In addition to all other Rules, the following
requirements shall apply in any watershed with listed anadromous salmonids.
Requirements of
14 CCR
§
936.9 precede other sections of the
FPRs.
Geographic scope -- Requirements for Watersheds with
Listed Anadromous Salmonids differ depending on the geographic location of the
watershed and geomorphic characteristics of the Watercourse. Unique
requirements for Watersheds with Listed Anadromous Salmonids are set forth for
1) Watercourses in the coastal anadromy zone with Confined Channels, 2)
Watercourses with Flood Prone Areas or Channel Migration Zones, and 3)
Watercourses with Confined Channels located outside the coastal anadromy
zone.
Watersheds which do not meet the definition of
"Watersheds with Listed Anadromous Salmonids" are not subject to this section
except as follows: The provisions of
14 CCR
§
936.9, subsections (k)-(q) also apply
to Planning Watersheds immediately upstream of, and contiguous to, any
watershed with listed anadromous salmonids for purposes of reducing significant
adverse impacts from transported fine sediment. Projects in other watersheds
further upstream that flow into Watersheds with Listed Anadromous Salmonids,
not otherwise designated above, may be subject to these provisions based on an
assessment consistent with Cumulative Impacts assessment requirements in
14 CCR
§§
898 and
932.9 and Board Technical Rule
Addendum No. 2, Cumulative Impacts Assessment. These requirements do not apply
to upstream watersheds where permanent dams attenuate the transport of fine
sediment to downstream Watercourses with listed anadromous salmonids.
(a) Goal -- Every timber operation shall be
planned and conducted to protect, maintain, and contribute to restoration of
Properly Functioning Salmonid Habitat and listed salmonid Species. To achieve
this goal, every timber operation shall be planned and conducted to:
(1) Comply with the terms of a Total Maximum
Daily Load (TMDL).
(2) Prevent
significant sediment load increase to a Watercourse system or Lake.
(3) Prevent significant instability of a
Watercourse channel or of a Watercourse or Lake bank.
(4) Prevent significant blockage of any
aquatic migratory routes for any life stage of anadromous salmonids or Listed
Species.
(5) Prevent significant
adverse Effects to streamflow.
(6)
Consistent with the requirements of
14 CCR
§
936.9, subsections (f), (g), (h) and
(v), protect, maintain, and restore trees (especially conifers), Snags, or
downed large Woody debris that currently, or may in the foreseeable future,
provide large Woody debris recruitment needed for instream habitat structure
and Fluvial geomorphic functions.
(7) Consistent with the requirements of
14 CCR
§
936.9, subsections (f), (g), (h) and
(v), protect, maintain, and restore the quality and quantity of vegetative
Canopy needed to:
(A) provide shade to the
Watercourse or Lake to maintain daily and seasonal water temperatures within
the preferred range for anadromous salmonids or Listed Species where they are
present or could be restored; and
(B) provide a deciduous vegetation component
to the Riparian zone for aquatic nutrient inputs.
(8) Prevent significant increases in peak
flows or large flood frequency.
(b) Pre-plan adverse cumulative watershed
Effects -- Pre-plan adverse cumulative watershed Effects on the populations and
habitat of anadromous salmonids shall be considered. The Plan shall
specifically acknowledge or refute that such Effects exist. When the proposed
Timber Operations, in combination with any identified pre-plan watershed
Effects, will add to significant adverse existing cumulative watershed Effects,
the Plan shall set forth measures to effectively reduce such Effects.
(c) Objectives for Timber Operations or
silvicultural prescriptions in WLPZs -- Any timber operation or silvicultural
prescription within any Watercourse or Lake protection zone shall have
protection, maintenance, or restoration of the Beneficial Uses of water, and
Properly Functioning Salmonid Habitat and listed aquatic or Riparian-Associated
Species as significant objectives. Specific objectives are described below.
(1) Core Zone: The primary objective for this
zone is streamside bank protection to promote bank stability, wood recruitment
by bank erosion, and Canopy retention. Timber Operations are generally excluded
from this zone and limited to actions which meet the objectives stated above or
improve salmonid habitat consistent with
14 CCR
§
936.9 subsections (a) and
(c).
(2) Inner Zone: The primary
objective for this zone is to develop a large number of trees for large wood
recruitment, to provide additional shading, to develop vertical structural
diversity, and to provide a variety of Species (including hardwoods) for
nutrient input. This is accomplished through the establishment of high basal
area and Canopy retention by retaining or more rapidly growing a sufficient
number of large trees. Additional specific objectives include locating large
trees retained for wood recruitment nearer to the Core Zone and maintaining or
improving salmonid habitat on Flood Prone Areas and CMZs when present. Timber
Operations within WLPZs are limited to those actions which meet the objectives
stated above or to improve salmonid habitat consistent with
14 CCR
§
936.9 subsection (a) and
(c).
(3) Outer Zone: The primary
objective for this zone is to buffer the Inner and Core Zones and to provide
the following functions:
1) wind resistance
where windthrow is common or likely to occur,
2) additional wood recruitment,
3) microclimate control in the Inner or Core
Zones for purposes other than limiting water temperature change,
4) habitat for terrestrial wildlife Species
that depend on Riparian areas, and
5) an additional sediment filter on steeper
slopes with high or moderate Erosion Hazard Rating when Tractor Operations are
proposed.
(4) Class II
Large Watercourses (Class II-L): The primary objective is to maintain, protect
or restore the values and functions of Class II-L type Watercourses described
below. Class II-L Watercourses can have greater individual Effects on receiving
Class I Watercourse temperature, sediment, nutrient, and lame wood loading than
Class II standard (Class II-S) Watercourses due to larger channel size, greater
magnitude and duration of flow, and overall increased transport capacity for
watershed products. Other objectives stated in
14 CCR
§
936.9 subsections (c)(1) and (2) above
for the Core Zone and Inner Zone are also desired objectives for Class II-L
type Watercourses.
