Title 15 ENVIRONMENT
Chapter 15.02 CRITICAL AREAS PROTECTION
15.02.010 Title.
15.02.020 Preamble.
15.02.030 Purpose and intent.
15.02.040 Authority.
15.02.050 Definitions.
15.02.060 Applicability/regulated activities.
15.02.070 Exemptions.
15.02.080 Optional incentives for nondevelopment of critical areas.
15.02.090 Critical areas determination.
15.02.100 Critical area permit.
15.02.105 Relationship to other regulations.
15.02.110 Critical area inventory maps.
15.02.120 Critical area wetlands.
15.02.130 Fish and wildlife habitat conservation areas.
15.02.140 Frequently flooded critical areas.
15.02.150 Geologic hazard areas.
15.02.160 Critical aquifer recharge areas.
15.02.170 Mitigation plan performance standards.
15.02.180 Reasonable use exception.
15.02.190 Appeals.
15.02.200 Enforcement.
15.02.210 Fees.
15.02.220 Liability for damages.
15.02.230 Review.
15.02.240 Adoption by reference.
align="center">APPENDIX A
align="center">APPENDIX B
align="center">APPENDIX C
align="center">APPENDIX D
align="center">APPENDIX E
15.02.010 Title.
The title of the ordinance codified in this chapter is the “City of
Kalama Critical Areas Protection Ordinance.” (Ord. 1137 § 2 (part),
2004).
15.02.020 Preamble.
A. The city is responding to state mandates contained in the Growth
Management Act, RCW 36.70A.060, by developing and adopting this chapter which
classifies, designates, regulates and protects the function and values of
critical areas. The city believes it important to strike a balance between
critical land protection, private property rights and economic development and
diversification. Consequently, this chapter has been designed to encourage
landowners to protect critical areas by offering a range of incentives intended
to provide equitably for such protection. In addition, it is the intent of the
city to actively and constructively assist the applicant in the preparation and
processing of permits/approvals/plans/requirements or procedures. The ultimate
responsibility for providing complete and accurate application material and/or
required information falls on the applicant.
B. A limited amount of
scientific data is available to address all critical areas within the city. As
more information becomes available, it will be incorporated. (Ord. 1137 § 2
(part), 2004).
15.02.030 Purpose and intent.
A. The state of Washington’s Growth Management Act requires the city
to adopt development regulations affecting certain types of land to assure the
conservation of such areas. This chapter is intended to comply with the state
mandate. “Critical areas” include: wetlands, aquifer recharge areas,
geologically hazardous areas, fish and wildlife habitat, and frequently flooded
areas. These areas contain valuable natural resources, provide natural scenic
qualities important to the character of the community, perform important
ecological functions and processes, or present a hazard to life and property.
Identification, management and regulation for the protection of these lands and
areas are, therefore, necessary to protect the public health, safety and general
welfare of Kalama’s citizens. This chapter also describes the process used
to determine if a critical area exists on or adjacent to a particular parcel of
land. The process includes the use of maps, physical inspections and other
methods of fact-finding. It is the intent of the city to use the best available
science and data in making a critical area determination.
B. With respect to
particular critical areas, the city finds as follows:
1. Wetlands provide
numerous valuable functions, including but not limited to providing wildlife and
fish habitat, water quality enhancement, flood and erosion control, aquifer
recharge and discharge, shoreline stabilization, research and education
opportunities, and recreation.
2. Geologic hazards pose a risk to public and
private property and to the natural systems that make up the city’s
environment. These lands are susceptible to slides, erosion, seismic effects,
and mining hazards. Building and development practices should consider
topographical and geological features. Future development shall be directed to
more geologically stable areas and restricted on unsuitable ground. Regulating
these lands, and avoiding or minimizing alteration of geologic hazards, is
necessary to protect the health, safety and general welfare; therefore, two
categories have been established for review which are as follows: potentially
geologically hazardous areas which require more extensive review because of
severity of conditions and areas of geological concern, which may only require a
minimal amount of geological information with recommendations for site
development.
3. Aquifer recharge areas perform many important biological and
physical functions that benefit the city and its residents, including but not
limited to storing and conveying groundwater. Protection of aquifer recharge
areas is, therefore, necessary to protect the public health, safety and general
welfare.
4. Fish and wildlife habitat conservation areas perform many
important physical and biological functions that benefit the city and its
residents. These functions include but are not limited to: food, cover, nesting,
breeding and movement for fish and wildlife; maintaining and promoting diversity
of species and habitat; maintaining air and water quality; controlling erosion;
recreation, education and scientific study and aesthetic appreciation; and
providing neighborhood separation and visual diversity within urban
areas.
5. Frequently flooded areas pose a risk to public and private
property and public health. Regulation of these lands will promote efficient use
of the land and water resources by allocating frequently flooded areas to the
uses for which they are best suited and to discourage obstructions to
flood-flows or uses which pollute or deteriorate natural waters and water
courses.
C. It is the intent of this chapter to:
1. Implement the goals,
objectives and policies of the environmental and land use elements of the city
of Kalama’s comprehensive plan;
2. Comply with the requirements of the
Growth Management Act (RCW 36.70A) and mandate such rules and
guidelines;
3. Coordinate Kalama’s critical area protection activities
and programs with those of other jurisdictions;
4. Assist land owners by
providing incentives for critical area protection. (Ord. 1137 § 2 (part),
2004).
15.02.040 Authority.
This chapter is adopted under the authority of Chapter 36.70A RCW. (Ord.
1137 § 2 (part), 2004).
15.02.050 Definitions.
For the purposes of this chapter, the following definitions shall apply
unless the context clearly requires otherwise.
“Adjacent to”
means immediately adjoining (in contact with the boundary of the subject area)
or within a distance that is less than that needed to separate activities from
critical areas to ensure protection of the function and values of the critical
areas. Adjacent to shall mean any activity or development located:
1. On a
site immediately adjoining a critical area;
2. A distance equal to or less
than the required critical area buffer or setback width and building
setbacks;
3. A distance equal to or less than one-half mile (two thousand
six hundred forty feet) from a bald eagle’s nest;
4. A distance equal
to or less than three hundred feet upland from a stream, wetland or water
body;
5. Bordering or within the floodway, floodplain, or channel migration
zone; or
6. A distance equal to or less than two hundred feet from a
critical aquifer recharge area.
“Agricultural activities (existing and
ongoing)” means those activities involved in the production of crops and
livestock, including but not limited to operation and maintenance of existing
farm and stock ponds or drainage systems, irrigation systems, changes between
agricultural activities, and maintenance or repair of existing serviceable
structures and facilities, as allowed under Kalama Municipal Code Chapter 17.21,
Large-Lot Estates. Activities which bring an area into agricultural use are not
part of an ongoing activity. An activity ceases to be ongoing when the area on
which it was conducted has been converted to a nonagricultural use, or has been
unattended for five years. Forest practices are not included in this
definition.
“Alluvial fan” means a low, outspread, relatively
flat to gently sloping mass of loose alluvium, shaped like an open fan,
deposited by a stream where it issues from a narrow valley, or where a tributary
stream issues into the main stream, or wherever a constriction in a valley
abruptly ceases or the gradient of the stream suddenly decreases; it is steepest
near the mouth of the valley where its apex points upstream, and it slopes
gently and convexly outward with gradually decreasing
gradient.
“Alteration” means a human-induced action which
materially affects a regulated critical area or associated buffer, such as a
physical change to the existing condition of land or improvements, including but
not limited to: construction, clearing, filling and
grading.
“Applicant” means the person, party, firm, corporation,
Indian tribe, or federal, state or local government, or any other entity that
proposes any activity that could affect a critical area.
“Aquifer
recharge area” means areas where water infiltrates the soil and percolates
through it and surface rocks, to the groundwater.
“Best available
science” means current scientific information used in the process to
designate, protect, or restore critical areas, that is derived from a valid
scientific process as defined by WAC 365-195-900 through 925.
“Best
management practices” means systems of practices and management measures
that: (1) control soil loss and reduce water quality degradation caused by
nutrients, animal waste and toxins; (2) control the movement of sediment and
erosion caused by land alteration activities; (3) avoid adverse impacts to
surface and ground water quality, flow and circulation patterns; and (4) avoid
adverse impacts to the chemical, physical and biological characteristics of a
critical area.
“Buffer” or “buffer area” means an
area established to protect the integrity or functions and values of a critical
area from potential adverse impacts.
“Chemical applications”
means the application of herbicides, pesticides, organic or mineral-derived
fertilizers, or other hazardous substances.
“Clearing” means the
removal of trees, brush, grass, ground cover, or other vegetative matter from a
site.
“Conservation easement” means an interest or right of use
over a property, less than fee simple, to protect, preserve, maintain, improve,
restore, limit the future use of, or conserve for open space purposes, any land
or improvement on the land.
“Council” means the Kalama city
council.
“Critical area” means and includes the following areas
and ecosystems: (1) wetlands; (2) areas with a critical recharging effect on
aquifers used for potable water; (3) fish and wildlife habitat conservation
areas as defined in; (4) frequently flooded areas; and (5) geologically
hazardous areas.
“Development” means a construction project
involving property improvement or a change of physical character within the
site; the act of using land for building or extractive purposes.
“Development” shall include, but shall not be limited to, the
activities identified in Section 15.02.060 of this
chapter.
“Development intensities” for the purpose of Section
15.02.120 of this chapter, development intensities shall consist of two
types:
1. High Intensity. Any use or activity with a high probability of
disturbing a wetland and wetland fauna and flora, including but not limited to,
construction of buildings, roads, and other improvements, land clearing and loud
noises.
2. Low Intensity. Any use activity with a low probability of
disturbing a wetland and wetland fauna and flora.
“Enhancement”
means actions performed to improve the condition or functions and values of an
existing viable wetland or buffer, or fish and wildlife habitat area or buffer.
Enhancement actions include but are not limited to increasing plant diversity,
increasing fish and wildlife habitat, installing environmentally compatible
erosion controls, and removing invasive plant species such as milfoil and
loosestrife.
Erosion Hazard Area. See “Geologic hazard
areas.”
“Excavation” means the mechanical removal of earth
material.
Existing and On-going Agricultural Activities. See
“Agricultural activities.”
“Fill material” means a
deposit of earth or other natural or man-made material placed by artificial
means.
“Filling” means the act of placing fill material (on any
critical area) including temporary stockpiling of fill material.
“Fish
and wildlife habitat conservation areas” means those areas identified as
being of critical importance to maintenance of fish and wildlife including those
listed in Table 15.02.130-1.
“Floodway” means those portions of
the area of a river valley lying streamward from the outer limits of a
watercourse upon which flood waters are carried during periods of flooding that
occur with reasonable regularity, although not necessarily annually, said
floodway being identified, under normal condition, by changes in surface soil
conditions or changes in types or quality of vegetative ground cover
condition.
“Geologic hazard areas” means areas susceptible to
erosion, sliding, earthquake, or other geologic events (see Section 15.02.150 of
this chapter for classifications).
“Grading” means an excavating
and/or filling of the earth’s surface or combination
thereof.
“Hydric soils” means soils which are wet long enough to
periodically produce anaerobic (reduced oxygen) conditions, thereby influencing
plant growth.
