlands, or on shorelands in a manner that raises the elevation or creates dry land. The
physical structure of a she -bank stabilization structure shall not be considered fill. However, fill placed behind the
structure is considered fill. Stream bed manipulation for irrigation diversions or restoration shall not be considered fill.
"Fish and wildlife habitat conservation" means land management for maintaining populations of species in suitable
habitats within their natural geo aphic distribution so that the habitat available is sufficient to support viable
populations over the long term and isolated subpopulations are not created. This does not mean maintaining all
individuals of all species at all times, but it does mean not degrading or reducing populations or habitats so that they
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are no longer viable over the long term. Counties and cities should engage in cooperative planning and coordination
to help assure long term population viability.
"Fish and wildlife habitat conservation areas" are areas that serve a critical role in sustaining needed habitats and
species for the functional integrity of the ecosystem, and which, if altered, may reduce the likelihood that the species
will persist over the long term. These areas may include, but are not limited to, rare or vulnerable ecological
systems, communities, and habitat or habitat elements including seasonal ranges, breeding habitat, winter range, and
movement corridors, and areas with high relative population density or species richness. Counties and cities may
also designate locally important habitats and species. Fish and wildlife habitat conservation areas does not include
such artificial features or constructs as irrigation deliversystems, irrigation infrastructure, irrigation canals, or
drainage ditches that lie within the boundaries of, and are maintained by, a port district or an irrigation district or
compaM.
"Habitats of local importance" are designated as fish and wildlife habitat conservation areas based on a finding by
the city that they are locally important.
Felated efitieal areas (44R-GA�" iiiehide all 4ies;e -A-veas 44q- 44-41G, 117.0-9.030(C4 A4thilithe eit-,, E4
., 1.;,.4 we ,,,- a+A .,,4a aos@F- ; „F „�o,.�;,,,� 4 B414, of their- ..,,,,o F the F,,p,.tf ,4pd ;
"OrdinM high water mark" (OW M) means that mark on lakes and streams which will be found by examining the bed
and banks and ascertaining where the presence and action of waters are so common and usual, and so long continued in
ordinM years, as to mark upon the soil or vegetation a character distinct from that of the abutting upland. Provided, that
in any area where the ordinM high water line cannot be found, the ordinM high water line is the elevation of the mean
annual flood.
"Scour" means the removal of underwater material by waves and currents, especially at the base or toe of a shoo -c -bank
stabilization or other in -water structure.
"Species of local importance" are those species that are of local concern due to their population status or their
sensitivity to habitat alteration or that are game species.
der," as 'ased 41 this title,
"Vegetative buffer" or "buffer" means an area extending landward from the ordinary high water mark of a lake or stream
and/or from the edge of a wetland which is maintained or otherwise allowed to provide, under optimal conditions,
adequate soil conditions and native vegetation for the performance of the basic functional properties of a fish and wildlife
conservation area�r, wetland and other hydrologically related critical areas as set forth in YMC 17.09.030(E)
(Functional Properties) and YMC 17.09.040(D) (Wetland Functions and Rating). It is understood that optimal conditions
do not always exist due to degradation of the vegetative buffer before establishment of this title, or due to colonization by
nonnative species. Such conditions still provide functional properties, though at a lower level, depending on the difference
from natural conditions.
"Waters of the state" are all lakes, rivers, ponds, streams, inland waters, underground waters, salt waters, and all
other surface waters and watercourses within the jurisdiction of the state of Washineton.
17.09.020 Flood hazard areas.
FLOODWAY FRINGE USES
J. Permitted Uses. The following uses are permitted in the floodwainge areas:
1. Permitted Uses. Any use permitted in the zoning district in accordance with YMC Title 15 and in the
environment designation in accordance with this title, unless prohibited by subsection K of this section, that said
use is in compliance with the flood hazard protection standards of YMC 17.09.020(H) and other applicable
provisions of this Title and will have a negligible effect upon the floodway in accordance with the floodway
encroachment provisions of YMC 17.09.020(J)(2).
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2. All new encroachments. including fill. new construction and other development. if certification by a
registered professional engineer is provided demonstrating through hydrologic and hydraulic analysis
performed in accordance with standard engineering practice that the effect of the subject encroachment
together with the cumulative effects of all similar potential encroachments shall not materially cause water
to be diverted upland of the established floodway fringe, cause erosion, obstruct the natural flow of water,
reduce the car it ing cUacity of the floodway, or result in any increase in flood levels during the occurrence
of the base flood discharge,
3. All new encroachments, including fill, new construction and other development if:
a. The new encroachment is separated from the waterbod by an existing public roadwalegal
development.
b. The new encroachment is located in a residential zone with a density of greater than 1 unit per acre.
4. Utility Transmission Lines. Utility transmission lines shall be permitted when consistent with YMC Title 15
and where not otherwise inconsistent with this section, except that when the primary 12=ose of such a
transmission line is to transfer bulk products or energy through a floodwainge or special flood hazard area,
such transmission line shall conform to the following:
a. Electric transmission lines shall cross floodway fringe and special flood hazard areas by the most direct
route feasible. When support towers must be located within floodwainge or special flood hazard areas,
they shall be placed to avoid high floodwater velocity and/or depth areas, and shall be adequately
floodproofed.
b. Buried utility transmission lines transporting hazardous materials, including but not limited to crude and
refined petroleum products and natural gas, shall be buried a minimum of four feet. Such burial depth shall
be maintained within the floodway fringe or special flood hazard area to the maximum extent of potential
channel migration as determined byhydrolog c� analyses. All such hydrologic analyses shall conform to
requirements of YMC 17.05.060(C)(3)(c).
c. Beyond the maximum extent of potential channel migration, utility transmission lines transporting
hazardous and nonhazardous materials shall be buried below existing natural and artificial drainage features.
d. Aboveground utility transmission lines, not including electric transmission lines, shall only be allowed
for the transportation of nonhazardous materials. In such cases, applicants must demonstrate that line
placement will have no appreciable effect upon flood depth, veloci , or passage. Such lines shall be
adequately protected from flood damage.
e. Aboveground utility transmission line appurtenant structures, including valves, pumping stations or other
control facilities, shall not be permitted in floodway fringe or special flood hazard areas except where no
other alternative is available, or in the event a floodway fringe or special flood hazard location is
environmentally preferable. This does not apply to domestic water and regional wastewater transmission
pipes. In such instances, aboveground structures shall be located so that no appreciable effect upon flood
depth, veloci , or passage is created, and shall be adequately floodproofed.
5. Any use permitted in the zoning district in accordance with YMC Title 15, unless prohibited by YMC
17.09.0200(1-4) above Daypermitted if a study is prepared byqualified individual, in accordance with this
Title_ that addresses whether the encroachment would have an adverse impact on fish and wildlife and/or
floodplain functions.
K. Prohibited Uses.
The following uses are prohibited in the floodwainge areas:
1. Any structure, including manufactured homes and the expansion of manufactured home/parks, designed for
or to be used for human habitation of a permanent nature (including temporary dwellings authorized by YMC
15.04.130 and 15.04.140) that does not meet the criteria in YMC 17.09.0200(1-5)?` ew m^,,,,a ^,,,fe ,ievae
e as
2. Any new encroachments, including fill, new construction and other development, unless certification by a
registered professional engineer is provided demonstrating through hydrologic and hydraulic analysis
performed in accordance with standard engineering practice that the effect of the subject encroachment
together with the cumulative effects of all similar potential encroachments shall not materially cause water to
be diverted upland of the established floodway fringe, cause erosion, obstruct the natural flow of water,
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reduce the carr ing capacity of the floodway fringe, or result in any increase in flood levels during the
occurrence of the base flood discharge:
3. Construction or reconstruction of residential structures within the designated floodway fringe, except for:
a. Repairs, reconstruction, or improvements to a structure which do not increase the ground floor area,
and
b. Repairs, reconstruction or improvements to a structure, the cost of which does not exceed fifty percent
of the assessed value of the structure either:
1. Before the repair, reconstruction or improvement is started: or
2. If the structure has been damaged and is being restored, before the damage occurred.
c. Work done on structures to correct existing violations of existing health, sanitaa or safety codes, or to
structures identified as historic places, shall not be included in the fifty percent.
d. If subsection 2 of this section is satisfied, all new construction and substantial improvements shall
comply with all applicable flood hazard reduction provisions of Part Four.