(5) A primary
objective for all WLPZs is to implement practices to maintain, protect and
contribute to restoration of Properly Functioning Salmonid Habitat and repair
conditions detrimental to the Species or Species habitat. Practices to meet
this objective include, but are not limited to, thinning for increased conifer
growth; felling or Yarding trees for wood placement in the channel; restoration
of conifer deficient areas; management to promote a mix of conifers and
hardwoods; Abandonment and upgrading of non-functioning or high risk roads,
Watercourse crossings, Tractor Roads, and Landings; and fuel hazard reduction
activities that will reduce fire hazards and stand replacing wildfires which
would result in significant adverse Effects to salmonid Species or Riparian
habitat.
(d) Measures to
Offset Adverse Watershed Effects --
(1) The
Plan shall fully describe:
(A) the type and
location of each measure needed to fully offset sediment loading, thermal
loading, and potential significant adverse watershed Effects from the proposed
Timber Operations, and
(B) the
Person(s) responsible for the implementation of each measure, if other than the
Timber Operator.
(2) In
proposing, reviewing, and approving such measures, preference shall be given to
the following:
(A) measures that are both
onsite (i.e., on or near the Plan area) and in-kind (i.e., erosion control
measures where sediment is the problem), and
(B) sites that are located to maximize the
benefits to the impacted portion of a Watercourse or Lake. Out-of-kind measures
(i.e., improving shade where sediment is the problem) shall not be approved as
meeting the requirements of this subsection.
(e) Channel Zone requirements --
(1) There shall be no Timber Operations
within the Channel Zone with the following exceptions:
(A) Actions directed to improve salmonid
habitat with review and concurrence by CDFW.
(B) Actions necessary for the construction,
reconstruction, removal, or Abandonment of approved Watercourse
crossings.
(C) Actions necessary
for the protection of public health, safety and general welfare. This includes
actions necessary to protect infrastructure facilities including, but not
limited to, roads, bridges, powerlines, utilities, water drafting structures,
homes, and other Approved and Legally Permitted Structures.
(D) Actions to allow for full suspension
Cable Yarding when necessary to transport logs through the Channel
Zone.
(E) Class III Watercourses
consistent with
14 CCR
§
936.9 subsection (h)(7).
(F) Actions reviewed by the RWQCB which seek
to correct or remediate adverse impacts to the Beneficial Uses of
water.
(2) In all
instances where trees are proposed to be felled within the Channel Zone, a base
mark shall be placed below the cut line of the harvest trees within the zone.
Such Marking shall be completed by the RPF that prepared the Plan, or a
Supervised Designee, prior to the preharvest inspection.
(f) Class I Watercourses --
(1) For Class I Watercourses, where fish are
always or seasonally present or where fish habitat is restorable, any Plan
involving Timber Operations within the WLPZ shall contain the following
information:
(A) Clear and enforceable
specifications of Timber Operations within the Class I WLPZ, including a
description of how any disturbance, or log or tree cutting and removal shall be
carried out to conform with
14 CCR
§§
936.2, subsection (a) and 936.9,
subsection (a).
(B) Documentation
of how proposed harvesting in the WLPZ contributes to the objectives of each
zone stated in
14 CCR
§
936.9, subsection (c) and other goals
in
14 CCR
§
936.9, subsection (a)(1)-(8).
Documentation shall include the examinations, analysis, and other requirements
listed in
14 CCR §
936.4, subsection
(a).
(2) Class I
Watercourses with Confined Channels in Watersheds in the Coastal Anadromy Zone:
The following are the minimum requirements for WLPZ delineation and Timber
Operations in Class I WLPZs in Watersheds in the coastal anadromy zone where
Confined Channels are present. WLPZ width ranges from 100-150 feet slope
distance, depending on the Silvicultural System applied above the WLPZ. Three
Zones are established within the WLPZs: The Core Zone is nearest to the water,
the Inner Zone is the middle zone contiguous to the Core Zone, and the Outer
Zone is furthest from the water and contiguous to the Inner Zone. Graphic
depictions of zones and the abbreviated descriptions of the silvicultural
prescriptions and operational requirements are shown in Figure 4. Table 1
specifies the enforceable standards to be used for protection of Class I
Watercourses for the area included in the coastal anadromy zone:
(A) Core Zone: The minimum width of the Core
Zone shall be 30 feet measured from the Watercourse Transition Line or Lake
Transition Line. No Timber Operations are permitted in this zone except for
those listed in
14 CCR
§
936.9, subsection (e)(1) (A)-(F), or
those approved pursuant to
14 CCR
§
936.9, subsection (v).
Sanitation-Salvage is prohibited except as provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
(B) Inner Zone: The minimum
width of the Inner zone shall be 70 feet measured from the landward edge of
Core Zone. Timber Operations are permitted in this zone when conducted to meet
the goals of this section, objectives for the Inner Zone in
14 CCR
§
936.9, subsection (c)(2), pursuant to
14 CCR
§
936.9, subsections (e)(1)(A)-(F), or
pursuant to
14 CCR
§
936.9, subsection (v). Harvesting
prescriptions should focus on practices that use thinning from below.
Silvicultural Systems for harvesting are limited to the use of commercial
thinning or single tree selection modified to meet the following requirements:
1. When commercial thinning is used, the QMD
of conifer trees greater than 8 inches dbh in the preharvest Project area shall
be increased in the postharvest stand.
2. Sanitation-Salvage is prohibited except as
provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
3. Postharvest stand shall
have a minimum 80% Overstory Canopy cover in the Coast and Southern Forest
Districts of the coastal anadromy zone and a minimum 70% Overstory Canopy cover
in the Northern Forest District of the coastal anadromy zone. The postharvest
Canopy may be composed of both conifers and hardwood Species and shall have at
least 25% Overstory conifer Canopy.
4. Postharvest stand shall retain the 13
largest conifer trees (live or dead) on each acre of the area that encompasses
the Core and Inner Zones.
5. Large
trees retained to meet
14 CCR
§
936.9, subsections (f)(2)(B)(1.) and
(3.) above that are the most conducive to recruitment to provide for the
Beneficial Functions of Riparian Zones (e.g., trees that lean towards the
channel, have an unimpeded fall path toward the Watercourse, are in an advanced
state of decay, are located on Unstable Areas or downslope of such an Unstable
Areas, or have undermined roots) are to be given priority to be retained as
future recruitment trees.