“Hydrologic unit (watershed)” means an area of
land above or upstream from a specific point on a stream, which is enclosed by a
topographic divide such that direct surface runoff from precipitation normally
drains by gravity into the stream or the area above the specified point on a
stream.
“Indigenous” means any native species of plant or
wildlife that occurs naturally on a particular site or
area.
“Lake” means a naturally existing or artificially created
body of standing water, including reservoirs, twenty acres or greater in size,
which exists on a year-round basis and occurs in a depression of land or
expanded part of a stream.
“Landfill” means a disposal facility
or part of a facility at which solid waste is placed in or on
land.
“Landslide” means the abrupt downslope movement of a mass
of soil or rock.
Landslide Hazard Area. See Section
15.02.150(D).
“Liquefaction” is a process in which soil loses
strength, and behaves like a liquid.
“Mitigation” means an
action designed to replace project-induced critical area losses or impacts;
including, but not limited to, avoiding, minimizing, or compensating for adverse
wetland impacts. Mitigation in order of preference:
1. Avoiding the impact
altogether by not taking a certain action or parts of actions;
2. Minimizing
impacts by limiting the degree or magnitude of an action and its
implementation;
3. Rectifying impacts by repairing, rehabilitating or
restoring the affected environment;
4. Reducing or eliminating an impact
over time by preservation and maintenance operations during the life of the
action;
5. Compensating for an impact by replacing or providing substitute
resources or environments;
6. “In-kind mitigation” means
replacement of wetlands or surface water systems with substitute wetlands or
surface water systems whose characteristics and functions and values closely
approximate those destroyed or degraded by a regulated
activity;
7. “Out-of-kind mitigation” means replacement of
surface water systems or wetlands with substitute surface water systems or
wetlands with characteristics which do not closely approximate those destroyed
or degraded by a regulated activity.
“Noxious weeds” means any
plant which, when established, is highly destructive, competitive or difficult
to control. The county maintains a noxious weed list.
“Open
space” means land classified as open space under Chapter 84.34 RCW for its
current use value and placed in open space tax
assessment.
“Pond” means a naturally existing or artificially
created body of standing water under twenty acres, which exists on a year-round
basis and occurs in a depression of land or expanded part of a
stream.
“Primary association of a species” includes its breeding
areas, nesting areas, primary foraging areas, and primary migration
corridors.
“Priority habitat” means those habitat types or
elements with unique or significant value to a diverse assemblage of species. A
priority habitat may consist of a unique vegetation type or dominant plant
species, a described successional stage, or a specific structural
element.
“Qualified professional” means a person who has
received a degree form an accredited college or university in a field necessary
to identify and evaluate a particular critical area, and/or a person who is
professionally trained, licensed and certified in such field(s). Areas of
technical expertise shall generally be as follows: wetlands biology or ecology
(for wetlands); stream and/or fisheries biology or ecology (for streams);
wildlife biology or ecology (for critical habitat); or a Washington State
licensed geologist, hydrogeologist or engineering geologist (most frequently
referred to as a geotechnical engineer). A qualified wetland professional shall
be certified by the Society of Wetland Scientists as a professional wetland
science or wetland professional in training. When a landscape or planting plan
is required by these regulations, a qualified professional is one who has
demonstrated expertise in the use of indigenous plant species, slope
stabilization, and arboricultural practices. A qualified professional shall be
required to demonstrate the basis for their qualifications, and submit copies of
past reports that have been accepted by other jurisdictions on critical area
permit applications. A demonstration of qualifications may include, but shall
not be limited to submission of a copy of professional certification, such as
either a graduate certificate or state license.
“Regulated
activity” for the purposes of this chapter (other regulations can or may
apply as well) means activities occurring in a critical area or associated
buffer that are subject to the provisions of this chapter. See regulated
activities in KMC Section 15.02.060.
“Restoration” means efforts
performed to reestablish functional values and characteristics of a critical
area that have been destroyed or degraded by past alterations (e.g., filling or
grading).
“Riparian habitat” means areas adjacent to aquatic
systems with flowing water that contain elements of both aquatic and terrestrial
ecosystems that mutually influence each other. The width of these areas extends
to that portion of the terrestrial landscape that directly influences the
aquatic ecosystem by providing shade, fine or large woody material, nutrients,
organic and inorganic debris, terrestrial insects, or habitat for
riparian-associated wildlife. Widths shall be measured from the ordinary high
water mark. It includes the entire extent of the floodplain and the extent of
vegetation adapted to wet conditions as well as adjacent upland plant
communities that directly influence the stream system. Riparian habitat areas
include those riparian areas severely altered or damaged due to human
development activities.
“Shorelands and shoreland areas” means
those lands extending landward for two hundred feet in all directions as
measured on a horizontal plane from the ordinary high water mark; floodways and
contiguous floodplain areas landward two hundred feet from such floodways; and
all wetlands and river deltas associated with the streams, lakes and tidal
waters which are subject to the provisions of Chapter 90.58
RCW.
“Site” means any parcel or combination of contiguous
parcels, or right-of-way, or combination of contiguous rights-of-way under the
applicant’s ownership or control where the proposed regulated activity
occurs.
“Slope” means an inclined earth surface, the inclination
of which is expressed as the ratio of horizontal distance to vertical distance.
In these regulations, slopes are generally expressed as a percentage; percentage
of slope refers to a given rise in elevation over a given run in distance.
Slopes fifteen to thirty percent constitute areas of geologic concerns. Slopes
greater than thirty percent constitute potential areas of geological
hazard.
“Snag” means any dead, partially dead, or defective
(cull) tree at least ten feet tall and twelve inches in diameter at breast
height.
“Snag-rich areas” means areas that are characterized by
the presence of relatively high numbers of large diameter (> twenty inches
dbh) snags, in varying states of decay, suitable for use by broad and diverse
groups of wildlife. Snag-rich areas include naturally regenerated (un-managed)
forests, riparian areas, and burned, damaged, or diseased forests. Snag-rich
areas may also include individual snags or small groups of snags of exceptional
value to wildlife due to their scarcity or location in particular
landscapes.
“Streams” means water contained within a channel,
either perennial or intermittent, and classified according to WAC 222-16-030 or
WAC 222-16-031. Streams also include natural watercourses modified by man.
Streams do not include irrigation ditches, waste ways, drains, outfalls,
operational spillways, channels, stormwater runoff facilities or other wholly
artificial watercourses, except those that directly result from the modification
to a natural watercourse.
“Talus slope” means a slope formed by
the accumulation of rock debris at the bottom of steep slopes or
cliffs.
“Utility line” means pipe, conduit, cable, or other
similar facility by which services are conveyed to the public or individual
recipients. Such services shall include, but are not limited to water supply,
electric power, natural gas, communications and sanitary
sewer.
“Wetland” means areas that are inundated or saturated by
surface water or ground water at a frequency and duration sufficient to support,
and that under normal circumstances do support, a prevalence of vegetation
typically adapted for life in saturated soil conditions. Wetlands generally
include swamps, marshes, bogs, and similar areas. Wetlands do not include those
artificial wetlands intentionally created from nonwetland sites, including, but
not limited to, irrigation and drainage ditches, grass-lined swales, canals,
detention facilities, wastewater treatment facilities, farm ponds, and landscape
amenities. This definition does include, however, those artificial wetlands
intentionally created to mitigate for the conversion of existing wetlands. The
three general types of wetlands are emergent, forested and scrub-shrub. The
Washington State Wetlands Identification and Delineation Manual (Ecology, March
1997) based on the 1987 Corps of Engineers Wetland Delineation Manual will be
used to delineate wetland boundaries.
“Wetland functions” are
determined by physical, chemical and biological characteristics and include but
are not limited to: fish and wildlife habitat, aquifer recharge and discharge,
water quality, shoreline stabilization, and flood and erosion
control.
“Wetland value” means wetland processes or attributes
that are valuable or beneficial to society. (Ord. 1137 § 2 (part),
2004).
15.02.060 Applicability/regulated activities.
A. All persons proposing development in critical areas or their buffers
shall first obtain a critical areas permit pursuant to this chapter, except as
exempted pursuant to Section 15.02.070 of this chapter. A critical area that
extends beyond or is adjacent to the boundaries of the proposed project site
shall be reviewed in its entirety and not only the portion contained within or
adjacent to the site.
B. Development activities shall include, but are not
limited to the following:
1. Removing, clearing, grading, excavating,
disturbing, or dredging soil, sand, gravel, minerals, organic matter or
materials of any kind;
2. Dumping, discharging or filling with any
material;
3. Subdivisions, short subdivisions, planned unit developments
(PUDs), manufactured housing parks and RV parks;
4. Construction,
reconstruction, demolition or alteration of the size of any structure or
infrastructure;
5. Construction of any new public or private road or
driveway;
6. Destroying, planting or altering vegetation through clearing,
harvesting, cutting, intentional burning, shading, or planting nonnative species
where these activities would alter the character of a critical area, or its
buffer;
7. Draining, flooding, or disturbing the water level or water
table;
8. Activities causing adverse changes in water temperature, physical
or chemical changes of water sources to wetlands or surface water
systems;
9. Chemical applications that are determined by the city and/or the
Department of Fish and Wildlife to be harmful to wetland habitat, riparian
corridors associated with surface water systems, or wildlife or fish life. (Ord.
1137 § 2 (part), 2004).
15.02.070 Exemptions.
Upon determination by the city, the following activities may be exempt
from the provisions of this chapter:
A. The policies, regulations, and
procedures of this chapter do not apply to those activities and uses conducted
pursuant to the Washington State Forest Practices Act and its rules and
regulations, RCW 76.09 and WAC 222, where state law specifically limits local
authority, except with regard to developments and conversions requiring local
approval, and when the city is the lead agency for environmental
review;
B. Existing and on-going agricultural activities not involving
chemical applications as defined in this chapter;
C. Development occurring
within a seismic hazard area as described in Section 15.02.150(D)(3) and
containing no other critical area as defined by this chapter;
D. Development
occurring within frequently flooded areas and containing no other critical area
as defined by this chapter, provided, the development meets the requirements of
Kalama Municipal Code Chapter 14.16, Floodplain Management;
E. Maintenance,
operation, reconstruction of existing public and private roads, streets,
driveways, utility lines, and existing public buildings and facilities provided
that reconstruction of any such facilities does not extend outside the
previously disturbed portions of the right-of-way or building lot
lines;
F. Exterior alterations to existing single-family residential
structures comprising up to twenty-five percent of the existing building’s
footprint, but not to exceed five hundred square feet, if such alteration or
construction does not involve the excavation of materials from any adjacent
slope which is greater than fifteen percent, and if such alteration does not
extend further into a critical area;
G. Construction, alteration or
enlargement of decks, patios, walkways and other outside fixtures common to
residential housing and commercial activities, not involving the use of
industrial construction equipment such as backhoes, tractors, cranes, and does
not create additional impacts on an adjacent critical area;
H. For lands not
involving wetlands, wildlife habitats, designated endangered species areas, or
slopes greater than fifteen percent, excavation, grading, and filling the
following would be exempted:
1. If the excavation is less than two feet in
depth or does not create a cut slope greater than five feet in height and
steeper than one unit vertical in one and one-half units horizontal (sixty-six
and seven tenths percent slope) and does not exceed fifty cubic
yards,
2. Fill is less than one foot in depth and placed on natural terrain
with a slope flatter than one unit vertical in five units horizontal (twenty
percent slope), or less than three feet in depth, not intended to support
structures, that does not exceed fifty cubic yards on any one lot and does not
obstruct a drainage course (as stated in the 1997 edition of the Uniform
Building Code Appendix Chapter 33.3306.02(9));
I. The removal or control of
noxious weeds not involving chemical application, excavation, mechanical weed
control with the use of hand held tools and/or flooding;
J. Maintenance of
ground cover or other vegetation in a critical area or buffer area that was
disturbed prior to January 2000, provided that, no further disturbance is
created;
K. Minimal site investigative work required by the city, state or a
federal agency, or any other applicant such as surveys, soil logs, percolation
tests, and other related activities, provided that impacts on environmentally
critical areas are minimized and disturbed areas are restored to the
pre-existing level of function and value within one year after tests are
concluded;
L. Passive recreational uses, sport fishing or hunting,
scientific or educational review, or similar minimum impact, nondevelopment
activities;
M. Maintenance of intentionally created artificial wetlands or
surface water systems including irrigation and drainage ditches, grass-lined
swales and canals, detention facilities, farm ponds, and landscape or ornamental
amenities. Wetlands, natural streams, natural streams that are channelized,
lakes or ponds created as mitigation for approved land use activities or that
provide critical habitat are not exempt and shall be regulated according to the
mitigation plan;