FLOODWAY USES
L. Permitted Uses. Permitted uses include anv use permitted in the zoning district in accordance with YMC Title 15 and
in the environment designation in accordance with this title; provided, that said use is in compliance with the flood hazard
protection standards of subsections H and I of this section, YMC 17.05.050 and other applicable provisions of this title,
and will have a negligible effect upon the floodway as certified by a registered professional engineer through hydrologic
and hydraulic analysis performed in accordance with standard engineering eering practice. The analysis must demonstrate that the
effect of the subject encroachment together with the cumulative effects of all similar potential encroachments shall not:
1. Materially cause water to be diverted from the established floodway;
2. Cause erosion
3. Obstruct the natural flow of water,
4. Reduce the caMing capacity of the floodway; or
5. Result in any increase in flood levels during the occurrence of the base flood discharge.
M. Prohibited Uses. The following uses/developments are prohibited in the floodwa :
1. Any structure, including manufactured homes, designed for or to be used for human habitation of a permanent
nature (including temporary dwellings authorized by YMC 15.04.130 and 15.04.140),
2. Any encroachments, including fill, new construction and other development unless demonstrated by a
registered professional engineer through hydrologic and hydraulic analysis performed in accordance with standard
engineering eering practice that the effect of the subject encroachment together with the cumulative effects of all similar
potential encroachments shall materially cause water to be diverted from the established floodway, cause erosion,
obstruct the natural flow of water, reduce the caMing capacity of the floodway, or result in any increase in flood
levels during the occurrence of the base flood discharge
3. Aboveground utility transmission line appurtenant structures, including valves, pumping stations, or other
control facilities, shall not be permitted in the floodway, except for domestic water and regional wastewater
facilities where necessary;
4. Where a floodway has not been determined by12reliminaror2s of Engineers' investigations or official
designation, a floodway shall be defined by qualified engineering work b, tepplicant on the basis of a verified
one -hundred -year flood event,
5. Construction or reconstruction of residential structures within designated floodways, except as allowed under
Chapter 17.11 YMC;
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6. The construction or storage of any object subject to flotation or movement during flood level periods,
7. The following uses, due to their high degree of incompatibility with the purpose of establishing and
maintaining a functional floodway, are specifically prohibited:
a. The filling of wetlands, except as authorized under YMC 17.09.030, Fish and wildlife habitat and the
stream corridor system, and YMC 17.09.040, Wetlands,
b. Solid waste landfills, dumps, junkyards, outdoor storage of vehicles, and/or materials; and
C. Damming or relocation of any watercourse that will result in any downstream increase in flood levels
during the occurrence of the base flood discharge (see YMC 17.09.0300).
8. The listing of prohibited uses in this section shall not be construed to alter the general rule of statutory
construction that any use not permitted is prohibited.
N. Nonconforming Uses and Structures. Existing structures and uses within the special flood hazard areas established by
this section or amendments thereto, which were lawful before these sections were adopted or amended, but which would
be prohibited, or restricted under the terms of this section or future amendment, are governed under Chapter 17.11 YMC.
17.09.030 Fish and wildlife habitat and the stream ^ , ,char s stemconservation areas.
A. Purpose and Intent.
Affld- 11o.i - �a ; . f f ;io �a i ; i is io� of .;^� i ; f i^ sails, water, o..;^� �a . ;ldl;fo
Policies and standards to help conserve and protect fish and wildlife habitat conservation areas are designed to accomplish
the following:
1. Meet the requirements of the Shoreline Management Act (Chapter 90.58 RCW) re ag rding *4^ as@ ^f
best available science that is
applicable to the issues of concern,
2. '-
4. Pr-eNjde
Require consideration of alternatives for necessary development, construction, and uses
within fish and wildlife habitat
conservation areas,
43. Prevent decline in the quantijy and quality of surface and subsurface waters,
64. Conserve, restore, and protect fish and wildlife habitats, vegetation, and ecological relationships,
�5. Protect ^r^^, ^f the *r^^m coFFi ^r fish and wildlife habitat conservation areas from the potential
negative effects of development through coordinated land use planning, and,
96. Dr^^ a^ ^r^*p^*i^^ T ^*l^^a 44^^*i^^, aH A -+4+@ -,Protect fish and wildlife habitat conservation areas
through voluntary agreements or government incentives.
B. Protection Approach.
1. To maintain fish and wildlife habitat, there must be adequate environmental conditions for reproduction,
foraging, resting, cover, and dispersal of animals. Factors affecting both habitat and its quality include the presence
of essential resources such as food, water, cove , and lack of disturbance and diseases. The
city of Yakima protects fish and wildlife habitat through:
a. Designation offish and wildlife habitat conservation areas; and
b. Dr^.o *;^^ of habitat for- S^o^;oss i^^^*oa ^o^r thP, t !ffApplication of development standards based on best
available science to proposed activity and development in or near fish and wildlife habitat conservation areas.
T-140 gi „f V.,I4,14a,S .,,.14 to „�o,.�;.. ♦1.,-0.,�o..oa .. a.,., roa ra �;�;. oSigess 14ab;t.,t is 1.
DESIGNATION AND MAPPING
C
.,f t o fella i+ �Designation: Fish and wildlife habitat conservation areas are those habitat areas that
meet any of the criteria listed below:
1. Areas with which state and federal endangered, threatened, and sensitive species have a primary
association,
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2. Habitats and species of local importance:
3. Naturally occurring ponds under 20 acres and their submerged aquatic beds that provide fish or wildlife
habitat,
4. Waters of the state, including any required buffers and associated Federal Emergency Management
Agency -mapped floodplains and floodways,
5. Lakes, ponds, streams, and rivers planted with game fish by a governmental or tribal entity: and
6. State natural area preserves, natural resource conservation areas, and state wildlife areas.
D. Habitat and Habitats of Local Importance.
1. 44s; „v local e r .„hatsOr- Sigesip; that a„o to .r o; ao i;�;� iqqiqa!a4q+I, o ;.;. ; to
oa,, o the i;voi;499 t4at t4@ 0 0 , ;n 4:RAP. ;� ffia ro a,, o aver- .i o , .o All species and habitats
identified by WDFW's Priority Habitats and Species program that maybe found in the city of Yakima are
designated as fish and wildlife habitat conservation areas and afforded protection under this chapter.
3. Development Standards. Projects located within habitats of local importance, or within 200 feet of species of
local importance, as designated in subsection (D)(1) of this section, shall mPP* the, 4apd-Ar4l beta ,, r^*4or *h^^
comply with the applicable development standards in subsections I through P of this section, Hfile .s r-eN-ie .. ;. �
In addition, pgrojects shall be designated using many eg ment
recommendations established for the species or habitat by federal and state agencies, or those adopted for species
and habitats of local importance by the city of Yakima. The department shall consider the extent such
recommendations are used in its decision on the proposal, and may consider recommendations and advice from
agencies with expertise.
E. Functional Properties.
1. °*r@a+14S, �� ^^^a� ^^a ., *�^^a�Aquatic fish and wildlife habitat conservation areas require a sufficient
riparian area to support one or more of the following functional properties:
a. 44@a+rrStabilizing banks
b. Providing a sufficient shade canopy to maintain water temperatures that support fish and their habitat,
c. Moderatingthe he impact of stormwater runoff,
d. Filtering solids, nutrients and harmful substances,
e. Preventing Ssurface erosion;
f Providing and maintaining- migratory corridors for wildlife,
g. Providing food in the form of various insects and other benthic macroinvertebrates,
h. Supporting a diversity of wildlife habitats; or
i. Allowing for the natural occurrence of woody debris and organic matter to collect in the aquatic
environment.
F °*r@^msrakes aR P-9 Water Typing System. For purposes of this chapter, the city of Yakima herebypts
the WAC 222-16-031 Interim water typing system, for those features designated as
critical areas in subsection C of this section as follows:
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1. Type 1 st-��^ waters are those waters, within their ordinM high water mark (OHWM), meeting the criteria
as "shorelines of the state" and "shorelines of statewide significance" under Chapter 90.58 RCW. Other waters
associated with Type 1 waters are not considered Type 1 waters,
2. Type 2 waters means segments of natural waters which are not classified as Type 1 Water and
have a high fish, wildlife, or human use. These are segments of natural waters and periodically inundated
areas of their associated wetlands, which:
a. Are diverted for domestic use by more than 100 residential or camping units or by a public
accommodation facility licensed to serve more than 10 persons, where such diversion is determined by
the department to be a valid appropriation of water and only considered Type 2 Water upstream from
the point of such diversion for 1,500 feet or until the drainage area is reduced by 50 percent, whichever
is less,
b. Are diverted for use by federal, state, tribal or private fish hatcheries. Such waters shall be
considered Type 2 Water upstream from the point of diversion for 1,500 feet, including tributaries if
highly significant for protection of downstream water quality. The department may allow additional
harvest beyond the requirements of Type 2 Water designation provided by the department of fish and
wildlife, department of ecology, the affected tribes and interested parties that:
1. The management practices proposed by the landowner will adequately protect water quality for
the fish hatchery: and
2. Such additional harvest meets the requirements of the water type designation that would appy
in the absence of the hatchery:
3. Are within a federal, state, local or private campground having more than 30 camping units:
Provided, That the water shall not be considered to enter a campground until it reaches the
boundary of the park lands available for public use and comes within 100 feet of a camping unit.