(C) Outer Zone: The minimum width of the
Outer Zone shall be 50 feet measured from the landward edge of Inner Zone. This
zone is required where evenaged Regeneration Methods, Seed Tree removal,
shelterwood removal, Alternative Prescriptions declared under
14 CCR
§
933.6, subsection (b)(3) as most
related to any evenaged Silvicultural System, variable retention or
rehabilitation of understocked areas will be utilized contiguous to the
Watercourse and Lake protection zone. Timber Operations are permitted in this
zone when conducted to meet the goals of this section, including those for the
Outer Zone in
14 CCR
§
936.9, subsection (c)(3), and (5),
pursuant to
14 CCR
§
936.9, subsection (e)(1)(A)-(F), or
pursuant to
14 CCR
§
936.9, subsection (v). Silvicultural
Systems for harvesting are limited to the use of commercial thinning or single
tree selection modified to meet the following requirements:
1. Postharvest stand shall have a minimum 50%
Overstory Canopy cover. The postharvest Canopy may be composed of both conifers
and hardwood Species and shall have at least 25% Overstory conifer
Canopy.
2. Priority shall be given
to retain wind firm trees.
(D) Preferred Management Practices in the
Inner and Outer Zones: When Timber Operations are considered pursuant to
14 CCR
§§
936.3, subsection (c) and 936.4,
subsection (d), the following Preferred Management Practices should be
considered for inclusion in the Plan by the RPF and by the Director:
1. Preflagging or Marking of any skid trails
before the preharvest inspection;
2. Heavy equipment should be limited to
slopes less than 35% with low or moderate EHRs;
3. Use feller bunchers or hydraulic heel boom
loaders which do not drag/skid logs through the zone;
4. Minimize turning of heavy equipment which
would result in increased depth of ground surface depressions; and
5. Use mechanized harvesting equipment which
delimb harvested trees on pathway over which heavy equipment would
travel.
(E) Additional
Special Operating Zone: For situations contiguous to the Outer Zone where
evenaged Regeneration Methods, Seed Tree removal step, shelterwood removal
step, Alternative Prescriptions declared under
14 CCR
§
933.6, subsection (b)(3) as most
related to any evenaged Silvicultural System, variable retention or
rehabilitation of understocked areas with the same effect as a clearcut is
used, slopes are greater than 50%, and the Outer Zone is located on any north
aspect, the RPF shall consider the need for a special operating zone for
purposes of shading the Watercourse from direct low angle solar radiation from
beneath the Overstory Canopy that is expected to have a potential significant
adverse impact on water temperature. When the special operating zone is needed,
the special operating zone shall retain Understory and mid-canopy conifers and
hardwoods. These trees shall be protected during falling, Yarding and Site
Preparation to the extent Feasible. Width of the zone shall be 50 feet measured
from the landward edge of the Outer Zone.
Table 1: Procedure for Determining WLPZ Widths and
Protective Measures Class I WLPZs -- Confined Channels -- Coastal Anadromy
Zone
Pursuant to
14 CCR
936.9(f)(2)
|
Zone Designation |
Zone
width |
Overstory Canopy
Cover |
Large
Tree |
Silviculture |
Operational |
|
(ft.) |
|
Retention |
Requirements |
Requirement |
Channel Zone |
Variable |
Retain all trees except per 936.9(e)(1) A-F or
936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or
936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or
936.9(v) |
No timber operations except per 936.9(e)(1)A-F or
936.9(v); |
Core Zone per
936.9(f)(2)(A) |
30 ft. |
Retain all trees
except per 936.9(e)(l)A-F or 936.9(v) |
Retain all trees except per
936.9(e)(1) A-F or 936.9(v) |
Retain all trees except per 936.9(e)(1) A-F
or 936.9(v); no sanitation salvage except 916.9(s)(t) and (u). |
No
timber operations except per 936.9(e)(1) A-F or 936.9(v); |
Inner Zone per
936.9(f)(2)(B) |
70 ft. |
80% Coast and Southern Forest
District of Coastal Anadromy Zone per 936.9(f)(2)(B)3. |
70% in Northern
Forest District of Coastal Anadromy Zone per 936.9(f)(2)(B)3. |
13
largest trees/ac. per 936.9(f)(2)(B)4. |
Increase QMD; No sanitation
salvage except 916.9(s)(t) and (u); commercial thinning or single tree
selection only. |
Preferred Management Practices in 936.9(f)(2)(D) |
Outer Zone per
936.9(f)(2)(C) |
50 ft. |
50% |
NA |
Commercial thinning or single tree selection
only; Retain wind firm trees. |
Preferred Management Practices in
936.9(f)(2)(D) |
|
|
|
|
|
|
Outer Zone applicable only where even-aged
regeneration used adjacent to the WLPZ |
|
per
936.9(f)(2)(C).1. |
|
|
|
Special Operating Zone per
936.9(f)(2)(E) |
50 ft. |
NA |
NA |
SOZ applicable only where even-aged
regeneration used adjacent to the WLPZ. Retain understory and midstory trees
per 936.9(f)(2)(E) |
All other Forest Practice Rules |
Figure 4: Graphic of profile view of Class I WLPZ
with Confined Channels in Watersheds in the Coastal Anadromy Zone (not to
scale)
Click
here to view image
Outer Zone:
50 ft. Outer Zone required only when even-aged
Silvicultural System contiguous to WLPZ
Modified commercial thinning or single tree
selection
50% overstory Canopy (OSC)
Inner Zone:
Modified commercial thinning or single tree
selection
Increase QMD
No Sanitation Salvage
Retain 80% OSC in the Coast and Southern Forest Districts
of the coastal anadromy zone and 70% OSC in the Northern Forest District of the
coastal anadromy zone
Retain 13 largest trees/ac.
(3) Class I Watercourses with Flood Prone
Areas or Channel Migration Zones: The following are the minimum requirements
for WLPZ delineation and Timber Operations in Class I WLPZs in locations where
Flood Prone Areas and/or CMZs are present. WLPZ widths vary depending on the
extent of the Flood Prone Area and Silvicultural System applied contiguous to
the WLPZ.