N. Activities occurring in nonregulated wetlands.
Shoreline, state and federal regulations may apply to wetlands not regulated
under this chapter;
O. Emergency actions;
1. Emergency actions which
must be undertaken immediately or for which there is insufficient time for full
compliance with this chapter when it is necessary to:
a. Prevent an imminent
threat to public health or safety,
b. Prevent imminent danger to public or
private property, or
c. Prevent an imminent threat of serious environmental
degradation;
2. In the event a person or emergency agency determines that
the need to take emergency action is so urgent that there is insufficient time
for review by the city, such emergency action may be taken immediately, as long
as the following requirements are observed:
a. Work is limited to the
minimum work necessary to alleviate the emergency,
b. For emergency work
within waters of the state, the person or agency undertaking such action will
receive verbal hydraulic permit approval from the Washington Department of Fish
and Wildlife prior to beginning any work,
c. The person or agency
undertaking such action shall notify the city within one working day following
the commencement of the emergency activity. Following such notification, the
city shall determine if the action taken was within the scope of the emergency
actions allowed in this subsection. If the city determines that the action taken
or a portion of the action taken is beyond the scope of allowed emergency
actions, the city may initiate enforcement action, as set forth in KMC Section
15.20.200,
d. Upon completion of the emergency repair or restoration work,
all damage to the critical area shall be fully restored;
P. Projects with a
footprint of less than five hundred square feet which are not placed on fill or
require no excavation into slopes greater than fifteen
percent;
Q. Construction of structures on lots with slopes of greater than
fifteen percent, if the city receives a report prepared in the last five years
by a qualified professional who has examined the site and the report clearly
states that construction on the site will not cause any geologic hazards, to the
proposed building or surrounding properties. (Ord. 1137 § 2 (part),
2004).
15.02.080 Optional incentives for nondevelopment of critical areas.
A. Introduction. This section describes the alternatives available to
property owners and incentives they may pursue in lieu of developing or altering
their property under the terms and standards of this chapter. The incentives and
options listed allow property owners to use any or all of the options that best
suit their needs.
B. Open Space. Any person who owns an identified critical
area as defined by this chapter may apply for current use assessment pursuant to
Cowlitz County Code Chapter 18.52, the Cowlitz County Open Space Ordinance, and
RCW 84.34, Open Space, Agriculture, and Timber Lands--Current Use
Assessment-Conservation Futures.
C. Conservation Easement. Any person who
owns an identified critical area as defined by this chapter shall be entitled to
place a conservation easement over that portion of the property designated a
critical area by naming the city or its qualified designee under RCW 64.04.130
(Interests in land for purposes of conservation, protection, preservation,
etc.--Ownership by certain entities--Conveyances) as beneficiary of the
conservation easement. The purpose of the conservation easement shall be to
protect, preserve, maintain, restore, limit the future use of, or conserve for
open space purposes the land designated as critical area(s), in accordance with
RCW 64.04.130. Details governing easement restrictions shall be negotiated
between the property owners and the city. See process for conservation easement
or density incentives, subsection E of this section.
D. Density Adjustments.
The city shall allow transfer of density for residential uses from lands
containing critical areas, as defined by this chapter, when developed pursuant
to Kalama Municipal Code Chapter 16.18, Planned Unit Development. Residential
density may only be transferred from a critical area to an area on the same site
which is not a critical area. For development proposals on lands determined to
contain critical areas as defined by this chapter, the city shall determine
allowable dwelling units for residential development proposals based on the
formula below.
|
Percentage of Site in Critical Area
|
Percentage of Adjustment
|
|
1--10%
|
100%
|
|
11--20%
|
90%
|
|
21--30%
|
80%
|
|
31--40%
|
70%
|
|
41--50%
|
60%
|
|
51--60%
|
50%
|
|
61--70%
|
40%
|
|
71--80%
|
30%
|
|
81--90%
|
20%
|
The density adjustment can only be applied within the development
proposal site and any fractional amounts will be rounded down. The applicant may
reduce lot sizes below the minimum required for that zone (residential
designation) to accommodate the transfer of density by following the procedures
set forth in the Kalama Municipal Code Chapter 16.10.
E. The process for
conservation easement or density incentives will be as follows:
1. Contents
of Application. Record owners of real property seeking relief under this section
shall file with the city council an application for a conservation easement,
density incentives or adjustments.
2. Contents of Application. The applicant
is responsible for submitting a complete and accurate application. A complete
application shall include:
a. Completed master application and/or any
required supplement sheets signed by the owner of the property;
b. A map
drawn to scale, showing the following information:
i. Name, address and
telephone number of the property owners(s),
ii. Name, address and telephone
number of the preparer of the application,
iii. Date of
submittal,
iv. North arrow,
v. Property boundary lines,
vi. A legal
description of the property,
vii. A description of the nature, size and
location of each critical area located on the property, as determined by a
qualified professional,
viii. All existing and/or public and private roads,
sewer, and water lines, wells, county utilities, easements, water courses,
lakes, springs, drainage facilities, on-site sewage disposal drainfield areas,
on and within one hundred feet of the property boundaries,
ix. The
boundaries of all lands reserved in the deeds for the common uses of the
property owners.
3. City Staff Action. The city clerk-treasurer, public
works director and city planner shall determine if the application is complete
within twenty-eight days. If additional information is necessary, the
application shall be returned to the property owner, together with a list
identifying the deficiencies. When the application is complete, the city staff
shall determine whether all or part of the property is in fact subject to any
critical area regulations in this chapter. Staff shall forward written findings
to the council.
4. Council Decision. Within thirty days of receipt of the
staff’s findings, the council shall make the final determination on
whether all or part of the property is subject to this chapter. For conservation
easement applications, if the council determines that all or part of the
property is subject to this chapter, the council shall consider the acceptance
of a conservation easement, as beneficiary on behalf of the city or its
qualified designee under RCW 64.04.130, over that portion of the property
subject to this chapter to the extent requested by the record owner of the
property. The grantee of a conservation easement must agree to execute the
easement form approved by the city attorney. For density incentive applications,
the council shall consider a requested density transfer subject to its final
approval of a preliminary subdivision plat. The application for density transfer
must be submitted as a part of the preliminary plat application.
F. Land
Exchange. State agencies or local government may convey, sell, lease or trade
existing public lands in order to obtain public ownership of a fee interest,
leasehold interest or conservation easement over all or part of a critical area.
Such exchanges may occur only upon agreement between the record owner and state
and local agencies authorized to exchange the subject land. The process for land
exchange involving the city of Kalama will be as follows: all applications for
land exchanges must be filed in accordance with the requirements of this
section. For the purposes of this section, any requirements to provide
information, appraisals or notice relating to the “property” or
“subject property” shall apply to all properties involved in the
proposed exchange.
1. Contents of Application. The applicant is responsible
for submitting a complete and accurate application. A complete application shall
include:
a. Completed master application and/or any required supplement
sheets signed by the record owner of the property;
b. A map, drawn to scale,
showing the following information:
i. Name, address and telephone number of
the property owners(s),
ii. Name, address and telephone number of the
preparer of the application,
iii. Date of submittal,
iv. North
arrow,
v. Property boundary lines and dimensions,
vi. Legal description
of the property,
vii. Description of the nature, size and location of each
critical area located on the property, as determined by a qualified
professional,
viii. All existing public or private roads, sewer and water
lines, wells, city utilities, easements, water courses, lakes, springs, drainage
facilities, on-site sewage disposal drainfield areas, on and within one hundred
feet of the property boundaries,
ix. The boundaries of all lands reserved in
the deeds for the common uses of the property owners,
x. A written appraisal
from a licensed appraiser of the city’s choice, providing the fair market
value of the properties,
xi. An environmental assessment of the property,
indicating the presence or absence of environmental contaminants. The city shall
commission the assessment at the property owner’s cost.
2. City Staff
Action. The city clerk-treasurer, public works director and the city planner
shall determine if the application is complete within twenty-eight days. If
additional information is necessary, the application shall be returned to the
property owner, together with a list identifying the deficiencies. Staff shall
forward written findings to the council.
3. Council Action. The city council
shall hold a public hearing to review all property owner requests, pursuant to
this section. Notice of public hearing shall be made at least thirty days prior
to the scheduled hearing date. Notice shall consist of the publication of a
legal notice in the newspaper of record stating the description of the property,
and the purpose, date, time and location of the hearing. Such notice shall also
be mailed first class to the property owner and all persons owning property, as
identified in the auditor’s records, within three hundred feet of the
subject property boundaries thirty days prior to the hearing. And, two or more
notices shall be posted in the vicinity of the subject property ten days prior
to the hearing. Procedures for land exchanges may be subject to additional
notice and advertising requirements.
4. Following the public hearing, the
council shall issue its written decision, with findings. There shall be no
deadline for the city council’s decision on land exchanges, which shall be
completely discretionary. (Ord. 1137 § 2 (part), 2004).
15.02.090 Critical areas determination.
A determination of critical areas is required for all land use or
development applications. Staff will conduct an environmental review, based on
existing in-house data and an on-site inspection, to determine if critical areas
exist on or are adjacent to a parcel and whether the site or project is exempted
as provided in Section 15.02.070 of this chapter.
A. Complete Application
for Critical Area Determination. A complete application for a critical area
determination will include all of the following:
1. A completed master
application with applicable land use application, including a critical area
checklist;
2. A vicinity map;
3. A site drawing showing property
boundaries, and existing plus proposed development locations on-site;
4. A
critical area determination fee.