4. Are used by fish for spawning, rearing or migration. Waters having the following
characteristics are presumed to have highly significant fish populations:
i. Stream segments having a defined channel 20 feet or greater within the bankfull width and
having a gradient of less than 4 percent.
ii. Lakes, ponds, or impoundments having a surface area of 1 acre or greater at seasonal low
water; or
5. Are used by fish for off -channel habitat. These areas are critical to the maintenance of optimum
survival of fish. This habitat shall be identified based on the following criteria:
i. The site must be connected to a fish bearing stream and be accessible during some period
of the year, and
ii. The off -channel water must be accessible to fish through a drainage with less than a 5%
gradient.
listed ;.. A ..a;* R „F�
3. Type 3 waters means segments of natural waters which are not classified as Type 1 or 2 Waters and have
a moderate to slight fish, wildlife, or human use. These are segments of natural waters and periodically
inundated areas of their associated wetlands which:
a. Are diverted for domestic use by more than 10 residential or camping units or by a public
accommodation facility licensed to serve more than 10 persons, where such diversion is determined by
the department to be a valid appropriation of water and the only practical water source for such users.
Such waters shall be considered to be Type 3 Water upstream from the point of such diversion for 1,500
feet or until the drainage area is reduced by 50 percent, whichever is less:
b. Are used by fish for spawning, rearing or migration. The requirements for determining fish use are
described in the board manual section 13. If fish use has not been determined:
1. Waters having any of the following characteristics are presumed to have fish use:
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a. Stream segments having a defined channel of 3 feet or greater in width, and having a
gradient of 16 percent or less,
b. Stream segments having a defined channel of 3 feet or greater within the bankfull width,
and having a gradient greater than 16 percent and less than or equal to 20 percent, and having
greater than 175 acres contributing basin size, based on h, dro abWe boundaries,
c. Ponds or impoundments having a surface area of less than 1 acre at seasonal low water and
having an outlet to a fish stream,
d. Ponds of impoundments having a surface area greater than 0.5 acre at seasonal low water.
2. The department shall waive or modify the characteristics in (i) of this subsection where:
a. Waters have confirmed, long term, naturally occurring water quality parameters incapable
of supporting fish,
b. Snowmelt streams have short flow cycles that do not support successful life history phases
of fish. These streams typically have no flow in the winter months and discontinue flow by
June 1; or
c. Sufficient information about a geomorphic region is available to support a departure from
the characteristics in (i) of this subsection, as determined in consultation with the department of
fish and wildlife, department of ecology, affected tribes and interested parties.
Wall „� �.,-o,,,ti., ., ;thip tl.o ..;h .,F V.,L;,ti.., pot ..1„�,;i4V a „S T o 1 ,,,- 7 (soo 34442 17 nl non
o t St+ ».
4. Type 4 s*--�m- waters means all segments of natural waters within the bankfull width of defined channels
that are perennial nonfish habitat streams. Perennial streams are flowing waters that do not go dry any time of
a year of normal rainfall and include the intermittent dry portions of the perennial channel below the
uppermost point of perennial flow.
� (see )AiTh 1:7.01.090, st--y-af .11 -
5. Type 5 waters means all segments of natural waters within the bankfull width of the defined channels that
are not Type 1, 2, 3, or 4 Waters. These are seasonal, nonfish habitat streams in which surface flow is not
present for at least some portion of the ,year and are not located downstream from any stream reach that is a
Type 4 Water. Type 5 Waters must be physically connected by an above -ground channel system to Type 1, 2,
3, or 4 Waters.��r-P-. ,.... —Ave ,.n eigheiiie .,.i ..t..,,,.,..... I4-W4R �x , of v,.kiff ,, iiat el- s.i€ied as 4A,ige 1, ' i�
6. Lakes and Ponds.
a. Lakes and ponds not designated as a shoreline that receive water from the OHWM of a Type 2, 3, or 4
stream shall have the same surface water type as the highest stream type from which the lake or pond
receives water.
b. Natural lakes and ponds, not designated as a shoreline, that do not receive water from the OHWM of a
Type 1, 2, 3, or 4 stream shall be Type 3 ponds.
0. r„ @S +14S +let 40 +lawd- as i oi;�o #h -at o .oa to „ T o f
r xx o.i �a Rati+ cv40+14.
foupa ip vrar 1:7.09.040"(2,
H. Maps. Certain fish and wildlife habitat ^^a related or-itiga4conservation areas have been inventoried
and are depicted on a series of taper and electronic maps. The maps do not officially define the extent or characteristics of
specific critical areas, but rather the potential physical boundaries and characteristics. Maps may be both regulator, and
nonregulatory in nature as described below:
1. Regulatory maps include any floodway or floodplain identified as a special flood hazard area by the Federal
Emergencygement Agency (FEMA) as identified in the flood insurance studies (FIRMs).
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2. Informational maps indicate the approximate presence, location and/or typin of f the potential critical area.
Informational maps include, but are not limited to, the following_
a. Wetlands-,
b. Streams,
C. Channel migration zone; and
d. Species and habitats of local importance. Note: This map will be generated at such a time when the city_
of Yakima formally adopts a species or habitat of local importance.
3. Other nonre ug latory information sources include maps or other data sources, but are not limited to:
a. Comprehensive flood hazard management plans,
b. Soil survey of the city of Yakima,
c. Surface geologic maps;
d. Historic and current aerial photo series; and
e. Geohydraulic studies—geologic cross-sections showing aquifers and confining units.
GENERAL DEVELOPMENT STANDARDS
L Prohibited Uses. The following uses and activities are prohibited within a designated ted fish
and wildlife habitat conservation area:
1. Storage, handling, and disposal of material or substances that are dangerous or hazardous with respect to water
quality and life safety,
2. The placement of mining tailings, spoilage, and mining waste materials, except for that associated with the
mining ofrg avel,
3. The draining or filling of a wetland, lake or pond, except as provided for in YMC 17.07.060(B),
4. The removal and transport of material for fill outside of the stream corridor,
5. Site runoff storage ponds, holding tanks and ponds, and other similar waste disposal facilities. Note: This
provision does not include regional wastewater plant facilities, collection pipes, septic systems approved by a local
or state agency, and other related facilities,
6. Solid waste disposal sites,
7. Automobile wrecking yards,
8. Fill for the sole purpose of increasing land area within the stream corridor,
9. Uses located within the floodway fringe that are listed in YMC 17.09.020(x); and
10. Uses located within the floodway that are listed in YMC 17.09.020(M).
J. General Policies and Standards. The following policies and standards shall apply to any development, construction, or
use carried out within a designated ted hydrologically related critical area:
1. The ordinM high water mark of a stream or lake, and the edge of a wetland, shall be marked on the ground
before any development, construction, or use is initiated,
2. Existing vegetation and any vegetative species pertinent to the critical area identified on the project site within
the stream corridor shall only be disturbed to the minimum extent possible;
3. Nesting areas and other sensitive habitat identified within a stream corridor shall be disturbed to the minimum
extent possible,
4. Projects within the stream corridor shall be scheduled to occur at times and during seasons having the least
impact to spawning, nesting, or other sensitive wildlife activities. Scheduling recommendations from the
appropriate state and/or federal agency may be considered,
5. The following measures are incorporated into stormwater permits approved by a local, state or federal agency
and transportation prof ects using the Stormwater Management Manual for Eastern Washington. Developments that
do not require a stormwater permit shall also incorporate the following elements into project design
a. Excavation, grading, cut/fills, compaction, and other modifications which contribute to erosion of soils
shall be confined to the minimum necessary to complete the authorized work and avoid increased sediment
load,
b. The removal of ground -cover vegetation, excavation, and grading shall be scheduled for periods when
soils are the least vulnerable to erosion, compaction and movement unless suitable protective measures are
used to prevent erosion,
c. Increases in impervious surface area, compaction of soil, changes in topography, and other modifications
of land within a stream corridor shall provide on-site facilities for detention, control, and filtration if potential
increases have been identified to occur_
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d. The discharge point for controlled stormwater runoff shall be designed and constructed to avoid erosion,
and
e. Matting or approved temporary ground cover shall be used to control erosion until natural vegetative
ground cover is successfully established,
6. Prior to the approval of development, construction, or uses within a designated stream corridor, any existing
source of biochemical or thermal degradation identified as originating on the prof ect property shall be corrected,
7. Facilities which use fertilizers, pesticides or herbicides shall use landscaping, low-risk products, application
schedules, and other protective methodology to minimize the surface and subsurface transfer of biochemical
materials into the stream corridor,
8. Modifications to natural channel gradient, channel morphology, drainage patterns, and other stream features
shall not permanently alter or obstruct the natural volume or flow of surface waters,
9. Development, construction, or uses within the stream corridor shall not alter or divert flood flows, cause
channel shift, erosion, and increase or accelerate the flooding of upstream or downstream flood hazard areas,
10. Structures placed inclose proximity to the outer edge of bends in stream channels shall be located to
minimize the hazard from stream undercutting and stream bank erosion stemmingfrom rom potential future stream
nu ragr tion;
11. The Department of Ecology and adjacent communities shall be notified prior to any alteration or relocation of
a watercourse and evidence of such notification shall be submitted to the Federal Emergency Management Agency,
12. Maintenance shall be provided for the altered or relocated portion of said watercourse so that the flood-
canying capacity is not diminished,
13. Development shall not obstruct, cut off, or isolate stream corridor features,
14. Nothing in these regulations shall constitute authori , of M person to trespass or in any wage upon
the rights of private ownership,
15. Projects located within the floodway must meet the requirements of YMC 17.09.020(L), and
16. AU portion of the vegetative buffer temporarily damaged or disturbed as a result of construction activities
(excluding approved permanent use areas) shall be repaired at the completion of construction using the reclamation
found in subsection Q of this section.