There are up to 5 zones established within the WLPZ: The
CMZ (when present), the Core Zone is the portion of the Flood Prone Area
nearest the water (and contiguous to the CMZ when present), the Inner Zone A is
contiguous to the Core Zone, the Inner Zone B is contiguous to Inner Zone A and
extends to the landward edge of the Flood Prone Area, and the Outer Zone is
hillslope area and is contiguous to the Inner Zone B and landward perimeter of
the Flood Prone Area. Table 2 specifies the enforceable standards to be used
for protection of Class I Watercourses with Flood Prone Area or Channel
Migration Zones. The zones and the abbreviated descriptions of the
silvicultural prescriptions, and operational requirements are shown in Figure
5.
(A) Channel Migration Zone: When a
CMZ is present, no Timber Operations are permitted in this zone except for
those listed in §
936.9, subsection (e)(1)(A)-(F),
or pursuant to
14 CCR
§
936.9, subsection (v).
(B) Core Zone: The minimum width of the Core
Zone shall be 30 feet measured from the Watercourse Transition Line or Lake
Transition Line. No Timber Operations are permitted in this zone except for
those listed in
14 CCR
§
936.9, subsection (e)(1) (A)-(F), or
those approved pursuant to
14 CCR
§
936.9, subsection (v).
Sanitation-Salvage is prohibited except as provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
(C) Inner Zone A: The Inner
Zone A generally encompasses the portion of the Flood Prone Area from 30 feet
beyond the WTL (Core Zone perimeter) up to 150 feet from the WTL. The minimum
width of the Inner Zone A shall be the greater of the distance from the
landward edge of the Core Zone to the landward edge of the Inner Zone A or 70
feet. The maximum width is 120 feet. Timber Operations are permitted in this
zone when conducted to meet the goals of this section, including those for the
Inner Zone in
14 CCR
§
936.9, subsection (c)(2), pursuant to
14 CCR
§
936.9, subsections (e)(1) (A)-(F) or
pursuant to
14 CCR
§
936.9, subsection (v). Harvesting
prescriptions should focus on practices that use thinning from below.
Silvicultural Systems for harvesting are limited to the use of commercial
thinning or single tree selection modified to meet the following requirements:
1. When commercial thinning is used, the QMD
of conifer trees greater than 8 inches dbh in the preharvest Project area shall
be increased in the postharvest stand.
2. Sanitation-Salvage is prohibited except as
provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
3. Postharvest stand shall
have a minimum 80% Overstory Canopy cover in the Coast and Southern Forest
Districts of the coastal anadromy zone and a minimum 70% Overstory Canopy cover
in all other Watersheds with Listed Anadromous Salmonids. The postharvest
Canopy may be composed of both conifers and hardwood Species and shall have at
least 25% Overstory conifer Canopy.
4. Postharvest stand shall retain the 13
largest conifer trees (live or dead) on each acre of the area that encompasses
the Core and Inner Zones.
5. Large
trees retained to meet
14 CCR
§
936.9, subsections (f)(3)(C)(1.) and
(3.) above that are the most conducive to recruitment to provide for the
Beneficial Functions of Riparian Zones (e.g. trees that lean towards the
channel, have an unimpeded fall path toward the Watercourse, are in an advanced
state of decay, are located on Unstable Areas or downslope of such an Unstable
Areas, or have undermined roots) are to be given priority to be retained as
future recruitment trees.
(D) Inner Zone B: The Inner Zone B is
applicable when there are very wide Flood Prone Area. The Inner Zone B
encompasses the portion of the Flood Prone Area from the landward edge of the
Inner Zone A (i.e.150 feet from the WTL) to the landward edge of the Flood
Prone Area. The landward edge of the Inner Zone B (i.e. the landward perimeter
of the Flood Prone Area) shall be established in accordance with Flood Prone
Area definitions in
14 CCR
§
895.1. Timber Operations are permitted
in this zone when conducted to meet the goals of this section, including those
for the Inner Zone in
14 CCR
§
936.9, subsection (c)(2),
14 CCR
§
936.9, subsection (e)(A)-(F), or
pursuant to
14 CCR
§
936.9, subsection (v). Silvicultural
Systems for harvesting are limited to the use of commercial thinning or single
tree selection modified to meet the following requirements:
1. Postharvest stand shall retain the 13
largest conifer trees (live or dead) on each acre of the area that encompasses
the Core and Inner Zones.
2.
Postharvest stand shall have a minimum 50% Overstory Canopy cover. The
postharvest Canopy may be composed of both conifers and hardwood Species and
shall have at least 25% Overstory conifer Canopy.
(E) Preferred Management Practices in the
Inner Zone A and B of Flood Prone Areas. When Timber Operations are considered
pursuant to
14 CCR
§
936.3, subsection (c) and 936.4,
subsection (d), the following Preferred Management Practices should be
considered for inclusion in the Plan by the RPF and by the Director when Timber
Operations are conducted in the Inner Zones of the Flood Prone Area.
1. Implement actions to improved salmonid
habitat conditions: Implement maintenance and repair actions that contribute to
improving undesired existing conditions and contribute to restoring Properly
Functioning Salmonid Habitat.
2.
Minimize Yarding and Skidding: Skid trails, Yarding corridors, falling
activities, and log Yarding, should not alter the natural drainage or flow
patterns. EEZ of 30 feet should be applied near side channels and areas of
ponding. Very limited, pre-flagged, pre-approved prior to falling skid trails
shall be used and abandoned so as to minimize risk of becoming new secondary
channels by Flood Flows. Minimize or exclude, to the extent Feasible, tractor
Skidding/crossings over, through, or along secondary channels (protection of
overflow channels is a key element). Locate Tractor Roads on high ground areas
to the greatest extent possible. When Feasible, use feller-bunchers which do
not drag/skid logs through the zone, minimize turning of equipment which would
result in increased depth of ground surface depressions, and utilize mechanized
harvesting equipment which delimbs harvested trees on the pathway over which
equipment would travel. Cable Yarding corridors should be located at wide
intervals consistent with practices that use lateral Yarding. Full suspension
should be used when possible.