B. Staff Determination of a Critical Area.
A critical area determination is made by the city staff, without a public
hearing. The determination will be based upon:
1. Review of the critical
area determination application, together with any optional critical area study
submitted by the applicant;
2. Review of materials and information compiled
by the city of Kalama, including any consultant report the city may commission;
and
3. On-site inspection of the property.
C. Issuance of Determination
of Critical Area. The determination shall be in writing and shall be provided to
the applicant and property owner of record, if different than the applicant.
When a critical area exists, a critical area determination notice will be
issued. A property owner may request a redetermination by the staff once in any
twelve-month period, subject to fees, when a change in physical conditions or
government institutional actions warrant such redetermination. Formal appeal may
be made in accordance with this section. (Ord. 1137 § 2 (part),
2004).
15.02.100 Critical area permit.
If the critical area determination reveals that there is a critical
area(s) on the property subject to the underlying land use or development
permit, an application for a critical area permit must be submitted. No
development or activity may take place on the property with critical areas
except in conformance with this chapter and an issued critical areas
permit.
A. Critical Area Permit Application. A complete application for a
critical area permit shall consist of the following:
1. A Detailed Site Plan
Drawn to Scale. The site plan should clearly show the following
information:
a. North arrow,
b. Property boundary line and
dimensions,
c. Location and dimensions of all existing and proposed
development or alternations, including public and private roads, sewer and water
lines, wells, utilities, easements, water sources, lakes and springs, drainage
facilities, on-site sewage disposal and drainfield areas, within the property
boundary,
d. All critical areas, buffers and the development proposal with
dimensions,
e. Limits of any areas to be cleared;
2. A copy of the
determination of critical area issued by the city showing it having been
recorded through the county auditor’s office;
3. A stormwater
management plan for the project with consideration of the drainage impacts based
on “best management practices”;
4. Critical area report(s)
addressing the specific critical area(s) on the site including all information
as defined in the applicable Appendix(s) B through E. This report must also
include the following:
a. The date the report was prepared,
b. The
names, and qualifications of all person(s) preparing the report,
c. The
professional stamp of the person(s) preparing the report,
d. The dates and
documentation of any fieldwork preformed on the site,
e. A statement
verifying the accuracy of the report, as well as all assumptions relied upon in
the report,
f. An assessment of the probable cumulative impacts to critical
areas resulting from development of the site,
g. Analysis of site
development alternatives,
h. A SEPA environmental checklist if the site is
located within any of the following:
i. Geologic hazard
area,
ii. Wetlands,
iii. Riparian habitat area;
5. A permit
fee.
B. Area Permit Approval Criteria. An application for a critical area
permit shall demonstrate compliance with all of the following criteria in order
to be approved:
1. The proposed alteration, activity or development proposal
must satisfy all standards for alterations, activities or development in
critical areas, as set forth in this chapter;
2. The proposed mitigation
shall be supported by sufficient evidence to demonstrate that the mitigation
will protect the critical area, and ensure no net loss of critical habitat value
or functions; and
3. The proposed alteration, activity or development
proposal shall be consistent with all other applicable codes.
C. Issuance of
Critical Area Permit. Decisions on critical areas permits are made by the same
authority as the underlying development application. The critical areas permit
shall be approved, approved with conditions or denied based on the above
criteria. The decision on a critical area permit shall be in writing and shall
be supported by written findings of fact and conclusions. Appeals of critical
area permit decisions shall follow the process set forth in Section 15.02.190 of
this chapter. (Ord. 1137 § 2 (part), 2004).
15.02.105 Relationship to other regulations.
Areas characterized by a particular critical area may also be subject to
other regulations due to the overlap of multiple functions of critical areas. In
the event of any conflict between these regulations and any other regulations of
the city, the regulations which provide the greater protection for critical
areas shall apply. No permit granted pursuant to this chapter shall remove
applicant’s obligation to comply in all respects with the applicable
provision of any other federal, state or local law or regulation. (Ord. 1137
§ 2 (part), 2004).
15.02.110 Critical area inventory maps.
A. The approximate location and extent of critical areas and lands within
the city planning area are shown on the maps adopted as part of this chapter.
These maps are based on the best available information and are intended to be
used as a general guide for the assistance of property owners and as information
for the public. Boundaries are generalized; field investigation and analysis by
the city may be required to confirm the existence of a critical area. The city
will update information and resource material when new data is available and
updates are feasible.
B. In the event of any conflict between the location,
designation or classification of a critical area shown on the city maps and the
criteria or standards of this section, the criteria, standards and determination
of any field investigation shall prevail.
Table 15.02.110-1
Summary of Map
Sources
|
Topic
|
Map/Data Sources
|
|
Geologically Hazardous Areas
|
1. Slope Stability of Longview-Kelso Urban Area, Division
of Geology and Earth Resources, Department of Natural Resources, 1973.
2. Geologic Hazard Map of Cowlitz County, Cowlitz County
GIS Department.
3. Soil Conservation Service, Cowlitz Area Soil Survey,
1974, or as amended.
4. Other Department of Natural Resource Maps--when
available.
|
|
Frequently Flooded Areas
|
5. FEMA, National Flood Insurance Program, Flood
Insurance Rate Maps.
|
|
Critical Aquifer Recharge Areas
|
6. Cowlitz County Aquifer Recharge Map, Cowlitz County
GIS Department 1993.
|
|
Wetlands
|
7. City of Kalama’s Wetland Inventory Map, Cowlitz
County Wetlands Map, Cowlitz County GIS Department, 1993 Source: Hydric Soils,
USDA, Soil Conservation Service; National Wetlands Inventory Maps, US Department
of Interior, Fish and Wildlife Service.
|
|
Fish and Wildlife Habitat Conservation Areas
|
8. Priority Habitat and Species Maps, Washington
Department of Wildlife, 1991, as amended.
9. Forest Practice Act Stream Mapping, as
amended.
|
(Ord. 1137 § 2 (part), 2004).
15.02.120 Critical area wetlands.
A. Wetland physical functions include but are not limited to:
1. Flood
control functions;
2. Fish and wildlife habitat environments;
3. Ground
and surface water aquifer recharge functions;
4. Sediment retention and
pollution control functions.
B. Wetland Classification. Wetlands shall be
rated according to the Department of Ecology’s publication titled Wetlands
Rating System for Western Washington (publication No. 93-074, 1991), which is
based on the Washington State Four-Tier Wetlands Rating System, and regulated
according to the threshold outlined in subsection C, of this
section.
1. Category 1. Documented site-specific habitat for state listed
endangered, threatened or sensitive animal species. WAC
232-12-011.
2. Category 2.
a. High quality, regionally rare, wetland
with irreplaceable ecological functions;
b. Complex wetlands of three or
more wetland types which cannot be replicated through newly created wetlands or
restoration; or
c. Wetlands improved or enhanced by agency approved
mitigation projects.
3. Category 3. Wetlands of sufficient characteristics
to provide any of the following:
a. Flood control functions;
b. Ground
and surface water aquifer recharge function;
c. Fish and wildlife
habitat;
d. Water quality attributes for sediment retention and pollution
control; or
e. Wetlands of any size created as a result of agency
approved/permitted mitigation projects.
4. Category 4.
a. Wetlands
dominated by nonnative, invasive plant species;
b. Wetlands two acres or
larger which are not classifications 1, 2, 3 or 4(a) wetlands.
C. Wetland
Designation. For the purposes of this chapter, “regulated wetland
designation for minimum size” is as follows:
|
Wetland Classification
|
Minimum Size
|
|
Category 1
|
No minimum size
|
|
Category 2
|
No minimum size
|
|
Category 3
|
No minimum size
|
|
Category 4(a)
|
1 acre
|
|
Category 4(b)
|
2 acres
|
D. Development Limitations--Alterations of Wetlands. Regulated
development, as described in Section 15.02.060, shall conform with and be
governed by the following:
1. Alteration of category 1 wetlands is
prohibited unless the alteration would improve or maintain the existing wetland
function and value, or the alteration would create a higher value or less common
wetland type which would improve the functions or values of the wetland as
indicated within the wetland technical study and the mitigation plan, developed
by a qualified wetland professional.
2. Alteration of categories 2 and 3
wetlands may be allowed only when it is demonstrated, by a qualified wetland
professional, through a wetlands site assessment that any of the following
criteria are met:
a. Public benefit will accrue through the
alteration;
b. No reasonable and practical alternative to the alteration
exists through on-site design; or
c. The alteration would improve or
maintain the existing wetland function and value, or the alteration would create
a higher value or less common wetland type with more functions and values as
indicated within the wetland technical study and the mitigation
plan.
3. Alteration of categories 4(a) and 4(b) regulated wetlands may be
allowed if adequate alternatives cannot be identified during the site plan
review process and other state and federal regulatory agencies concur with the
alteration.
E. Wetland Buffers. The purpose of a buffer is to provide
appropriate protection to any identified wetland to maintain the structure,
function, and values of the wetland system.
1. Buffers are required for all
regulated wetlands (see Definitions for “regulated wetland”
definition). Wetland buffer widths are established, based on the wetland
category and the land use intensity adjacent to it (as determined by the city
zoning code), as follows:
Table 15.02.120-1
Wetland Buffers
|
Categories
|
Buffer Width (in feet)
|
|
High Intensity Zones R-3, C-1, C-2, & I-1
|
Low Intensity Zones R-1 & R-2
|
|
I
|
300
|
200
|
|
II
|
200
|
100
|
|
III
|
100
|
50
|
|
IV
|
50
|
25
|
2. Buffer widths shall be measured perpendicular to the delineated
boundaries of the regulated wetland and extend horizontally the required
distance.
3. Variable buffer widths as set forth in subsection (E)(1) and
Table 15.02.120-1 are intended to protect the wetlands physical functions based
on:
a. A complete mapping of the wetland category unit on which the
regulated wetland is located shall be submitted for approval by the city;
and
b. Following a site visit by a qualified wetland, wildlife and fish
habitat professional, a report shall be submitted to the city, which evaluates
the impact of current and proposed land uses on the regulated wetland site, and
how the selected buffer width will minimize or reduce those impacts (See
Appendix C.)
4. Buffer widths intended to protect the wetland and associated
fish and wildlife habitat shall be based on Table 15.02.120-1.
5. Buffer
widths may be reduced on a case-by-case basis when it is determined to the
satisfaction of the city that a smaller area is adequate to protect the wetland
functions and values based on site-specific characteristics. Applicants for a
“buffer width reduction request” shall submit to the city a wetland
report as described in Appendix “C” of this chapter at the same time
they submit all other development applications. In no case shall the standard
buffer width be reduced by more than twenty-five percent, or the buffer width be
less than fifty feet except for buffers between category IV wetlands and low or
moderate intensity land uses. The city shall require a two-year monitoring
program to be developed to the satisfaction of the city. The monitoring program
shall require that quarterly “reports” be submitted to the city for
evaluation and approval. Subsequent corrective actions may be required if
adverse impacts to wetlands are discovered during the monitoring period. The
following information must be placed in the “wetland report”
supporting the reduction of any buffer:
a. The wetland report provides sound
rationale for the reduced buffer based on the best available science. The
rationale is supported by the Washington State Department of Ecology and the
Department of Fish and Wildlife;
b. The existing buffer area is
well-vegetated with native species and has less than ten percent slopes;
and
c. No direct or indirect, short-term or long-term, adverse impacts to
wetlands are identified by the Washington State Department of Ecology or the
Department of Fish and Wildlife, resulting from the proposed reduction of the
wetland buffer and the subsequent proposed development of the site in
question.