WATER DEPENDENCY DEVELOPMENT STANDARDS AND BUFFER REQUIREMENTS
K. Use Classifications. For Durnoses of this section_ the components of anv development_ construction_ or use requiring a
critical area development authorization shall be classified as provided below, and shall conform to the development
standards applicable to the classification provided in subsections L through O of this section:
1. Water -oriented uses are one of the following three categories of uses, as defined in YMC 17.01.090: water -
dependent, water -related, or water -enjoyment, or a combination of such uses.
2. Nonwater-oriented uses include any use not qualifying as uses in subsection (K)(1) of this section.
L. Water -Dependent Uses. The following provisions shall aDDly to water -dependent uses
1. Structures shall be clustered at locations on the water's edge having the least impact to the surface water and
shore.
2. Use areas and structures which require direct shore locations shall be located and constructed to minimize
impacts to the shore area and the vegetative buffer specified in subsection P of this section.
3. Use areas and structures requiring direct shore locations shall minimize any obstruction or impairment of
normal public navigation of the surface water.
M. Water -Related Uses. The following provisions shall apply to water -related uses:
1. Structures and use areas shall be located as far landward from the ordinary high water mark or wetland edge as
is possible and still preserve the essential or necessary relationship with the surface water.
2. Structures and use areas shall not be located within the vegetative buffer specified in subsection P of this
section except where existingdevelopment or the requirements associated with the use make such a location
unavoidable.
N. Water -Enjoyment Uses. The following provisions shall apply to water -enjoyment uses:
1. Structures and use areas shall be located as far landward from the ordinary high water mark or wetland edge as
is possible and still preserve the essential or necessary relationship with the surface water.
2. Structures and use areas may be located within the vegetative buffer specified in subsection P of this section;
provided, that the location and construction shall be conducted to minimize impacts to the shore area and the
vegetative buffer.
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O. Nonwater-Oriented Uses. The following provisions shall apply to nonwater-oriented uses
1. Structures and use areas shall be set back so as not to be located within the vegetative buffer specified in
subsection P of this section.
2. Construction abuttingthe he vegetative buffer specified in subsection P of this section shall be designed and
scheduled to ensure there will not be permanent damage or loss of the vegetative buffer.
P. Vegetative Buffers. The establishment of a vegetative buffer system is necessary to protect the functions and values of
SeFt,,4 i . a i n. related ;.; i o c.,, -a , -a �a i ,,ff f streams, lakes, and ponds ( e st@ ;
Table 09.030-1)- See YMC 17.09.040 for wetland buffer regulations.
1. Vegetative buffers shall be measured from the ordinary high water mark for streams, lakes, and ponds. The
width of the buffer shall be determined according to the stfeairrwater type.
2. The adequacy of these standard buffer widths presumes the existence of a relatively intact native vegetative
community within the buffer zone that is deemed adequate to protect the identified critical area.
a. If the vegetation is degraded, then revegetation may be considered with any adjustment to the buffer
width.
b. Where the use is being intensified, a degraded buffer may be revegetated to maintain the standard width.
Table 09.030-1. Standard Stream Buffers
Stream Type
Buffer Width
Type 1 shoreline streams
High Intensity_
mtd lakes, and ponds
Streams: 75'
Lakes: 50'
Essential Public Facilities: 100'
Floodway/CMZ: 100'
Shoreline Residential:
Streams: 80'
Lakes: 20'
Urban Conservancy,
Type 2 streams, lakes, and
75'
ponds
Type 3 streams (perennial),
50'
lakes, and ponds
Type 4 streams
25'
(intermittent), lakes, and
ponds
17.09.040 Wetlands.
A. Purpose and Intent. The purpose and intent of the provisions protecting wetland critical areas is equivalent to
the purpose and intent for YMC 17.09.030.
B. Desienatine and Mallin
1. GoflsistepA with WAG 73-22-9�-��Wetlands 44 shoo-ehw � sdietioi4 shall be delineated using the
procedure outlined in the approved federal wetland delineation manual and applicable regional supplements.
2. Wetlands are all areas meeting the definition for wetlands as defined in YMC 17.01.090 and are hereby
designated critical areas which are subject to this chapter, except the following:
a. Irrigation systems that create an artificial wetlands, and
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b. Areas where changes in irrigation practices have caused wetland areas to dry up_
3. The approximate location and extent of wetlands are shown on maps maintained by the city of Yakima.
These maps may include information from the National Wetlands Inventory produced by the U. S. Fish and
Wildlife Service and are to be used as a guide for the city of Yakima.
C. Protection Approach Wetlands will be protected using the protection approach for hydrologically related
critical areas found in YMC 17.09.030(B). Wetlands and their functions will be protected using the standards found
in this section and in YMC 17.09.030.
D. Wetland Functions and Rating.
1. Wetlands are uniaue landscape features that are the interface between the aauatic and terrestrial
environments. Wetlands provide the following functions:
a. Biogeochemical functions, which improve water quality in the watershed (such as nutrient retention
and transformation, sediment retention, metals, and toxics retention and transformation).
b. Hydrologic functions, which maintain the water regime in a watershed, such as: flood flow
attenuation, decreasing erosion, and groundwater recharge.
c. Food and habitat functions, which include habitat for invertebrates, amphibians, anadromous fish.
resident fish, birds, and mammals.
2. Wetlands shall be rated based on categories that reflect the functions and values of each wetland and shall
be based on the criteria provided in the Washington State Wetland Rating System for Eastern Washington,
revised 44^rGctober 2014 (Ecology Publication Number 44-46-4414-06-030, or as revised) which are
summarized below.
a. Category I wetlands are those that 1) represent a unique or rare wetland type: or 2) are more sensitive
to disturbance than most wetlands: or 3) are relatively undisturbed and contain ecological attributes that
are impossible to replace in a human lifetime: or 4) provide a high level of functions. Risk of any
degradation to these wetlands must be avoided because their functions and values are too difficult to
replace. Generally, these wetlands are not common and make up a small percentage of the wetlands in
the region.
1 .,tt,-ibtAes that d ff et It to lage !-`_eHeE.,11� these tl. pds
^ c�oivrarcrrvnccr�rair-acro-cirrrrcmrcv-i�naw�cnvnm�-mcoo��orrariccsai=rciivrcvi-raavn
.,.i maw „ a N,en, small o.. aee of the . etl.,p& w thi1 040 64A, of yal4 .,., The, f 11....,;....
'_xx7 tl. pills t� e (o t f oRe T,,,...1, -ed) the �x 7.,ship -4 Ct.,to
i. TGIIL[I1C[S:TGVIIZS�JG�eTLL�G'IpSLIL�1r—mIi1C^TSG-�VLCC'pSVi1CT1T[IICCLCT["/'1ZT"['11�/TiTJI1IIi�,C01^TpT[CLC
WetlapA R tii4e caste,,, for- gaste W.,shii ,.too ixxro e>~W�•
ii.
Alkali wet lam•
T�T.,t„ 1 1, 't., tl .,...1� /..,otl.,...1� •.l o..t; f;o.l 1,� xx7., 1,' rx .•t..,o..t ..f TAT t,,,-.,1
iii. rrarcrrcrrncizrcr�o�Poumiao-c-vPccmaao-i�ic�nrrlcav�-arasnia�tvirncl3i-rnn:crnvr�aicrsirr
Resour-ees N.,t.,fa i7o,-4a. xe D,-.......,.., epAists\. .,...1
b. Category II wetlands are difficult but not impossible to replace and provide high levels of some
functions. These wetlands occur more commonly than Category 1 wetlands, but still need a relatively
high level of protection. Ggegon, 11 d eglapas44o
W tl.,p T. t..,eei f to ' (o t f o ffe T,,,,A -ed) the W SE)-,
i. arorraaccs:rrovirii�oocwwazrr�'�iio--crr��'zaiic�rvrvaciim-�rvu7�o—arrcrrrTar,
ii.
iii. Forested we4and-s,
c. Category III wetlands are wetlands with a moderate level of functions and can often be adequately
replaced with a well-planned mitigation project. These wetlands generally have been disturbed in some
ways and are often less diverse or more isolated from other natural resources in the landscape than
Category II wetlands.