3.
Minimize Soil Erosion and Prevent Discharge: Design Timber Operations to avoid
turbid runoff by treating any ground disturbance greater than 100 square feet.
Operations shall be conducted only in dry soil conditions. Avoid disturbance of
vegetation not intended for harvest that could increase the likelihood of
erosion or damages the reinforcing root network on the channel banks, including
any secondary overflow channel. Restore any tracks or trails to an original
surface.
4. Avoid Slash
Concentration and Site Preparation: Logging Slash shall not be disposed of or
concentrated in side channels. When Slash is treated within the Flood Prone
Areas, scatter Slash and avoid piling or other Concentrations that may obstruct
flows in side channels. When Feasible, concentrate/mulch Slash in Tractor
Roads. No Mechanical Site Preparation, Broadcast Burning or pile
burning.
5. Delineate Zone on the
Ground: Locations of all WLPZ zones and CMZs shall be designated on the
ground.
6. Avoid Use of Water
Drafting Sites: Water drafting sites shall be located outside Flood Prone Areas
when Feasible (exceptions could include, but are not limited to, drafting from
an existing Watercourse crossing that is appropriately engineered to facilitate
Properly Functioning Salmonid Habitat and those sites designed and permitted
pursuant to a waste discharge or steam alteration permits.
7. Avoid Disturbance to Critical Flood Prone
Area Habitat: Avoid disturbance of abandoned meanders, oxbow Lakes, or other
features that provide off-channel habitat for fish during Flood Flows. Avoid
activities that could increase potential for diversion or avulsion of Stream
flow out of existing channel, including breaching or lowering the elevation of
natural levees. Retain adequate hydraulic roughness provided by trees on the
floodplain surface, thereby slowing flood water velocity on floodplains,
attenuating peak Flood Flows, and allowing sediment to be deposited. Retain
existing deciduous hardwoods preferential to anadromous salmonid Species and
down large Woody debris.
(F) Outer Zone: The width of the Outer Zone
is 50 feet measured from the landward edge of Inner Zone. This zone is required
where evenaged Regeneration Methods, Seed Tree removal, shelterwood removal,
Alternative Prescriptions declared under
14 CCR
§
933.6, subsection (b)(3) as most
related to any evenaged Silvicultural System, variable retention or
rehabilitation of understocked areas will be utilized contiguous to the
Watercourse and Lake protection zone. Timber Operations are permitted in this
zone when conducted to meet the goals of this section, including those for the
Outer Zone in
14 CCR
§
936.9, subsection (c)(3) and (5),
pursuant to
14 CCR
§
936.9 subsection (e)(1) (A)-(F), or
pursuant to
14 CCR
§
936.9, subsection (v). Silvicultural
Systems for harvesting are limited to the use of commercial thinning or single
tree selection modified to meet the following requirements:
1. Postharvest stand shall have a minimum 50%
Overstory Canopy cover. The postharvest Canopy may be composed of both conifers
and hardwood Species and shall have at least 25% Overstory conifer
Canopy.
2. Priority shall be given
to retain wind firm trees.
Table 2: Procedure for Determining WLPZ Widths and
Protective Measures Class I WLPZs -- with Flood Prone Areas or Channel
Migration Zones
Pursuant to
14 CCR
936.9(f)(3)
|
Zone Designation |
Zone
width |
Overstory Canopy
Cover |
Large
Tree |
Silviculture |
Operational |
|
(ft.) |
|
Retention |
Requirements |
Requirement |
Channel Zone or Channel Migration Zone
per 936.9(f)(3)(A) |
Variable |
Retain all trees except
per 936.9(e)(1)A-F or 936.9(v) |
Retain all trees except per
936.9(e)(1)A-F or 936.9(v) |
Retain all trees except per 936.9(e)(1) A-F
or 936.9(v) |
No timber operations except per 936.9(e)(1) A-F or
936.9(v); |
Core Zone per
936.9(f)(3)(B) |
30 ft. |
Retain all trees except per
936.9(e)(1)A-F or 936.9(v) |
Retain all trees except per 936.9(e)(1)A-F
or 936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or 936.9(v); no
sanitation salvage except 916.9 (s)(t) and (u). |
No timber operations
except per 936.9(e)(1)A-F or 936.9(v); |
Inner Zone A per
936.9(f)(3)(C) |
Minimum 70 ft. Maximum 120 ft. |
80% Coast and
Southern Forest District of Coastal Anadromy Zone per
936.9(f)(3)(C)3. |
70% in all other watersheds per
936.9(f)(3)(C)3. |
13 largest trees/ac. per
936.9(f)(3)(C)4. |
Increase QMD; No sanitation salvage except 936.9
(s)(t) and (u); commercial thinning or single tree selection
only. |
Preferred Management Practices in 936.9(f)(3)(E) |
Inner Zone B per
936.9(f)(3)(D) |
Variable: distance from Inner Zone A to end of
FPA. |
50% |
13 largest trees/ac. per
936.9(f)(3)(D)1. |
Increase QMD; No sanitation salvage except 916.9
(s)(t) and (u); commercial thinning or single tree selection
only. |
Preferred Management Practices in 936.9(f)(3)(E) |
Outer Zone per 936.9(f)(3)(F) aged
regeneration used adjacent to the WLPZ |
50 ft. |
50% |
NA |
Commercial thinning or single tree selection
only; Retain wind firm trees. |
Preferred Management Practices in
936.9(f)(3)(E) |
Figure 5: Graphic of Profile View of Class I WLPZ
in Flood Prone Areas and Channel Migration Zones (not to scale)
Click
here to view image
Outer Zone:
50 ft. Outer Zone required only when even aged
Silvicultural System contiguous to WLPZ
Modified commercial thinning or single tree
selection
50% Overstory Canopy (OSC).
Inner Zone B:
Modified commercial thinning or single tree
selection
50% Overstory Canopy (OSC)
Retain 13 largest trees/ac.
Inner Zone A:
Modified commercial thinning or single tree
selection
Increase QMD
No Sanitation Salvage
Retain 80% OSC in the Coast and Southern Forest Districts
of the coastal anadromy zone and 70% OSC in all other watersheds
Retain 13 largest
trees/ac.