F. Buffer Width Alterations--Wetland Variances and Width
Averaging.
1. Requests for variances to the wetland buffer widths may be
applied for in accordance with procedures as set forth in Kalama Municipal Code
Section 17.52.030, Application.
2. The city’s hearing examiner, may
grant variances from the regulated buffer widths as set forth in this section,
provided, that the applicant has not applied for a wetland buffer width
reduction, and where it can be shown, through a report prepared by a qualified
wetlands professional that granting the variance will not negatively impact the
required enhancements, functions and values of the wetland the buffer it is
intended to protect.
3. One of the ways that the buffer widths may be
modified or altered is by averaging (decreasing or increasing) the buffer width.
For example, if the widest width in a proposed buffer is fifty feet and the
narrowest width is twenty-five feet, the average width would be thirty-seven
feet, six inches wide.
4. The hearings examiner can grant the buffer width
averaging only if the applicant can demonstrate to the city through a report as
set forth in subsection E, buffer width reductions, of this section prepared by
a qualified wetlands specialist, all of the following:
a. The buffer width
averaging will not adversely impact the function and/or values of the
wetland;
b. Low intensity land uses will be adjacent to the reduced buffer
widths;
c. The total area contained within the averaged buffer is equal to
the required minimum within the standard buffer;
d. In no instance will the
buffer width be reduced more than fifty percent or be less than fifty feet for
any stormwater drainage way or a wetland site; and
e. The buffer area
proposed to be designated in buffer width averaging shall be contiguous to the
original buffer area and shall not include on-site septic systems, public or
private roadways, structures, or aboveground utilities. Existing disturbed areas
may not be approved for use as a buffer averaging area.
G. Activities
Allowed in a Wetland Buffer Zone. Activities within a buffer zone may be allowed
if prior to undertaking any activity in the buffer zone, the applicant shall
demonstrate that the activity has no adverse impact on the function of buffer
zones. Examples include: educational or scientific projects, nonmotorized
recreation, and utilities. Such activities or projects shall be consistent with
the wetland development limitations and mitigation standards set for the
buffered wetland. Prior to engaging in any activity, the applicant shall submit
documentation to the city that demonstrates the activity has:
1. Minimized
the buffer impact on regulated wetlands;
2. Fully mitigated or compensated
for all buffer alterations on regulated wetlands.
H. Wetland Mitigation
Standards.
1. Mitigation for alterations to wetlands shall achieve
equivalent or greater biologic functions. Mitigation plans shall be consistent
with the Department of Ecology Guidelines for Developing Freshwater Wetlands
Mitigation Plans and Proposals, 1994, as revised.
2. Wetland mitigation
actions shall not result in a net loss of wetland areas except when the
following criteria are met:
a. The lost wetland area provides minimal
functions and the mitigation action(s) results in a net gain in wetland
functions as determined by a site-specific function assessment; or
b. The
loss of wetland area provides minimal functions as determined by a site-specific
function assessment and other replacement habitats provide greater benefits to
the functioning of the watershed, such as riparian habitat restoration and
enhancement.
3. Mitigation actions shall address functions affected by the
alteration to achieve functional equivalency or improvement, and shall provide
similar wetland functions as those lost except when:
a. The lost wetland
provides minimal functions as determined by a site-specific function assessment
and the proposed mitigation action(s) will provide equal or greater functions or
will provide functions shown to be limiting within a watershed through a formal
watershed assessment plan or protocol; or
b. Out-of-kind replacement will
best meet formally identified regional goals such as replacement of historically
diminished wetland types.
4. Mitigation actions that require compensation by
replacing, enhancing or substitution, shall occur in the following order of
preference:
a. Restoring wetlands on upland sites that were formerly
wetlands;
b. Creating wetland on disturbed upland sites such as those with
vegetative cover consisting primarily of exotic introduced
species;
c. Enhancing significantly degraded wetlands;
d. Preserving
high-quality wetlands that are under imminent threat.
5. Mitigation actions
shall be conducted within the same sub-drainage basin and on the site as the
alteration except when all of the following apply:
a. There are no
reasonable on-site or in sub-drainage basin opportunities or on-site and in
sub-drainage basin opportunities do not have a high likelihood of success due to
development pressures, adjacent land uses, or on-site buffers or connectivity
are inadequate;
b. Off-site mitigation has a greater likelihood of providing
equal or improved wetland functions than the impacted wetland;
and
c. Off-site locations shall be in the same sub-drainage basin and the
same Water Resource Inventory Area (WRIA) unless:
i. The impact is located
near the boundary of a WRIA,
ii. Established regional or water shed goals
for water quality, flood or conveyance, habitat or other wetland functions have
been established and strongly justify location or mitigation at another
site.
6. Where feasible, mitigation projects shall be completed prior to
activities that will disturb all other cases, mitigation shall be completed
immediately following disturbance and prior to use or occupancy of the activity
or development. Construction of mitigation projects shall be timed to reduce
impacts to existing wildlife and flora.
The city may authorize a one time
temporary delay, up to one hundred twenty days, in completing minor construction
and landscaping when environmental conditions could produce a high probability
of failure or significant construction difficulties. 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, and 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 mitigation plan. The justification must be verified and
approved by the city, and include a bond in the form approved by the city
attorney.
7. Mitigation Ratios.
a. The following ratios shall apply to
creation or restoration that is in-kind, on-site, the same category, timed prior
to or concurrent with alteration, and has a high probability of success. These
ratios do not apply to remedial actions resulting from unauthorized alterations;
greater ratios shall apply in those cases.
Table 15.02.120-2
|
Regulated Wetland Type
|
Minimum Ratio of Replaced Wetland to Lost Wetland
|
|
Category 1 wetland
|
6 to 1
|
|
Category 2 wetland
|
3 to 1
|
|
Category 3 wetland
|
2 to 1
|
|
Category 4(a) wetland 4(b)
|
1.5 to 1
|
b. The city may increase the ratios under the following
circumstances:
i. Uncertainty exists as to the probable success of the
proposed restoration or creation;
ii. A significant period of time will
elapse between impact and replication of wetland functions;
iii. Proposed
mitigation will result in a lower category wetland or reduced functions relative
to the wetland being impacted; or
iv. The impact was an unauthorized
impact.
c. The city may decrease these ratios under the following
circumstances:
i. Documentation by a qualified wetlands specialist
demonstrates that the proposed mitigation actions have a very high likelihood of
success;
ii. Documentation by a qualified wetlands specialist demonstrates
that the proposed mitigation actions will provide functions and values that are
significantly greater than the wetland being impacted; or
iii. The proposed
mitigation actions are conducted in advance of the impact and have been shown to
be successful.
8. Wetlands Enhancement as Mitigation.
a. Impacts to
wetlands may be mitigated by enhancement of existing significantly degraded
wetlands. Applicants proposing to enhance wetlands must produce a critical area
report that identifies how enhancement will increase the functions of the
degraded wetland and how this increase will adequately mitigate for the loss of
wetland area and function at the impact site. An enhancement proposal must also
show whether existing wetland functions will be reduced by the enhancement
actions.
b. At a minimum, enhancement acreage shall be double the acreage
required for creation or restoration under subsection (H)(7) of this section.
The ratios shall be greater than double the required acreage where the
enhancement proposal would result in minimal gain in the performance of wetland
functions and/or result in the reduction of other wetland functions currently
being provided in the wetland.
9. Impacts to wetlands may be mitigated by
preservation of wetland areas.
a. Preservation as mitigation is acceptable
when done in combination with restoration, creation or enhancement providing
that a minimum of one-to-one acreage replacement is provided by restoration or
creation and the criteria below are met:
i. The impact area is small, and/or
impacts are to a category III or IV wetland;
ii. Preservation of high
quality system occurs in the same Water Resource Inventory Area (WRIA) or
watershed basin as the wetland impact;
iii. Preservation sites include
buffer areas adequate to protect the habitat and its functions from encroachment
and degradation; and
iv. Mitigation ratios for preservation in combination
with other forms of mitigation shall range from ten-to-one to twenty-to-one, as
determined by the city, depending on the quality of the wetlands being mitigated
and the quality of the wetlands being preserved.
b. Preservation of at-risk,
high-quality habitat may be considered as the sole means of mitigation for
wetland impacts when all of the following criteria are met:
i. Preservation
is used as a form of mitigation only after the standard sequencing of mitigation
(avoid, minimize, and then compensate) has been applied;
ii. Creation,
restoration, and enhancement opportunities have also been considered, and
preservation is the best mitigation option;
iii. The impact area is small
and/or impacts are to a category III or IV wetland;
iv. Preservation of a
high quality system occurs in the same Water Resource Inventory Area (WRIA) or a
watershed where the wetland impact occurs;
v. Preservation sites include
buffer areas adequate to protect the habitat and its functions from encroachment
and degradation;
vi. The preservation site is determined to be under
imminent threat, specifically, sites with the potential to experience a high
rate of undesirable ecological change due to on- or off-site activities.
“Potential” includes planned, or likely actions that are not
adequately protected under existing regulations (for example, logging of
forested wetlands); and
vii. The area proposed for preservation is of high
quality and critical for the health of the watershed or basin. Some of the
following features may be indicative of high quality sites:
• Category
I or II wetland rating,
• Rare wetland type (for example, bogs, mature
forested wetlands, estuaries),
• Habitat for threatened or endangered
species,
• Wetland type that is rare in the area,
• Provides
biological and/or hydrological connectivity,
• High regional or
watershed importance (for example, listed as priority site in watershed plan),
and
• Large size with high species diversity (plants and/or animals)
and/or high abundance.
c. Mitigation ratios for preservation as the sole
means of mitigation shall range from ten-to-one to twenty-to-one, as determined
by a qualified wetlands expert, depending on the quality of wetlands being
mitigated and the quality of the wetlands being preserved.
I. Wetland
Delineation. For the purposes of this section, wetland delineations shall be
performed in accordance with the procedures as specified in the Washington State
Wetlands Identification and Delineation Manual, as developed by the Washington
State Department of Ecology, March 1997 and based on “Corps of Engineers
Wetlands Delineation Manual” (1987). (Ord. 1137 § 2 (part),
2004).
15.02.130 Fish and wildlife habitat conservation areas.
A. Designation of Critical Fish and Wildlife Habitat Conservation Areas.
Critical fish and wildlife habitat conservation areas are designated according
to the classifications in the following Table 15.02.130-1:
Table 15.02.130-1
|
Classification
|
Description
|
|
(1) Areas with which state or federal-designated
endangered, threatened, candidate or sensitive species have a primary
association.
|
Areas which, if altered, may reduce the likelihood that
the species will reproduce over the long term. Habitats associated with these
species are those identified by Washington Department of Fish and
Wildlife’s current system for mapping species of concern. These habitats
are designated as critical areas, where endangered, threatened, candidate and
sensitive species are verified to have a primary association. There are no known
state or federally designated endangered, threatened, candidate or sensitive
species in Kalama.
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|
(2) Species and habitats of local importance.