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d. Catee-ory IV wetlands have the lowest levels of functions
NVRSEW. Ggegone0apAs and are often heavily disturbed qPA are etlap s that shotAd be able to
. These are wetlands that should be able to be replaced and, in some cases, improved.
However, experience has shown that replacement cannot be guaranteed in any specific case. These
wetlands may provide some important functions and also need to be protected.
3. Wetlands shall berated as they exist on the day of project application submission. Information regarding
the original condition of illegally modified wetlands that cannot be discerned from aerial photoaphs or other
reliable information sources shall use the highest appropriate points value within each missing data field of
the WRSEW rating sheet to complete the rating.
E. Wetland Buffers.
8. Buffer Requirements. The following buffer widths have been established in accordance with the best
available science. They are based on the category of wetland and the habitat score as determined by a
qualified professional using the Washington State Wetland Rating System for Eastern Washington: 2014
Update (Ecology Publication #14-06-030, or as revised). The adjacent land use intensity is assumed to be
high.
a. For wetlands that score 5 points or more for habitat function, the buffers in Table 27.6-1 can be used if
both of the following criteria are met:
1. A relatively undisturbed, vegetated corridor at least 100 feet wide is protected between the wetland
and any other Priority Habitats as defined by the Washington State Department of Fish and Wildlife
(http://wdfw.wa.gov/hab/Thshabs.htm).
The corridor must be protected for the entire distance between the wetland and the Priority Habitat by
some type of legal protection such as a conservation easement.
Presence or absence of a nearby habitat must be confirmed by a qualified biologist. If no option for
providing a corridor is available, Table 27.6-1 may be used with the required measures in Table 27.6-
2 alone.
2 The measures in Table 27.6-2 are implemented, where applicable, to minimize the impacts of the
adjacent land uses.
b. For wetlands that score 3-4 habitat points, only the measures in Table 27.6-2 are required for the use of
Table 27.6-1.
c. If an applicant chooses not to apply the mitigation measures in Table 27.6-2, or is unable to provide a
protected corridor where available, then Table 27.6-3 shall be used.
d. The buffer widths in Table 27.6-1 and 27.6-3 assume that the buffer is vegetated with a native plant
community appropriate for the ecoregion. If the existing buffer is unvegetated, sparsely vegetated, or
vegetated with invasive species that do not perform needed functions, the buffer should either be
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planted to create the appropriate plant community or the buffer should be widened to ensure that
adequate functions of the buffer are provided.
Table 27.6-1: Wetland Buffer Requirements if Table 27.6-2 is implemented and corridor provided
Buffer Width (feet) based on habitat score
Wetland Category 3-4 5 6-7 8-9
Category 1: Based on total 75 90 120 150
score
Category 1: Forested 75 90 120 150
Category 1: Bogs and
Wetlands of High 190
Conservation Value
Category 1: Alkali 150
Category IL Based on total 75 90 120 150
score
Category IL Vernal Pool 150
Category IL Forested 75 90 120 150
Category III (all) 60 90 120 150
Category IV (all) 40
Table 27.6-2: Required measures to minimize impacts to wetlands
Disturbance
Required Measures to Minimize Impacts
Lights
.
Direct lights away from wetland
Noise
.
Locate activity that generates noise away from wetland
•
If warranted, enhance existing buffer with native vegetation for plantings adjacent
to noise source
•
For activities that generate relatively continuous, potentially disruptive noise, such
as certain heave industry or mining, establish an additional 10 -feet heavily
vegetated buffer strip immediately adjacent to the outer wetland buffer.
Toxic Runoff
.
Route all new, untreated runoff away from wetland while ensuring wetland is not
dewatered
•
Establish covenants limiting use of pesticides within 150 -feet of wetland
•
Apply integrated pest management
Stormwater
.
Retrofit stormwater detention and treatment for roads and existing adjacent
Runoff
development
•
Prevent channelized flow from lawns that directly enters the buffer
•
Use Low Intensity Development techniques
Changes in water
e
Infiltrate or treat, detain, an disperse into buffer new runoff from impervious
regime
surfaces and new lawns.
Pets and human
e
Use privacy fencing OR plan dense vegetation to delineate buffer edge and to
disturbance
discourage disturbance using vegetation appropriate for the ecoregion
•
Place wetland and its buffer in a separate tract or protect with a conservation
easement
Dust
•
Use best management practices to control dust
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Table 27.6-3: Wetland Buffer Requirements if Table 27.6-2 is NOT imulemented and corridor NOT urovided
Buffer Width (feet) based on habitat score
Wetland Category 3-4 5 6-7 8-9
Category 1: Based on total 100 130 180 200
score
Category 1: Forested 100 130 180 200
Category 1: Bogs and
Wetlands of High
Conservation Value
Category 1: Alkali
Category IL Based on total
score
Category IL Vernal Pool
Category IL Forested
Category III (all)
Category IV (all)
250
200
100 130 180 200
200
100 130 180 200
80 130 180 200
50
e. Increased Wetland Buffer Area Width. Buffer widths shall be increased on a case-by-case basis as
determined by the administrative official when a larger buffer is necessary to protect wetland functions
and values. This determination shall be supported by appropriate documentation showing that it is
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reasonably related to protection of the functions and values of the wetland. This documentation shall
include, but not be limited to, the following criteria:
i. The wetland is used by a state or federally listed plant or animal species, or has unusual nesting
or resting sites such as heron rookeries or raptor nesting trees: or
I The adjacent land is susceptible to severe erosion, and erosion -control measures will not
effectively prevent adverse wetland impacts: or
iii. The adjacent land has minimal vegetative cover or slopes greater than 30 percent.
f. Buffer averaging to improve wetland protection may be permitted when all of the following conditions
are met:
i. The wetland has significant differences in characteristics that affect its habitat functions, such as
a wetland with a forested component adjacent to a degraded emergent component or a "dual -
rated" wetland with a Category 1 area adjacent to a lower -rated area.
ii. The buffer is increased adjacent to the higher -functioning area of habitat or more -sensitive
portion of the wetland and decreased adjacent to the lower -functioning or less -sensitive portion
as demonstrated by a critical areas report from a qualified wetland professional.
iii. The total area of the buffer after averaging is equal to the area required without averaging.
iv. The buffer at its narrowest point is never less than either 3/4 of the required width or 75 -feet for
Category I and II, 50 -feet for Category III, and 25 -feet for Category IV, whichever is greater.
g. Averaging to allow reasonable use of a parcel may be permitted when all of the following are met:
i. There are no feasible alternatives to the site design that could be accomplished without buffer
averaging.
ii. The averaged buffer will not result in degradation of the wetland's functions and values as
demonstrated by a critical areas report from a qualified wetland professional.
iii. The total buffer area of the buffer after averaging is equal to the area without averaging.
iv. The buffer at its narrowest point is never less than either 3/4 of the required width or 75 -feet for
Category I and II, 50 -feet for Category III, and 25 -feet for Category IV, whichever is greater.
2. To facilitate long-range planning using a landscape approach, the Administrative Official may identify and
pre-assess wetlands using the rating system and establish appropriate wetland buffer widths for such
wetlands. The Administrative Official will prepare maps of wetlands that have been pre -assessed in this
manner.
3. Measurement of Wetland Buffers. All buffers shall be measured perpendicular from the wetland boundary
as surveyed in the field. The buffer for a wetland created, restored, or enhanced as compensation for
approved wetland alterations shall be the same as the buffer required for the category of the created,
restored, or enhanced wetland. Buffers must be fully vegetated in order to be included in buffer area
calculations. Lawns, walkways, driveways, and other mowed or paved areas will not be considered buffers
or included in buffer area calculations.
4. Buffers on Mitigation Sites. All wetland mitigation sites shall have buffers consistent with the buffer
requirements of this Chapter. Buffers shall be based on the expected or target category of the proposed
wetland mitigation site.
5. Buffer Maintenance. Except as otherwise specified or allowed in accordance with this chapter, wetland
buffers shall be retained in an undisturbed or enhanced condition. In the case of compensatory mitigation
sites, removal of invasive non-native weeds is required for the duration of the mitigation bond, YMC §
15.27.605(10)(b)(i)(10).
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6. Impacts to Buffers. Requirements for the compensation for impacts to buffers are outlined in YMC §
15.27.605.
7. Overlapping Critical Area Buffers. If buffers for two contiguous critical areas overlap (such as buffers for
a stream and a wetland), the wider buffer applies.