(4) Class I Watercourses with Confined
Channels outside Watersheds in the Coastal Anadromy Zone: The following are the
minimum requirements for WLPZ delineation and Timber Operations in Class I
WLPZs in locations outside of Watersheds in the coastal anadromy zone where
Confined Channels are present. WLPZ width is 100 feet slope distance, with an
additional 25 foot ELZ depending on the Silvicultural System applied contiguous
to the WLPZ. Three zones are established within the WLPZs: The Core Zone is
nearest to the water, the Inner Zone is the middle zone contiguous to the Core
Zone, and the Outer Zone is furthest from the water and contiguous to the Inner
Zone. Graphic depiction of zones and the abbreviated descriptions of the
silvicultural prescriptions and operational requirements are shown in Figure 6.
Table 3 specifies the enforceable standards to be used for protection of Class
I Watercourses for the area outside the coastal anadromy zone:
(A) Core Zone: The minimum width of the Core
Zone shall be 30 feet measured from the Watercourse Transition Line or Lake
Transition Line. No Timber Operations are permitted in this zone except for
those listed in
14 CCR
§
936.9, subsection (e)(1)(A)-(F), or
those approved pursuant to
14 CCR
§
936.9, subsection (v).
Sanitation-Salvage is prohibited except as provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
(B) Inner Zone: The minimum
width of the Inner Zone shall be 40 feet measured from the landward edge of
Core Zone. Timber Operations are permitted in this zone when conducted to meet
the goals of this section, including those for the Inner Zone in
14 CCR
§
936.9, subsection (c)(2), pursuant to
14 CCR
§
936.9, subsections (e)(1) (A)-(F) or
pursuant to
14 CCR
§
936.9, subsection (v). Harvesting
prescriptions should focus on practices that use thinning from below.
Silvicultural Systems for harvesting are limited to the use of commercial
thinning or single tree selection modified to meet the following requirements:
1. When commercial thinning is used, the QMD
of conifer trees greater than 8 inches dbh in the preharvest Project area shall
be increased in the postharvest stand.
2. Sanitation-Salvage is prohibited except as
provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
3. Postharvest stand shall
have a minimum 70% Overstory Canopy cover. The postharvest Canopy may be
composed of both conifers and hardwood Species and shall have at least 25%
Overstory conifer Canopy.
4.
Postharvest stand shall retain the 7 largest conifer trees (live or dead) on
each acre of the area that encompasses the Core and Inner Zones.
5. Large trees retained to meet
14 CCR
§
936.9, subsections (f)(4)(B)(1.) and
(3.) above that are the most conducive to recruitment to provide for the
Beneficial Functions of Riparian Zones (e.g., trees that lean towards the
channel, have an unimpeded fall path toward the Watercourse, are in an advanced
state of decay, are located on Unstable Areas or downslope of such an Unstable
Areas, or have undermined roots) are to be given priority to be retained as
future recruitment trees.
(C) Outer Zone: The minimum width of the
Outer Zone shall be 30 feet measured from the landward edge of Inner Zone. When
evenaged Regeneration Methods, Seed Tree removal, shelterwood removal,
Alternative Prescriptions declared under
14 CCR
§
933.6, subsection (b)(3) as most
related to any evenaged Silvicultural System, variable retention, or
rehabilitation will be utilized contiguous to Watercourse and Lake protection
zones, an additional 25 foot ELZ is required contiguous to the Outer Zone.
Timber Operations are permitted in the Outer Zone when
conducted to meet the goals of this section, including those for the Outer Zone
in 14 CCR
§
936.9, subsection (c)(3) and (5)
pursuant to
14 CCR
§
936.9, subsection (e)(1) (A)-(F), or
pursuant to
14 CCR
§
936.9, subsection (v). Silvicultural
Systems for harvesting are limited to the use of commercial thinning or single
tree selection modified to meet the following requirements:
1. Postharvest stand shall have a minimum 50%
Overstory Canopy cover. The postharvest Canopy may be composed of both conifers
and hardwood Species and shall have at least 25% Overstory conifer
Canopy.
2. Priority shall be given
to retain wind firm trees.
(D) Preferred Management Practices in the
Inner and Outer Zone: When Timber Operations are considered pursuant to
14 CCR
§§
936.3, subsection (c) and 916.4,
subsection (d), the following Preferred Management Practices should be
considered for inclusion in the Plan by the RPF and by the Director:
1. Preflagging or Marking of any skid trails
before the preharvest inspection;
2. Heavy equipment should be limited to
slopes less than 35% with low or moderate EHRs;
3. Use feller bunchers or hydraulic heel boom
loaders which do not drag/skid logs through the zone;
4. Minimize turning of heavy equipment which
would result in increased depth of ground surface depressions; and
5. Use mechanized harvesting equipment which
delimb harvested trees on pathway over which heavy equipment would travel.
Table 3: Procedure for Determining WLPZ Widths and
Protective Measures Class I WLPZs -- Confined Channels -- Outside the Coastal
Anadromy Zone
Pursuant to
14 CCR
936.9(f)(4)
|
Zone Designation |
Zone
width |
Overstory Canopy Cover |
Large
Tree |
Silviculture |
Operational |
|
(ft.) |
|
Retention |
Requirements |
Requirements |
Channel
Zone |
Variable |
Retain all trees except per 936.9(e)(1)
A-F or 936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or
936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or
936.9(v) |
No timber operations except per 936.9(e)(1) A-F or
936.9(v); |
Core Zone per
936.9(f)(4)(A) |
30 ft. |
Retain all trees except per 936.9(e)(1)
A-F or 936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or
936.9(v) |
Retain all trees except per 936.9(e)(1) A-F or 936.9(v); no
sanitation salvage except 916.9(s)(t) and (u). |
No timber operations
except per 936.9(e)(1) A-F or 916.9(v); |
Inner Zone per
936.9(f)(4)(B) |
40 ft. |
70% per 936.9(f)(4)(B)3. |
7
largest trees/ac. per 936.9(f)(4)(B)4. |
Increase QMD; No sanitation
salvage except 916.9(s)(t) and (u); commercial thinning or single tree
selection only. |
Preferred Management Practices in 936.9(f)(4)(D) |
Outer Zone per
936.9(f)(4)(C)1. |
30 ft. |
50% per
936.9(f)(4)(C).1. |
NA |
Commercial thinning or single tree
selection only; Retain wind firm trees. |
Preferred Management Practices
in 936.9(f)(4)(D) |
ELZ Applicable only where even-aged
regeneration used adjacent to the WLPZ |
25
ft. |
NA |
NA |
All other Forest Practice Rules |
All
other Forest Practice Rules |
Figure 6: Graphic of profile view of Class I WLPZ
with Confined Channels outside Watersheds in the Coastal Anadromy Zone (not to
scale)
Click
here to view image
Outer Zone:
Modified commercial thinning or single tree
selection
50% Overstory Canopy (OSC)
Inner Zone:
Modified commercial thinning or single tree
selection
Increase QMD
No Sanitation Salvage
70% OSC
Retain 7 largest
trees/ac.