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Habitat: Includes seasonal ranges or habitat elements
with which a given species has a primary association, and which if altered, may
reduce the likelihood that the species will maintain and reproduce over the
long-term. These may be areas of high relative density or species richness,
breeding habitat, winter range, and movement corridors. These may also include
habitats that are of limited availability or high vulnerability to alteration,
such as cliffs, talus and wetlands; and
|
|
Species: Wildlife species which require protective
measures for their continued existence due to their population status or
sensitivity to habitat alterations or are highly valued by the local citizens.
Species meeting the above criteria but not depending upon a habitat of local
importance (as listed above) to meet criteria habitat needs are those
documented, verified, and mapped in Cowlitz County. Kalama’s species of
local importance include the western pond turtle, blacktail deer, bobcat,
raccoon, and bear.
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|
(3) Commercial and recreational shell fish
areas.
|
There is recreational crawfish fishery in
Kalama.
|
|
(4) Kelp and eelgrass beds; herring and smelt spawning
areas.
|
There are no kelp, eelgrass beds, or herring spawning
areas known to occur in Kalama. The Washington State Hydraulic Code guidelines
and information from the Washington State Department of Fish and Wildlife are
used to identify smelt spawning areas.
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|
(5) Naturally occurring ponds under twenty acres and
their submerged aquatic beds that provide fish or wildlife habitat.
|
Naturally occurring ponds are waters with a surface area
of less than 20 acres but greater than one acre and man-made ponds developed as
mitigation as part of a permitting process or mitigation agreement. Naturally
occurring ponds do not include ponds deliberately created such as canals,
detention facilities, wastewater treatment facilities, farm ponds, temporary
construction ponds (of less than three years duration), and landscape amenities.
Kalama has one existing stormwater detention pond of long-term existence which
borders I-5.
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|
(6) Waters of the state.
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Waters of the state shall be those defined in WAC
222-16-030 and 031, Forest Practices Board, and Definitions.
|
|
(7) Lakes, ponds, streams, and rivers planted with game
fish by a governmental or tribal entity.
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Waters of the state which regularly have game fish
introduced. Kalama borders the Columbia River.
|
|
(8) State natural area preserves and natural resource
conservation areas.
|
Currently, there are no known areas in the city of
Kalama.
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|
(9) Unintentionally created ponds.
|
Ponds with a surface area of less than 20 acres, but
greater than one acre. No known ponds of this nature are located in
Kalama.
|
B. Riparian Habitat Areas. Unless otherwise allowed in this title, all
structures and activities shall be located outside of the riparian habitat
areas.
1. Establishment of Riparian Habitat Areas. Riparian habitat areas
shall be established for habitats that include aquatic and terrestrial
ecosystems that mutually benefit each other, and that are located adjacent to
rivers, perennial or intermittent streams, drainage ways, seeps, and
springs.
2. Riparian Habitat Area Widths. Riparian habitat area widths are
shown in the table in KMC Table 15.02.120-2. A riparian habitat area shall have
the width specified unless a greater width is required pursuant in subsection K
or a lesser width is allowed pursuant to subsection L. Widths shall be measured
outward in each direction, on the horizontal plane, from the ordinary high water
mark. Riparian areas should be sufficiently wide to achieve the full range of
riparian and aquatic ecosystem functions, which include but are not limited to
protection of instream fish habitat through control of temperature and
sedimentation in streams; preservation of fish and wildlife habitat; and
connection of riparian wildlife habitat to other habitats.
Table 15.02.130-2
Riparian Habitat
Areas
|
Stream Types
|
Recommended RHA Widths
|
|
Type 1(S) and 2(F) (Shorelines of Statewide
Significance)
|
250 feet
|
|
Type 3(F) (channel >10 feet wide)
|
200 feet
|
|
Type 3(F) (channel < 5 feet wide)
|
150 feet
|
|
Type 4(Np) and 5(Ns) (high mass wasting
potential)
|
225 feet
|
|
Type 4(Np) and 5(Ns) (low mass wasting
potential)
|
150 feet
|
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Type 5(Ns) with no segment of stream classified as a 1,
2, 3 or 4
|
25 feet
|
|
Any stream type that is culverted or buried is not
subject to limits at that site
|
0 feet
|
C. Buffer Widths for Fish and Wildlife Habitat Areas. Buffer widths
that are designed for the protection of the functions of fish and wildlife
habitat will be regulated by Table 15.02.120-2, unless a report is submitted and
accepted by the city of Kalama, prepared by a qualified fish and wildlife
habitat professional, which provides for a different buffer width that will
achieve the same functions and values as the buffer widths set forth in this
section.
D. Development Performance Standards. Regulated development, as
described in Section 15.02.060 of this chapter, shall conform and be governed by
the following items in this subsection, and in subsections C through I of this
section. When impacts to critical fish and wildlife habitat cannot be avoided,
the performance standards contained in this section shall be used to develop
plans submitted for regulated activities. Critical area permits within fish and
wildlife habitat conservation areas may be approved with conditions, approved or
denied based on the following performance standards.
1. Develop a habitat
site plan and design scheme showing the following:
a. Locate buildings and
structures in a manner that preserves the habitat or minimizes adverse
impacts;
b. Consolidate habitat and vegetated open space in contiguous
blocks, and where possible locate habitat contiguous to other habitat, open
space or landscaped areas to contribute to a continuous system or corridor that
provides connections to adjacent habitat areas;
c. Use native species in any
landscaping of disturbed or undeveloped areas and in any enhancement of habitat
or buffers;
d. Emphasize diversity in selection of plant materials and
structure of landscaping;
e. Remove and/or control any noxious, or
undesirable species of plants as identified by the Cowlitz County weed control
board;
f. Demonstrate how existing trees will be preserved, preferably in
groves;
g. Preserve and introduce native plant species which serve as food,
shelter from climatic extremes and predators, and structure and cover for
reproduction and rearing of young for critical wildlife;
h. Preserve the
natural hydraulic and ecological functions of drainage systems;
i. Preserve
critical fish and wildlife habitat areas through maintenance of stable channels,
adequate low flows, management of stormwater runoff, erosion and
sedimentation;
j. Manage access to critical fish and wildlife habitat areas
to protect species which are sensitive to human disturbance;
k. Maintain or
enhance water quality through control of runoff and use of best management
practices.
E. Habitat Management Plan--Classification 1 Only. A habitat
management plan (Appendix D) will be required if the regulated activity is
within a classification 1 habitat area, or identified within one thousand three
hundred feet from an endangered, threatened, candidate or sensitive species
point or habitat locations in classification 1 habitat area.
F. Habitat
Management Plan Requirements.
1. The habitat management plan will be
prepared by a qualified professional. (See Appendix D at the end of this
chapter).
2. Habitat management plans will be sent to the Washington State
Department of Fish and Wildlife and other appropriate state and federal agencies
for comment with the SEPA checklist.
G. Habitat Protection for
Classification 2. (Table 15.02.130-1) Protection for these habitat areas shall
be through the development performance standards in this section in coordination
with the Washington State Department of Fish and Wildlife.
H. Habitat
Protection for Classifications 3 and 4. (Table 15.02.130-1) Protection of these
areas shall be coordinated with the Washington State Department of Fish and
Wildlife.
I. Habitat Protection for Classifications 5, 6, 7 and 9. (Table
15.02.130-1) These classifications shall require protective buffers or riparian
habitat areas as shown on Table 15.02.120-2 of this chapter. Activities within
these areas and buffers will require a critical areas permit. Within
classification 6--types 1, 2, 3, 4, and 5 waters shall also be protected as
defined in WACs 222-16-030 and 031, Forest Practices Board,
Definitions.
J. Habitat Protection for Classification 8. Protection for
state natural area preserves and natural resource conservation area habitat is
achieved by the Washington State Department of Natural Resources.
K. Habitat
Protection for Classification 9. Protection for habitat provided by
unintentionally created ponds shall be through the performance standards in this
section.
L. Increased Riparian Habitat Area Widths. The recommended riparian
habitat area widths shall be increased, as follows:
1. When the
environmental review determines that the recommended width is insufficient to
prevent habitat degradation and to protect the structure and functions of the
habitat area;
2. When the frequently flooded area exceeds the recommended
riparian habitat area width, the riparian habitat area shall extend to the outer
edge of the frequently flooded area;
3. When the channel migration zone
exceeds the recommended riparian habitat area width, the riparian habitat area
shall extend to the outer edge of the channel migration zone;
4. When the
habitat area is in an area of high blowdown potential, the riparian habitat area
shall be expanded an additional fifty feet on the windward side; and
5. When
the habitat area is with an erosion or landslided hazard area, or buffer, the
riparian habitat area shall be the recommended distance, or the erosion or
landslide hazard area or buffer, whichever is greater.
M. Riparian Habitat
Area Width Averaging. The city may allow the recommended riparian habitat area
width to be reduced in accordance with critical area report prepared by a
qualified professional only if:
1. The width reduction will not reduce
stream or habitat functions, including those of nonfish habitat;
2. The
width reduction will not degrade the habitat, including habitat for anadromous
fish;
3. The proposal will provide additional habitat protection;
4. The
total area contained in the riparian habitat area of each stream on the
development proposal site is not decreased;
5. The recommended riparian
habitat area width is not reduced by more than twenty-five percent in any one
location;
6. The width reduction will not be located within another critical
area or associated buffer; and
7. The reduced riparian habitat area width is
supported by best available science.
N. Riparian Habitat Mitigation.
Mitigation of adverse impacts to riparian habitat areas shall result in
equivalent functions and values on a per function basis, be located as near the
alteration as feasible, and be located in the same sub-drainage basin as the
habitat impacted. (Ord. 1137 § 2 (part), 2004).
15.02.140 Frequently flooded critical areas.
A. Frequently Flooded Area Classifications and Designation. All lands
identified in the Federal Emergency Management Agency (FEMA) Flood Insurance
Rate Maps, as amended, and approved by the city, as within the one hundred-year
floodplain are designated as frequently flooded areas. These maps are based on
the following:
1. Flood Insurance Study--City of Kalama.
B. Development
Limitations. All development within designated frequently flooded areas shall
comply with the city of Kalama’s floodplain management ordinance, Chapter
14.16, as now or hereafter amended. (Ord. 1137 § 2 (part), 2004).
15.02.150 Geologic hazard areas.
A. Geologically hazardous areas are those areas susceptible to erosion,
sliding, earthquake, or other geological events that pose a threat to the health
and safety of citizens when incompatible development is sited in areas of
significant hazard. Areas susceptible to one or more of the following types of
hazards shall be designated as a geologically hazardous area:
1. Erosion
hazard;
2. Landslide hazard;
3. Seismic hazard;
4. Mine
hazard;
5. Other geological events.
B. Classifications of Geologically
Hazard Areas. Geologic hazard areas fall within two
classifications:
1. Areas of Geological Concern. Slopes between fifteen
percent to thirty percent or areas where there is documentation that geological
hazard exists.
2. Areas of Potential Geological Hazard. Slopes greater than
thirty percent, or areas where no documentation exists as to the presence or
absence of a geological hazard.
C. Additional Requirements for Geologically
Hazardous Areas.