8. Allowed Buffer Uses. The following uses may be allowed within a wetland buffer in accordance with the
review procedures of this Chapter, provided they are not prohibited by any other applicable law and they
are conducted in a manner so as to minimize impacts to the buffer and adjacent wetland:
a. Conservation and Restoration Activities. Conservation or restoration activities aimed at protecting the
soil, water, vegetation, or wildlife.
b. Passive recreation. Passive recreation facilities designed and in accordance with an approved critical
area report, including:
1. Walkways and trails, provided that those pathways are limited to minor crossings having no
adverse impact on water quality. They should be generally parallel to the perimeter of the wetland,
located only in the outer twenty-five percent (251/o) of the wetland buffer area, and located to
avoid removal of significant trees. They should be limited to pervious surfaces no more than five
(5) feet in width for pedestrian use only. Raised boardwalks utilizing non -treated pilings may be
acceptable.
2. Wildlife -viewing structures.
c. Educational and scientific research activities.
d. Normal and routine maintenance and repair of any existing public or private facilities within an
existing right-of-way, provided that the maintenance or repair does not increase the footprint or use of
the facility or right-of-wa.
e. The harvesting of wild crops in a manner that is not injurious to natural reproduction of such crops,
chemical applications, or alteration of the wetland by changing existing topography, water conditions,
or water sources.
f. Drilling for utilities/utility corridors under a buffer, with entrance/exit portals located completely
outside of the wetland buffer boundary, provided that the drilling does not interrupt the ground water
connection to the wetland or percolation of surface water down through the soil column. Specific
studies by a hydrologist are necessary to determine whether the ground water connection to the
wetland or percolation of surface water down through the soil column is disturbed.
g. Enhancement of a wetland buffer through the removal of non-native invasive plant species. Removal
of invasive plant species shall be restricted to hand removal. All removed plant material shall be taken
away from the site and appropriately disposed of. Plants that appear on the Washington State Noxious
Weed Control Board list of noxious weeds must be handled and disposed of according to a noxious
weed control plan appropriate for that species. Revegetation with appropriate native species at natural
densities is allowed in conjunction with removal of invasive plant species.
h. Repair and maintenance of non -conforming uses or structures, where legally established within the
buffer, provided they do not increase their degree of nonconformity.
9. Signs and Fencing of Wetlands and Buffers.
a. Tenmorary markers. The outer berimeter of the wetland buffer and the clearing limits identified by an
approved permit or authorization shall be marked in the field with temporary "clearing limits" fencing
in such a way as to ensure that no unauthorized intrusion will occur. The marking is subject to
inspection by the Administrative Official prior to the commencement of permitted activities. This
temporary marking shall be maintained throughout construction and shall not be removed until
permanent signs, if required, are in place.
b. Permanent signs. As a condition of anypermit or authorization issued pursuant to this chapter, the
Administrative Official may require the applicant to install permanent signs along the boundary of a
wetland or buffer.
1. Permanent signs shall be made of an enamel -coated metal face and attached to a metal post or
other non -treated material of equal durability. Signs must be posted at an interval of one (1) every
50 -feet, or one (1) per lot if the lot is less than 50 -feet wide, and must be maintained by the
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property owner in perpetuity. The signs shall be worded as follows or with alternative language
approved by the Administrative Official:
Protected Wetland Area
Do Not Disturb
Contact the Citv of Yakima
Regarding Uses, Restrictions, and Opportunities for Stewardship
2. The provisions of Subsection (a) may be modified as necessary to assure protection of sensitive
features or wildlife.
c. Fencing.
1. The abblicant shall be reauired to install a bermanent fence around the wetland or buffer when
domestic grazing animals are present or may be introduced on site.
2. Fencing installed as part of a proposed activity, or as required in this Subsection, shall be designed
so as not to interfere with species mitigation, including fish runs, and shall be constructed in a
manner that minimizes impacts to the wetland and associated habitat.
1. Veeetali ,e bttffer-s shall he meas -ed fr,..., the edge f the . ,e#ap l The ..,;.144 of the h„ff 4�
�.1 .o,:,,,;.. .1 .1• ... the tl .,...1 t, Th ..,...1.,,-.11. ff ;.l.l,� •.lo.l ; T 1.1
c�cccrinrricaiiccvicr'Iii�cv-cxxc=v`�camicrc�i�rn�am.cr�mr�r-Cric �iv�iacazirzimxc
no nen 1 bel....,
nton-z,vncie—appncable t, dic-tneii)actsvf-the -aca�jaeemt1. "
6cr.
3. if .,., „ 1;...,.,t ..hooses Hot to appiv the W 4; .,401 ..astir -es „ Table 09.0 4 0 2 the., „ th;,-i-,
three e„t 4 „ the .. i 4h of .,11 h„ff ,-e.l F..,- oma,.,,,, le e„t, f;A,ec f ..vt WIFcE
Ivrvcrsrr
with the rr„ iea4ioi rr,eastifes „1.1 he ., e h,,...1,-0.1 f ..t l.,,ff
4. The .,.le -,taev of these st.,.,.1.,f h„Ff .. i the s the e ;steme of ., el.,tA el ., aet .,.,t;v e
., the b4fe -moo e that is .lee..,e.l ade uge to ,-..teet the identg4e
GF4ieal area. -
if the eeeta4ioi is .le.,, -a e.l the.4 rxeta4ioi w v he .l si efew4h am,adjt..,
ste.,t t
the bu ..,i.lth _ _
b. xx7hm the use s he;.,e ipAemsi e.l .le..,-.,.le.l h„ffe mo he , et.,te.l to .,tai the
Table 09.040
4. Standard Wetland Buffer -
width ;F..,etin,..1
sear -es 24 25 1...1.:4..4
width if wetland
s 26 10 l...h;4..4
width ;F..,.,41.,,..1
sear -es 2!1 26 habit -at
f'.,4.,...,,.., T. Based an 4.,4.,1 s...,,..,
A.1
A .1�.1 45-A
A .1
f'.,4.,..arw T. Far-ested
tp
Add 15 A
A .14-4
A .1d-7
n4egar., T. Rnrsc.
�
44044
7�Y04p4
1
-W�T
-W�T
G ategar., T. A11..,1;
4-54-A
��iTYA
1 HA
A�Y
-WA
A�Y
-WA
Gateg
t1I7�,41. a rw 1! Natural HeAt
Y- 044
1Yf A
-WA
-WA
f'.,4.,..arw TT. Based an 4.,4.,1 s...,,..,
A.lr�cm'1--1-5-A
A. 4-45-A
d-7
n4egar.
4-59
-WA
-WA
-WA
f'.,4.,..arw TT. Far-ested-
Add 15 A
A.1
A.1
.,4.,...,,.., TTT /.illA
6044
A .1
A44-6"
-A
.4,.rsarw W/+A4
48€4
-WA
-WA
-WA
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F. Compensatory MitigationReguir-emefqs.
6. Mitigation Sequencing. Before impacting any wetland or its buffer, an applicant shall demonstrate that the
following actions have been taken. Actions are listed in the order of preference:
a. Avoid the impact altogether by not taking a certain action or parts of an action.
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b. Minimize impacts by limiting the degree or magnitude of the action and its implementation, b., ung
appropriate technology, or by taking affirmative steps to avoid or reduce impacts.
c. Rectify the impact by repairing, rehabilitating, or restoring the affected environment.
d. Reduce or eliminate the impact over time by preservation and maintenance operations.
e. Compensate for the impact by replacing, enhancing, or providing substitute resources or environments.
f Monitor the required compensation and take remedial or corrective measures when necessary
7. Requirements for Compensatory Mitigation:
a. Combensatory mitigation for alterations to wetlands shall be used onlv for impacts that cannot be
avoided or minimized and shall achieve equivalent or greater biologic functions. Compensatory
mitigation plans shall be consistent with Wetland Mitigation in Washington State Part 2: Develop
Mitigation Plans Version 1, (Ecology Publication #06-06-01 lb, Olympia, WA, March 2006 or as
revised), and Selecting Wetland Mitigation Sites Using a Watershed Approach (Eastern Washington)
(Publication #10-06-07, November 2010).
b. Mitigation ratios may also be determined using the credit/debit tool describe in "Calculating Credits
and Debits for Compensatory Mitigation in Wetlands ofEastern Washington: Final Report (Ecology
Publication #11-06-045, August 2012), consistent with subsection 8 of this Chapter.
8. Compensating for Lost or Affected Functions. Combensatory mitigation shall address the functions
affected by the proposed project, with an intention to achieve functional equivalency or improvement of
functions. The goal shall be for the compensatory mitigation to provide similar wetland functions as those
lost, except when either:
a. The lost wetland provides minimal functions, and the proposed compensatory mitigation actions)
will provide equal or greater functions or will provide functions shown to be limiting within a
watershed through a formal Washington state watershed assessment plan or protocol, or
b. Out -of -kind replacement of wetland type or functions will best meet watershed goals formally
identified by the City, such as replacement of historically diminished wetland types.