(g) Class II Watercourses --
The following are the minimum requirements for Class II
WLPZ delineation and Timber Operations. Differing Rules are specified for
Watersheds in the Coastal Anadromy Zone, the Southern Subdistrict of the Coast
Forest District, and areas outside the coastal andromy zone. WLPZ width ranges
from 50 to 100 feet slope distance, depending on side slope steepness in the
WLPZ and the Watercourse type. Additional site-specific measures may be
incorporated into the Plan as necessary to protect Beneficial Uses of water
relative to Riparian function pursuant to
14 CCR
§§
936.2(c),
936.4(a)(1), and
936.9(b).
(1) Determine the Class II Watercourse Type:
Class II Watercourses are composed of two types--Class II-S (standard)
Watercourses and Class II-L (large) Watercourses. Class II-S Watercourses are
those classified as Class II Watercourses pursuant to
14 CCR
§
936.5, but do not possess the
characteristics of a Class II-L Watercourse.
(A) A Class II-L Watercourse is defined as a
Class II Watercourse having a contributing drainage area of >= 100 acres in
the Coast Forest District, or >= 150 acres for the Northern and Southern
Forest Districts, as measured from the confluence of the receiving Class I
Watercourse.
(B) All Class II-L
Watercourses shall incorporate requirements stated in
14 CCR
§
936.9, subsection (g)(2) for a
distance of one-thousand feet (1,000 ft.), or total length of Class II,
whichever is less, as measured from the confluence with a Class I Watercourse.
The RPF shall include the mapped location of Class II-L Watercourse segments
receiving protections pursuant to
14 CCR
§
936.9, subsection (g)(2) in the Plan
area. Where such Class II-L Watercourses branch prior to the end of the
one-thousand foot (1,000 ft.) protection distance, the branch that meets or
exceeds the drainage area standards of
14 CCR
§
936.9, subsection (g)(1)(A) shall
receive the remainder of the one-thousand foot (1,000 ft.) protection distance.
If two or more branches meet or exceed the drainage area standards of
14 CCR
§
936.9, subsection (g)(1)(A)1., then
the remainder of the one-thousand foot (1,000 ft.) protection distance shall be
applied to all branches exceeding the standard. If no individual branch exceeds
the drainage area standards of
14 CCR
§
936.9, subsection (g)(1)(A)1., then
the single branch with the largest drainage area shall receive the remainder of
the one-thousand foot (1,000 ft.) protection distance.
(2) Class II WLPZ Widths and Operational
Requirements: All Class II WLPZs shall be composed of two zones regardless of
the Watercourse type: a Core Zone and an Inner Zone. The Core Zone is nearest
to the water, the Inner Zone is contiguous to the Core Zone and is furthest
from the water. The width of the Core and Inner Zones vary depending on the
following three factors:
(i) side slope
steepness in the WLPZ,
(ii) whether
the Watercourse is a Class II-S or Class II-L Watercourse type, and
(iii) whether the Watercourse is within a
watershed in the coastal anadromy zone or outside the coastal anadromy zone.
Graphic depictions of zones and the abbreviated descriptions of the
silvicultural prescriptions and operational requirements are shown in Figure 7.
(A) Core Zone: The width of Core zone varies
from 10 feet to 30 feet measured from the Watercourse or Lake Transition Line.
When established, no Timber Operations are permitted in this zone except for
those listed in
14 CCR
§
936.9, subsection (e)(1)(A)-(F), or
practices approved pursuant to
14 CCR
§
936.9, subsection (v).
Sanitation-Salvage is prohibited except as provided in §
936.9, subsections (s), (t), and
(u). Table 4. summarizes the minimum width for the Core Zone.
(B) Inner Zone: The widths of the Inner Zone
vary from 35 feet to 90 feet and shall be measured from the landward edge of
Core Zone or WTL, whichever is greater. Timber Operations are permitted in this
zone when conducted to meet the goals of this section, including those for the
Inner Zone in
14 CCR
§
936.9, subsections (c)(2) and (4),
pursuant to
14 CCR
§
936.9, subsections (e)(1)(A)-(F) or
pursuant to
14 CCR
§
936.9 subsection (v). Harvesting
prescriptions should focus on practices that use thinning from below. Inner
Zone widths are summarized in Table 4.
1.
Class II-S Watercourses: Any Class II-S Watercourses shall receive protection
in conformance with
14 CCR
§§
936 through
936.7 in addition to the
requirements listed under
14 CCR
§§
936.9(g)(2)(A) and
(B).
2. Class II-L Watercourses in the coastal
anadromy zone: Silvicultural Systems for harvesting are limited to the use of
commercial thinning or single tree selection modified to meet the following
requirements:
(i) When commercial thinning is
used, the QMD of conifer trees greater than 8 inches dbh in the preharvest
Project area shall be increased in the postharvest stand.
(ii) Sanitation-Salvage is prohibited except
as provided in
14 CCR
§
936.9, subsections (s), (t) and
(u).