1. A critical areas report for a geologically hazardous
area shall be prepared by a qualified engineer or geologist, licensed in the
state of Washington, with experience analyzing geologic, hydrologic, and ground
water flow and has experience preparing reports for the relevant type of
hazard.
D. Designations of Specific Hazard Areas.
1. Areas of Historic
Failure.
a. Areas of historic failure, such as areas designated as
quaternary slumps, earthflows, mudflows or landslides; or
b. Area with any
of the following:
i. Slope greater than fifteen percent,
ii. Steep
hillsides intersecting geologic contacts with a relatively permeable sediment
overlying a relatively impermeable sediment or bedrock,
iii. Springs or
ground water seepage,
iv. Slopes that are parallel or sub-parallel to planes
of weakness; such as bedding planes, joint systems, and fault planes,
and
v. Slopes having gradients greater than eighty percent and subject to
rockfall during seismic shaking;
c. Areas potentially unstable as a result
of rapid stream incision, stream bank erosion, and undercutting by wave
action;
d. Areas located in a canyon, on an active alluvial fan, or that are
presently subject to inundation by debris flows or catastrophic
flooding;
e. Areas identified as being unstable or very unstable on
Department of Natural Resources soils based stability maps. (Washington State
Department of Natural Resources);
f. Steep slopes that are greater than
thirty percent and higher than ten feet;
g. Areas that include soil creep
which is a gradual movement of soil in response to gravity and weather. Severe
soil creep can be an indicator of future landslide activity.
2. Erosion
Hazard. Erosion hazard areas are those areas identified by the presence of soils
which are recognized as having a severe erosion hazard by the U.S. Department of
Agriculture Soil Conservation Service, Cowlitz Area, Washington.
3. Seismic
Hazard Areas. For the purposes of this classification, a seismic hazard area is
any area indicated by a zone 2B or higher rating as defined by the Seismic Risk
Map of the United States, adopted by the Washington State Legislature and
defined in the Uniform Building Code (UBC).
4. Mine Hazard Areas. For the
purposes of this classification, mine hazard areas are:
a. Abandoned mines,
shafts, tunnels and/or workings where locations are known;
b. Abandoned
mines, shafts, tunnels and/or workings where exact locations are unknown, but
based upon the best available information that there is good cause to believe it
is within an area which may be reasonably delineated;
c. Abandoned powder
magazines or bunkers.
E. Development Standards.
1. Development Standards
for Landslide Hazard and Erosion Hazard Designations. Any area identified as
potential geological hazard for landslides and erosion will require further
studies and methods of mitigation prior to any consideration of development in
the area. Any allowed or regulated activity on areas identified as landslide or
erosion hazards or their buffers shall conform to the following
standards:
a. Grading. The city has adopted Chapter 33 of the Appendix to
the 1997 Uniform Building Code, Excavation and Grading. The applicable section
in the latest version of the Building Code adopted by the city applies unless
the activity is exempted, an excavation and grading permit is
required.
i. Clearing, grading and other construction activities shall not
aggravate or result in slope instability or surface sloughing.
ii. Slope
disturbance shall be minimized. Clearing, grading or filling of sloped areas
containing landslide or erosion hazard areas shall be limited to the period
between April 1st and October 1st, unless the applicant provides an erosion
control plan (approved by the city) that specifically identifies methods of
erosion control for wet-weather conditions.
iii. All authorized clearing for
roads and utilities shall be limited to the minimum necessary to construct the
engineered design.
iv. Undergrowth and vegetation shall be retained to the
maximum extent feasible.
v. No dead vegetation or other foreign material
shall be placed within landslide or erosion hazard areas, other than approved
for bank stabilization or if such grading is consistent with authorized
activities specified in a geological report.
b. Erosion Control. Compliance
with Kalama Municipal Code Chapter 14.18, Erosion Control, is required and
includes the use of best management practices (BMP).
i. Disturbance of trees
and vegetation shall be minimized to reduce erosion and maintain existing
stability of hazard areas.
ii. Vegetation removal on the slopes of waterways
between the ordinary high-water mark and the top of the banks shall be minimized
because of the potential for erosion.
iii. Vegetation and organic soil
material shall be removed from fill sites prior to the placement of
fill.
iv. Thinning of limbs of individual trees is preferred over tree
removal as a means to provide view corridors.
v. Vegetative cover or
engineered ground covers shall be placed on any disturbed surface to the extent
feasible.
vi. Drainage. Surface drainage, including downspouts, shall not be
directed across the face of a hazard area. If drainage must be discharged from
the top of a hazard area to its toe, it shall be collected above the top and
directed to the toe by tight line drain. An energy-dissipating device at the toe
for discharge to a swale or other acceptable natural drainage
areas.
vii. Stormwater retention and detention systems, including
percolation systems utilizing buried pipe, are prohibited unless a geological
report determines slope stability shall not be affected. The systems shall be
designed by a qualified professional. The qualified professional shall also
certify that the systems are installed as designed.
viii. The proposed
project will not increase the rate of surface water discharge or sedimentation
and will not decrease the adjacent property slope stability.
ix. Setbacks. A
hazardous area setback is required from the top, toe and along all sides of any
existing landslide or erosion hazard areas, as determined in the geological
report.
(A) Based on the results of the geological report, the city may
increase or decrease the setback as indicated.
(B) The setback shall be
clearly staked before and during any construction or clearing.
x. Sanitary
Sewage Lines. For the purpose of landslide or erosion control, the sanitary
sewage lines shall be located outside of the hazard area buffer, unless
otherwise justified by a qualified professional and approved by the city. The
placement of all sanitary sewage lines must be in compliance with all local
government health regulations.
xi. Design Guidelines.
(A) Structures
should be clustered where possible to reduce disturbance and removal of
vegetation.
(B) Foundations shall be stepped to the contours of the slope to
the extent possible.
(C) Roads, walkways and parking areas should be
designed to parallel the natural contours of the site.
(D) Development
proposals shall be designed to minimize the impacts of the project resulting in
the least disturbance to the adjacent affected areas.
2. Development
Standards--Seismic Hazard Areas. All development within areas that meet the
classification for seismic hazard areas shall comply with the latest version of
the building code adopted by the city.
3. Development Standards--Mine Hazard
Areas. Development adjacent to a mine hazard is prohibited unless the applicant
can demonstrate the development will be safe. If a proposal is located adjacent
to a mine hazard area, a geological report may be required.
4. Maps that
illustrate critical areas include, but are not limited to:
a. Soil
Conservation Service, Cowlitz Area Soil Survey, February, 1974;
b. Geologic
hazard map developed by Cowlitz-Wahkiakum Council of Governments,
1993;
c. Federal insurance rate maps for Cowlitz County, FEMA
1993-1994;
d. Washington Department of Natural Resources, Soils Based Slope
Stability Map. (Ord. 1137 § 2 (part), 2004).
15.02.160 Critical aquifer recharge areas.
A. Classification--Critical Aquifer Recharge Areas. For the purposes of
this classification, the critical aquifer recharge areas are determined by the
combined effects of soil types and hydrogeology. (Critical Aquifer Recharge Map,
Cowlitz-Wahkiakum Council of Governments, 1993).
1. Classification 1. High
susceptibility areas, identified on the aquifer recharge map, with a very high
susceptibility to contamination of the underlying aquifer due to high soil
permeability and high water table.
B. Regulated Activities--Classification
1. The following activities are regulated or prohibited in classification 1,
critical aquifer recharge areas:
1. Solid Waste Disposal Facilities,
Junkyards, etc. Landfills, junkyards, salvage yards, auto wrecking yards, and
other solid waste disposal facilities, except those for the disposal of brush
and stumps, sawdust, and inert construction debris.
2. Aboveground and
Underground Storage Tanks and Vaults. Aboveground or underground storage tanks
or vaults for the storage of hazardous substances or dangerous wastes as defined
in WAC 173-303, Dangerous Waste Regulations, or any other substances, solids or
liquids in quantities identified by the county health department, consistent
with WAC 173-303, as a risk to groundwater quality, shall conform to the
city’s adopted Fire Code and WAC 173-360, Underground Storage Tank
Regulations.
3. Utility Transmission Facilities. Utility facilities which
carry liquid petroleum products or any other hazardous substance as defined in
WAC 173-303.
4. Land Divisions. Subdivisions, short subdivisions and other
divisions of land will be evaluated for their impact on ground water quality
within the classification 1 aquifer recharge areas. The following measures may
be required:
a. An analysis of the potential contaminate
loading;
b. Alternative site designs, phased development and/or ground water
quality monitoring;
c. Open spaces within development
proposals.
C. Hydrogeologic Testing and Site
Evaluation.
1. Hydrogeologic testing and site evaluation may be required for
any regulated activity. If federal or state regulations require hydrogeologic
testing, the city may waive the requirement for additional testing provided the
staff has adequate factual information to evaluate the proposal.
2. If
hydrogeologic testing and site evaluation are required, they shall be conducted
by a qualified professional and must include but are not limited to the
requirements in Appendix E, at the end of this chapter.
3. Development which
negatively impacts the quality of any classification 1, critical aquifer
recharge area shall be prohibited unless the hydrogeologic testing and site
evaluation satisfactorily demonstrate that adverse impacts will be mitigated.
(Ord. 1137 § 2 (part), 2004).
15.02.170 Mitigation plan performance standards.
A. Mitigation Planning Requirements. All critical areas mitigation
projects required pursuant to this chapter either as a permit condition or as
the result of an enforcement action shall follow a mitigation plan prepared by
or on behalf of the applicant and approved by the city council (Refer to Section
15.02.120(I) of this chapter for Wetland Mitigation Standards.)
B. When a
mitigation plan is required, the planning commission shall hold a public
hearing. Prior to the public hearing, resource agencies shall be notified of the
mitigation plan and any comments shall be considered by the planning commission
during the public hearing. The city council shall make the final decision on the
mitigation plan, which shall be based on satisfaction of the following
standards:
1. The mitigation plan shall be prepared by an applicant or
qualified professional.
2. The mitigation plan shall include:
a. An
assessment of the existing function and values of the critical area;
b. The
functions and values that will be lost;
c. The critical area’s
expected functions and values after mitigation.
3. Objectives shall be
stated in measurable terms, if feasible.
4. The mitigation plan shall
specify and describe how functions and values will be replaced.
5. The
mitigation plan shall include provisions for monitoring the mitigation area as
reasonably necessary to determine whether stated objectives have been
accomplished. A contingency plan shall be included in the event the stated
objectives are not accomplished.
6. Mitigation shall be provided on-site,
except where on-site mitigation is not scientifically feasible, economical or
practical due to physical features of the property. The burden of proof shall be
on the applicant to demonstrate that mitigation cannot be provided
on-site.
7. When mitigation cannot be provided on-site, mitigation shall be
provided in the immediate vicinity of the permitted activity on property owned
or controlled by the applicant where such mitigation is practical and beneficial
to the critical area and associated resources. Where possible, this means within
the same hydrologic unit as the location of the proposed
project.
C. Restoration shall be required when a critical area has been
altered by the landowner after the adoption of the critical areas ordinance and
prior to project approval or when a critical area is temporarily affected by
construction or any other temporary phase of a project. (Ord. 1137 § 2
(part), 2004).