9. ADDroaches to Combensatory Mitigation. Mitigation for lost or diminished wetland and buffer functions
shall rely on the approaches listed below.
a. Wetland mitigation banks. Credits from a certified wetland mitigation bank may be used to
compensate for impacts located within the service area specified in the mitigation bank instrument.
Use of credits from a wetland mitigation bank certified under Chapter 173-700 WAC is allowed if:
i. The approval authority determines that it would provide appropriate compensation for the
proposed impacts: and
ii. The impact site is located in the service area of the bank.
iii. The proposed use of credits is consistent with the terms and conditions of the certified
mitigation bank instrument.
iv. Replacement ratios for projects using bank credits is consistent with replacement ratios
specified in the certified mitigation bank instrument.
b. In -Lieu Fee Mitigation: Credits from an approved in -lieu -fee program may be used when all of
the following apply:
i. The approval authority determines that it would provide environmentally appropriate
compensation for the proposed impacts.
ii. The proposed use of credits is consistent with the terms and conditions of the approved
in -lieu -fee program instrument.
iii. Projects using in -lieu -fee credits shall have debits associated with the proposed impacts
calculated by the applicant's qualified wetland professional using the credit assessment
method specified in the approved instrument for the in -lieu -fee program.
iv. The impacts are located within the service area specified in the approved in -lieu -fee
instrument.
c. Permittee -responsible mitigation. In this situation, the permittee performs the mitigation after the
permit is issued and is ultimately responsible for implementation and success of the mitigation.
Permittee -responsible mitigation may occur at the site of the permitted impacts or at an off-site
location within the same watershed. Permittee -responsible mitigation shall be used only if the
applicant's qualified wetland professional demonstrates to the approval authority's satisfaction
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that the proposed approach is ecologically preferable to use of a bank or IL,F program, consistent
with the criteria in this section.
10. Types of Compensatory Mitigation. Mitigation for lost or diminished wetland and buffer functions shall
rely on a type listed below in order of preference. A lower -preference form of mitigation shall be used only
if the applicant's qualified wetland professional demonstrates to the approval authority's satisfaction that
all higher -ranked types of mitigation are not viable, consistent with the criteria in this section.
a. Restoration: The manipulation of the physical, chemical, or biological characteristics of a site
with the goal of returning natural or historic functions to a former or degraded wetland. For the
purpose of tracking net gains in wetland acres, restoration is divided into:
i. Re-establishment: The manipulation of the physical, chemical, or biological
characteristics of a site with the goal of returning natural or historic functions to a former
wetland. Re-establishment results in a gain in wetland acres (and functions). Activities
could include removing fill material, plugging ditches, or breaking drain tiles.
ii. Rehabilitation: The manipulation of the physical, chemical, or biological characteristics
of a site with the goal of repairing natural or historic functions of a degraded wetland.
Rehabilitation results in a gain in wetland function but does not result in a gain in wetland
acres. Activities could involve breaching a dike to reconnect wetlands to a floodplain or
return tidal influence to a wetland.
b. Establishment (Creation): The manipulation of the physical, chemical, or biological
characteristics of a site to develop a wetland on an upland or deepwater site where a wetland did
not previously exist. Establishment results in a gain in wetland acres. Activities typically involve
excavation of upland soils to elevations that will produce a wetland hydroperiod, create hydric
soils, and support the growth of hydrophytic plant species.
i. If a site is not available for wetland restoration to compensate for expected wetland
and/or buffer impacts, the approval authority may authorize creation of a wetland and
buffer upon demonstration by the applicant's qualified wetland professional that:
1. The hydrology and soil conditions at the proposed mitigation site are conducive
for sustaining the proposed wetland and that creation of a wetland at the site will
not likely cause hydrologic problems elsewhere,
2. Adjacent land uses and site conditions do not jeopardize the viability of the
proposed wetland and buffer (e.g., due to the presence of invasive plants or
noxious weeds, stormwater runoff, noise, light, or other impacts): and
3. The proposed wetland and buffer will eventually be self-sustaining with little or
no long-term maintenance.
c. Enhancement. The manipulation of the physical, chemical, or biological characteristics of a
wetland site to heighten, intensify, or improve specific function(s) or to change the growth stage or
composition of the vegetation present. Enhancement is undertaken for specified purposes such as
water quality improvement, flood water retention, or wildlife habitat. Enhancement results in a
change in some wetland functions and can lead to a decline in other wetland functions, but does
not result in a gain in wetland acres. Activities typically consist of planting vegetation, controlling
non-native or invasive species, modifying site elevations or the proportion of open water to
influence hydroperiods, or some combination of these activities. Applicants proposing to enhance
wetlands or associated buffers shall demonstrate how the proposed enhancement will increase the
wetland's/buffer's functions, how this increase in function will adequately compensate for the
impacts, and how existing wetland functions at the mitigation site will be protected.
d. Protection/Maintenance (Preservation). Removing a threat to, or preventing the decline of,
wetland conditions by an action in or near a wetland. This includes the purchase of land or
easements, or repairing water control structures or fences. This term also includes activities
commonly associated with the term preservation. Preservation does not result in a gain of wetland
acres. Permanent protection of a Category I or II wetland and associated buffer at risk of
degradation can be used only if:
i. The approval authority determines that the proposed preservation is the best mitigation
option,
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ii. The proposed preservation site is under threat of undesirable ecological change due to
permitted, planned, or likely actions that will not be adequately mitigated under existing
regulations:
iii. The area proposed for preservation is of high quality or critical for the health of the
watershed or basin due to its location. Some of the following features may be indicative
of high-quality sites:
1. Category I or II wetland rating (using the wetland rating system for western
Washington)
2. Rare or irreplaceable wetland type (for example, bogs, mature forested wetlands,
estuarine wetlands) or aquatic habitat that is rare or a limited resource in the
area,
3. The presence of habitat for priority or locally important wildlife species: or also
list has provides biological and/or hydrological connectivity;
4. Provides biological and/or hydrological connectivity,
5. Priority sites in an adopted watershed plan.
iv. Permanent preservation of the wetland and buffer will be provided through a
conservation easement or tract held by an appropriate natural land resource manager,
such as a land trust.
v. The approval authority may approve other legal and administrative mechanisms in lieu of
a conservation easement if it determines they are adequate to protect the site.
vi. Ratios for preservation in combination with other forms of mitigation generally range
from 10:1 to 20:1, as determined on a case-by-case basis, depending on the quality of the
wetlands being impacted and the quality of the wetlands being preserved. Ratios for
preservation as the sole means of mitigation generally start at 20:1.
11. Location of Combensatory Mitigation. Combensatory mitigation actions shall generally be conducted
within the same sub -drainage basin and on the site of the alteration except when the applicant can
demonstrate that off-site mitigation is ecologically_ preferable. The following criteria will be evaluated
when determining whether the proposal is ecologically preferable. When considering off-site mitigation,
preference should be given to using alternative mitigation, such as a mitigation bank, an in -lieu -fee
program, or advance mitigation.
a. There are no reasonable opportunities on site or within the sub -drainage basin (e.g., on-site options
would require elimination of high -functioning upland habitat), or opportunities on site or within
the sub -drainage basin do not have a high likelihood of success based on a determination of the
capacity of the site to compensate for the impacts. Considerations should include: anticipated
replacement ratios for wetland mitigation, buffer conditions and proposed widths, available water
to maintain anticipated hydrogeomorphic classes of wetlands when restored, proposed flood
storage capacity, and potential to mitigate riparian fish and wildlife impacts (such as connectivity):
b. On-site mitigation would require elimination of high-quality upland habitat.
c. Off-site mitigation has a greater likelihood of providing equal or improved wetland functions than
the altered wetland.
d. Off-site locations shall be in the same sub -drainage basin unless:
i. Established watershed goals for water quality, flood storage or conveyance, habitat, or
other wetland functions have been established by the City and strong) iffy location of
mitigation at another site: or
ii. Credits from a state -certified wetland mitigation bank are used as compensation, and the
use of credits is consistent with the terms of the certified bank instrument,
iii. Fees are paid to an approved in -lieu fee program to compensate for the impacts.
e. The design for the compensatory mitigation project needs to be appropriate for its location (i.e.,
position in the landscape). Therefore, compensatory mitigation should not result in the creation,
restoration, or enhancement of an atypical wetland.
12. Timing of Compensatory Mitigation. It is preferred that compensatory mitigation projects be completed
prior to activities that will disturb wetlands. At the least, compensatory mitigation shall be completed
immediately following disturbance and prior to use or occupancy of the action or development.
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Construction of mitigation broiects shall be timed to reduce inmacts to existing fisheries. wildlife. and
flora.
a. The Administrator may authorize a one-time temporary delay in completing construction or
installation of the compensatory mitigation when the applicant provides a written explanation
from a qualified wetland professional as to the rationale for the delay. An appropriate rationale
would include identification of the environmental conditions that could produce a high probability
of failure or significant construction difficulties (e.g., project delay lapses past a fisheries window,
or installing plants should be delayed until the dormant season to ensure greater survival of
installed materials). The delay shall not create or perpetuate hazardous conditions or
environmental damage or degradation, and the delay shall not be injurious to the health, safety, or
general welfare of the public. The request for the temporary delay must include a written
justification that documents the environmental constraints that preclude implementation of the
compensatory mitigation plan. The justification must be verified and approved by the City.
13. Wetland Mitigation Ratios:
Category and Tvue of
Creation or
Rehabilitation
Enhancement
Wetland
Re-establishment
Category L Bog, Natural
Not considered possible
Case by Case
Case by Case
Heritage Site
Category L Mature
Forested
6_1
12:1
24:1
Category L Based on
functions
4_1
8_1
16:1
Category
3:1
6:1
12:1
Category III
2:1
4:1
8:1
Category IV
1.5:1
3:1
6:1
Ratios for rehabilitation and enhancement may be reduced when combined with 1:1 replacement through creation or
re-establishment See Table lb, Wetland Mitigation in Washington State Part 1: Agencv Policies and Guidance --
Version 1, (Ecology Publication #06-06-01 la, Olympia, WA, March 2006 or as revised). See also Paragraph D.4
for more information on using preservation as compensation.
14. Credit/Debit Method. To more fully brotect functions and values. and as an alternative to the mitigation
ratios found in the joint guidance "Wetland Mitigation in Washington State Parts I and II" (Ecology
Publication #06-06-01 la -b, Olympia, WA, March, 2006), the administrator may allow mitigation based on
the "credit/debit" method developed by the Department of Ecology in "Calculating Credits and Debits for
Conmensatory Mitigation in Wetlands of Eastern Washineton: Final Rellorf' (Ecoloev Publication #11-06-
015, August 2012, or as revised
15. Combensatory Mitigation Plan. When a broiect involves wetland and/or buffer imbacts. a conmensato
mitigation plan prepared by a qualified professional shall be required, meeting the following minimum
standards:
a. Wetland Critical Area Report. A critical area report for wetlands must accompany or be included
in the compensatory mitigation plan and include the minimum parameters described in Minimum
Standards for Wetland Reports (Section XX.060.B) of this Chapter.
b. Compensatory Mitigation Report. The report must include a written report and plan sheets that
must contain, at a minimum, the following elements. Full guidance can be found in Wetland
Mitigation in Washington State—Part 2: Developing Mitigation Plans (Version 1) (Ecology
Publication #06-06-01 lb, Olympia, WA, March 2006 or as revised).
i. The written report must contain, at a minimum:
1. The name and contact information of the applicant: the name, qualifications, and
contact information for the primary author(s) of the compensatory mitigation
report: a description of the proposal, a summary of the impacts and proposed
compensation concept: identification of all the local, state, and/or federal
wetland -related bermit(s) reauired for the broiect and a vicinitv man for the
protect.
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2. Description of how the project design has been modified to avoid, minimize, or
reduce adverse impacts to wetlands.
3. Description of the existing wetland and buffer areas proposed to be impacted.
Include acreage (or square footage), water regime, vegetation, soils, landscape
position, surrounding lands uses, and functions. Also describe impacts in terms
of acreage by Cowardin classification hydrogeomorphic classification, and
wetland rating, based on Wetland Ratings, YMC 15.27.603.
4. Description of the compensatory mitigation site, including location and rationale
for selection. Include an assessment of existing conditions: acreage (or square
footage) of wetlands and uplands, water regime, sources of water, vegetation,
soils, landscape position, surrounding land uses, and functions.. Estimate future
conditions in this location if the compensation actions are NOT undertaken (i.e.,
how would this site progress through natural succession?).
5. Surface and subsurface hydrologic conditions, including an analysis of existing
and proposed hydrologic regimes for enhanced, created, or restored
compensatory mitigation areas. Include illustrations of how data for existing
hydrologic conditions were used to determine the estimates of future hydrologic
conditions
6. A description of the proposed actions for compensation of wetland and upland
areas affected by the project. Include overall goals of the proposed mitigation,
including a description of the targeted functions, hydrogeomorphic
classification, and categories of wetlands.
7. A description of the proposed mitigation construction activities and timing of
activities.
8. Performance standards (measurable standards for years post -installation) for
upland and wetland communities, a monitoring schedule, and a maintenance
schedule and actions proposed by year.
9. A discussion of ongoing management practices that will protect wetlands after
the development project has been implemented, including= proposed monitoring
and maintenance programs (for remaining wetlands and compensatory
mitigation wetlands).
10. A bond estimate for the entire compensatory mitigation project, including the
following elements: site preparation, plant materials, construction materials,
installation oversight, maintenance twice per year for up to five (5) years, annual
monitoring field work and reporting, and contingency actions for a maximum of
the total required number of years for monitoring.
11. Proof of establishment of Notice on Title for the wetlands and buffers on the
project site, including the compensatory mitigation areas.
ii. The scaled plan sheets for the compensatory mitigation must contain, at a minimum:
1. Surveyed edges of the existing wetland and buffers, proposed areas of wetland
and/or buffer impacts, location of proposed wetland and/or buffer compensation
actions.
2. Existing topography, ground -proofed, at two -foot contour intervals in the zone
of the proposed compensation actions if anyrg ading activity is proposed to
create the compensation area(s). Also existing cross-sections of on-site wetland
areas that are proposed to be impacted, and cross-section(s) (estimated one -foot
intervals) for the proposed areas of wetland or buffer compensation.
3. Conditions expected from the proposed actions on site, including future
hydrogeomorphic types, vegetation community types by dominant species
(wetland and upland), and future water regimes.
4. Required wetland buffers for existing wetlands and proposed compensation
areas. Also, identify any zones where buffers are proposed to be reduced or
enlarged outside of the standards identified in this Chapter.
5. A planting plan for the compensation area, including all species by proposed
community type and water regime, size and type of plant material to be
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installed, spacing of plants, typical clustering patterns, total number of each
species by community_ type, and timing of installation.
16. Buffer Mitigation Ratios. Impacts to buffers shall be mitigated at a minimum 1:1 ratio. Compensatory
buffer mitigation shall replace those buffer functions lost from development.
17. Protection of the Mitigation Site. The area where the mitigation occurred and any associated buffer shall
be located in a critical area tract or a conservation easement consistent with YMC 15.27 Part six.
18. Monitoring. Mitigation monitoring shall be required for a period necessary to establish that performance
standards have been met, but not for a period less than five years. If a scrub -shrub or forested vegetation
community is proposed, monitoring may be required for ten years or more. The project mitigation plan
shall include monitoring elements that ensure certainty of success for the project's natural resource values
and functions. If the mitigation goals are not obtained within the initial five-year period, the applicant
remains responsible for restoration of the natural resource values and functions until the mitigation goals
agreed to in the mitigation plan are achieved.
19. Advance Mitigation. Mitigation for projects with pre -identified impacts to wetlands may be constructed in
advance of the impacts if the mitigation is implemented according to federal rules, state policy on advance
mitigation, and state water quality regulations consistent with -Interagency Regulatory Guide: Advance
Permittee -Responsible Mitigation (Ecology Publication #12-06-015, Olympia, WA, December 2012).
20. Alternative Mitigation Plans. The Administrator may approve alternative wetland mitigation plans that are
based on best available science, such as priority restoration plans that achieve restoration goals identified in
the SMP. Alternative mitigation proposals must provide an equivalent or better level of protection of
wetland functions and values than would be provided by the strict application of this chapter. The
Administrative Official shall consider the following for approval of an alternative mitigation proposal:
a. The proposal uses a watershed approach consistent with Selecting Wetland Mitigation Sites Using
a Watershed Approach (Eastern Washington)(Ecology Publication #10-06-07, November 2010).
b. Creation or enhancement of a larger system of natural areas and open space is preferable to the
preservation of many individual habitat areas.
c. Mitigation according to Section E is not feasible due to site constraints such as parcel size, stream
type, wetland category, or geologic hazards.
d. There is clear potential for success of the proposed mitigation at the proposed mitigation site.
e. The plan shall contain clear and measurable standards for achieving compliance with the specific
provisions of the plan. A monitoring plan shall, at a minimum, meet the provisions in Section I
f. The plan shall be reviewed and approved as part of overall approval of the proposed use.
g. A wetland of a different type may be justified based on regional needs or functions and values: the
replacement ratios may not be reduced or eliminated unless the reduction results in a preferred
environmental alternative.
h. Mitigation guarantees shall meet the minimum requirements as outlined in Section 10.B.i.8.
i. Qualified professionals in each of the critical areas addressed shall prepare the plan.
J. The City may consult with agencies with expertise and jurisdiction over the critical areas during
the review to assist with analysis and identification of appropriate performance measures that
adequately safeguard critical areas.
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The Yakima Municipal Code is current through Ordinance 2015-047, passed December 8, 2015.
Page 69/69