15.02.180 Reasonable use exception.
If an applicant asserts that the application of this chapter would deny
him reasonable use of his property, the applicant may apply for a reasonable use
exception. A reasonable use exception is intended to address those cases in
which the application of this chapter unreasonably restricts all economic use of
parcel of land and the restriction cannot be remedied by other authorized
techniques or conditions.
A. Only the city council is authorized to issue
reasonable use exceptions under this code. A request for a reasonable use
exception shall be made on forms provided by the city clerk-treasurer and shall
contain the following information:
1. That the application of this chapter
to the subject property will deny all reasonable economically viable use of the
subject property otherwise allowed by applicable law;
2. That because of
special circumstances applicable to the subject property including size, shape,
topography and location, the application of this chapter would result in
unwarranted hardship;
3. That a strict application of this chapter will
deprive the land owner of rights commonly enjoyed by other properties in similar
areas with the critical area or buffer;
4. That the granting of a reasonable
use exception will not confer upon a land owner a special privilege that would
be denied by the terms of this chapter to other lands or structures with a
critical area or buffer that are of a similar nature or
circumstance;
5. That as a result of the proposed development varying from
the terms of this chapter there will be no threat to the public health, safety
or welfare on or off the subject property;
6. That the request is not based
upon conditions or circumstances which are the result of actions by the current
or previous land owners or that the request arises from any condition related to
land or building use, either permitted or nonconforming, on any neighboring
property. Such conditions or circumstances include:
a. Prior subdivision or
segregation of the subject property, or changes to the boundaries of the subject
property through a boundary line adjustment or otherwise,
b. Prior actions
taken in violation of this chapter or any local, state or federal law or
regulation, or
c. Natural constraints of the subject property that would
otherwise preclude the proposed development activities;
7. Before an
application for a reasonable use exception is acted upon, a review of the
application, for completeness and clarity shall be conducted by the city planner
and the finding shall be forwarded to the city council;
B. Any reasonable
use exception granted shall be for the least intrusion into the critical area or
buffer necessary to allow an economically viable use of the subject
property;
C. That any authorized alteration of a critical area or buffer
under this section shall be subject to conditions established by the city
council in accordance with this chapter, and may require mitigation under an
approved mitigation plan; and
D. A reasonable use exception application may
accompany an application for development permit, along with any applicable fees.
(Ord. 1137 § 2 (part), 2004).
15.02.190 Appeals.
An appeal of an administrative critical area determination or the
administrative decision on a critical area permit may be made before the hearing
examiner of the city per KMC Chapter 2.34. An appeal of any city council
decision on a critical area permit, mitigation plan or reasonable use exception
may be made to the Superior Court of Cowlitz County pursuant to state law. (Ord.
1137 § 2 (part), 2004).
15.02.200 Enforcement.
This chapter will be enforced as set forth in KMC Chapter 17.10. (Ord.
1137 § 2 (part), 2004).
15.02.210 Fees.
Fees for administering the provisions of this chapter shall be as set by
resolution of the city council. These fees are in addition to any other
applicable application fees. Actual costs include but are not limited to,
copies, postage, publication costs, city planner fees, and any outside
consultant fees. (Ord. 1137 § 2 (part), 2004).
15.02.220 Liability for damages.
This chapter shall not be construed to hold the Kalama city council, or
any officer or employee thereof, responsible for any damages to persons or
property by reason of the certification, inspection or noninspection of any
building, equipment or property as herein authorized. The purpose of this code
is not to create or otherwise establish or designate any particular class or
group of persons who will or should be especially protected or benefited by the
terms of this code. (Ord. 1137 § 2 (part), 2004).
15.02.230 Review.
The effects and operations of this chapter shall be reviewed by the Kalama
planning commission twelve months after the date of adoption. Subsequent reviews
will be completed as necessary by the planning commission. The planning
commission shall make recommendations for changes and amendments it deems
necessary to the Kalama city council. (Ord. 1137 § 2 (part),
2004).
15.02.240 Adoption by reference.
Pursuant to RCW 35A.12.140, one copy of RCW 64.04.130; RCW 84.34.020(2);
and RCW 76.09; and one copy of WAC 173.303; WAC 173.360; WAC 222; WAC
232-12-011; and WAC 365-195-900 are hereby adopted by reference, these statutes
are on file with the Kalama city clerk-treasurer for use and examination by the
public. (Ord. 1137 § 2 (part), 2004).
align="center">APPENDIX A
Critical Area Permits. If the critical area determination
reveals that there is a critical area(s) on or adjacent to the property subject
to the underlying land use or development permit, an application for a critical
area permit must be submitted. No development or activity may take place on the
property within or adjacent to the critical areas except in conformance with
this chapter and an issued critical areas permit.
A complete application for
a critical area permit shall consist of the following:
1. A Detailed Site
Plan Drawn to Scale. The site plan should clearly show the following
information:
a. North arrow,
b. Property boundary line and
dimensions,
c. Location and dimensions of all existing and proposed
development or alternations, including public and private roads, sewer and water
lines, wells, utilities, easements, water sources, lakes and springs, drainage
facilities, on-site sewage disposal and drainfield areas, within the property
boundary,
d. All critical areas, buffers and the development proposal with
dimensions,
e. Limits of any areas to be cleared;
2. A copy of the
determination of critical area issued by the city showing it having been
recorded through the county auditor’s office;
3. A stormwater
management plan for the project with consideration of the drainage impacts based
on “best management practices”;
4. Critical area report(s)
addressing the specific critical area(s) on the site including all information
as defined in the applicable Appendix(s) B through E. This report must also
include the following:
a. The date the report was prepared,
b. The
names, and qualifications of all person(s) preparing the report,
c. The
professional stamp of the person(s) preparing the report,
d. The dates and
documentation of any fieldwork preformed on the site,
e. A statement
verifying the accuracy of the report, as well as all assumptions relied upon in
the report,
f. An assessment of the probable cumulative impacts to critical
areas resulting from development of the site,
g. Analysis of site
development alternatives,
h. A SEPA environmental checklist if the site is
located within any of the following:
i. Geologic hazard
area,
ii. Wetlands,
iii. Riparian habitat area;
5. A permit
fee.
align="center">APPENDIX B
Geological Hazard Area Reports. All areas found to contain or
adjoin a geologically hazardous area as set forth in Section 15.02.150 of this
chapter shall submit a critical areas report prepared by a qualified
professional that contains an assessment of the geological hazards. All items
requested must be addressed in the report. If an item is not applicable to an
application then indicate NA and why it is not applicable. The reports shall
include all of the following:
Part 1--For all applications.
1. The
applicant must submit all information required by KMC 15.02.090 (Appendix
A);
2. A description of the surface and subsurface geology, hydrology,
soils, and vegetation found in the project area and in all hazard areas within
two hundred feet of the project sited shall be addressed in the
report;
3. Erosion vulnerability of site;
4. A site plan of the area
delineating the following:
a. The type and extent of the geologic hazard
areas, and any other critical areas and buffers on, adjacent to, within two
hundred feet of or that are likely to impact the proposal,
b. Proposed
development, including the location of existing and proposed structures, fill,
storage of materials, and drainage facilities, with dimensions indicating
distances to the floodplain,
c. Clearing limits,
d. An overview of the
existing channel or drainage way characteristics and stream hydraulics at the
subject property;
5. An assessment of the probability for storm-induced
erosion to occur along the drainage way on the subject property and the
estimated extent of the property that would be affected;
6. A recommendation
for the minimum no-disturbance buffer and minimum building setback from any
geological hazard based upon the geological analysis.
Part 2--For all
applications involving large multiple lot developments such as subdivisions,
small lot developments, planned unit developments, manufactured home parks,
apartments or condominiums, or large commercial or industrial developments as
well as any application for property located within or adjacent to a known
geological hazard area. Additional information required:
1. Topographic
data--contour map of proposed site at a scale of 1”:200’, that
clearly delineates the slopes between fifteen and twenty-nine percent and thirty
percent and greater, including figures for area coverage of each slope category
on the site;
2. Subsurface data--boring logs and exploratory methods, soil
and rock stratigraphy, ground water levels including seasonal
changes;
3. Site history--description of any prior grading, soil instability
or slope failure;
4. Seismic hazard--data concerning the vulnerability of
the site to seismic events;
5. Slope stability studies and opinion of slope
stability;
6. Proposed angles of cut and fill slopes and site grading
requirements;
7. Structural foundation requirements and estimated foundation
settlements;
8. Soil compaction criteria;
9. Proposed surface and
subsurface drainage;
10. A cross-section map, drawn to scale and at
five-foot contour intervals, from the edge of the stream or drainage way or
river’s surface to the furthest landward boundary of the property, and
including the proposed development;
11. Lateral earth
pressures;
12. Suitability for fill;
13. Laboratory data and soil index
properties for soil samples;
14. Building limitations; and
15. Site
evaluation: evaluation of the ability of the site to accommodate the proposed
activity. Where a valid geological report has been prepared within the last five
years for a specific site, and where the proposed activity and surrounding site
conditions are unchanged, such report may be referenced in a new
report.
align="center">APPENDIX C
Wetland Report. All areas found to contain or adjoin a wetland
as set forth in Section 15.02.120 of this chapter shall submit a critical areas
report prepared by a qualified professional. All items required by the report
must be addressed in the report. If an item is not applicable to an application
then indicate NA and why it is not applicable. The report shall include all of
the following:
1. The applicant must submit all information required by KMC
15.02.090 (Appendix A);
2. An on-site wetland delineation performed by a
qualified professional as defined in Section 15.02.050. The wetland boundaries
shall be staked and flagged. The recommended wetland buffer shall be staked and
flagged with different colored flags than those used for the wetland
delineation;
3. In addition to the requirements of Appendix A the site plan
shall include the following:
a. Wetland boundaries based upon a wetland
professional’s delineation and depicting sample points and differing
wetland types if any,
b. Recommended wetland buffer
boundary,
c. Internal property lines such as rights-of-way, easements,
etc.,
d. Topographical variations;
4. The final report must include each
of the following:
a. Site characteristics including topography, total
acreage, delineated wetland acreage, other water bodies, vegetation, soil types,
etc., and distances to and sizes of other off-site wetlands and water bodies
within one-quarter mile of the subject wetland,
b. Identification of the
wetland’s classification as defined in this Chapter 15.02, including the
rationale for selecting the wetland category,
c. Analysis of functional
values of existing wetlands, including flood control, water quality, aquifer
recharge, fish and wildlife habitat, and hydrologic characteristics,
d. A
complete description of the proposed project and its potential impacts to the
wetland and, if applicable, adjacent off-site wetlands, including construction
impacts,
e. Discussion of project alternatives including total avoidance of
impacts to wetland areas,
f. If mitigation for wetland impacts is proposed,
a description and analysis of that mitigation,
g. A wetland buffer
recommendation and rationale for the buffer size determination and activities
that could be and should not be allowed within the buffer zone.
align="center">APPENDIX D
Habitat Management Report Requirements. All areas found to
contain or adjoin a habitat conservation area as set forth in Section 15.02.130
of this chapter shall submit a critical areas report prepared by a qualified
professional. All items required by the report must be addressed in the report.
If an item is not applicable to an application then indicate NA and why it is
not applicable. The report shall include all of the