(iii) Postharvest stand shall
have a minimum 80% Overstory Canopy cover in the Coast and Southern Forest
Districts of the coastal anadromy zone and a minimum 70% Overstory Canopy cover
in the Northern Forest District of the coastal anadromy zone. The postharvest
Canopy may be composed of both conifers and hardwood Species and shall have at
least 25% Overstory conifer Canopy.
(iv) Postharvest stand shall retain the 13
largest conifer trees (live or dead) on each acre of the area that encompasses
the Core and Inner Zones.
(v) Large
trees retained to meet
14 CCR
§
936.9, subsections (g)(2)(B)2.(i) and
(iii) above that are the most conducive to recruitment to provide for the
Beneficial Functions of Riparian Zones (e.g. trees that lean towards the
channel, have an unimpeded fall path toward the Watercourse, are in an advanced
state of decay, are located on Unstable Areas or downslope of such Unstable
Areas, or have undermined roots) are to be given priority to be retained as
future recruitment trees.
3. Class II-L Watercourses outside Watersheds
in the Coastal Anadromy Zone: Silvicultural Systems for harvesting are limited
to the use of commercial thinning or single tree selection modified to meet the
following requirements:
(i) When commercial
thinning is used, the QMD of conifer trees greater than 8 inches dbh in the
preharvest Project area shall be increased in the postharvest stand.
(ii) Sanitation-Salvage is prohibited except
as provided in
14 CCR
§
936.9, subsections (s), (t), and
(u).
(iii) Postharvest stand shall
have a minimum 70% Overstory Canopy cover. The postharvest Canopy may be
composed of both conifers and hardwood Species and shall have at least 25%
Overstory conifer Canopy.
(iv)
Postharvest stand shall retain the 7 largest conifer trees (live or dead) on
each acre of the area that encompasses the Core and Inner Zones.
(v) Large trees retained to meet
14 CCR
§
936.9, subsections (g)(2)(B)3.(i) and
(iii) above that are the most conducive to recruitment to provide for the
Beneficial Functions of Riparian Zones (e.g. trees that lean towards the
channel, have an unimpeded fall path toward the Watercourse, are in an advanced
state of decay, are located on Unstable Areas or downslope of such an Unstable
Areas, or have undermined roots) are to be given priority to be retained as
future recruitment trees.
Table 4. Core and Inner Zone widths.
Water Class |
Class II-S (feet) |
Class II-L
(feet) |
Geographic |
Watersheds |
Watersheds |
Watersheds |
Watersheds |
location |
in
the coastal anadromy zone |
outside the coastal
anadromy zone |
in the coastal anadromy
zone |
outside the coastal anadromy
zone |
Slope class |
Core Zone
(feet) |
Inner Zone (feet) |
Core Zone (feet) |
Inner Zone
(feet) |
Core Zone (feet) |
Inner Zone (feet) |
Core Zone
(feet) |
Inner Zone (feet) |
[LESS THAN EQUAL
TO]30% |
15 |
35 |
10 |
40 |
30 |
70 |
20 |
80 |
30-50% |
15 |
60 |
10 |
65 |
30 |
70 |
20 |
80 |
>50% |
15 |
85 |
10 |
90 |
30 |
70 |
20 |
80 |
(3) Class II Watercourses in the Southern
Subdistrict of the Coast Forest District
In addition to all other Forest Practice Rules applicable
to timber harvesting within the Southern Subdistrict of the Coast Forest
District, the following Rules apply within a Class II WLPZ. These requirements
supersede any other requirements for Class II Watercourses contained in
14 CCR
§
916.9(g).
(A) Retain all trees within the Class II WLPZ
that meet the following criteria:
1. all
trees located within the Channel Zone;
2. all trees that have boles that overlap the
edge of the Channel Zone; and
3.
all trees with live roots permeating the bank or providing channel grade
control, with the following exception:
(i)
1/3 of the stems of redwoods with live roots permeating the bank or providing
channel grade control may be harvested.
(B) Where sufficient spacing exists prior to
harvesting, retained redwood trees greater than or equal to 12 inches dbh shall
not be spaced more than 25 feet apart.
(C) A minimum of 80% Overstory Canopy shall
be maintained within the Channel Zone. If 80% Overstory Canopy is not present
within the Channel Zone, the existing Overstory Canopy within the channel shall
not be reduced.
(D) No more than
1/3 of the conifers 18" dbh or larger may be harvested.
Figure 7: Graphic of profile view of WLPZs for
Class II Watercourses (excluding the Southern Subdistrict) (not to
scale)
Click
here to view image
Click
here to view image
(h) Class III Watercourses --
The following are the minimum requirements for Timber
Operations in Class III Watercourses, unless explained and justified in the
Plan and approved by the Director.
(1)
Establish a 30 foot wide ELZ on both sides of the Watercourse for slopes less
than 30% and an additional 20 foot ELZ where sideslopes are >30%. The ELZ is
measured from the WTL. Within the ELZ:
(A) no
new construction of Tractor Roads permitted;
(B) no ground based equipment on slopes
>50%; and
(C) ground-based
operations are limited to existing stable Tractor Roads that show no visible
evidence of sediment deposition being transported into the adjacent Watercourse
or to the use of feller-bunchers or shovel Yarding.
(2) Retain all Pre-Existing Large Wood on the
ground within the ELZ that is stabilizing sediment and is necessary to prevent
potential discharge into the Watercourse.
(3) Retain all pre-existing down wood and
debris in the Channel Zone.
(4)
Retain hardwoods, where Feasible, within the ELZ.
(5) Retain all Snags (except as required for
safety) within the ELZ.
(6) Retain
all Countable Trees needed to achieve Resource Conservation Standards in
14 CCR
§
932.7 within the ELZ.
(7) Retain all trees in the ELZ and Channel
Zone which show visible indicators of providing bank or bed stability,
excluding sprouting conifers that do not have boles overlapping the Channel
Zone. Visible indicators of stability include roots that permeate the bank or
provide channel grade control.
(8)
Exceptions pursuant to
14 CCR
§
936.9, subsections (e)(1)(A)-(F) are
permitted in any ELZ and Channel Zone.
(i) Section reserved for future
use.
(j) Inner Gorge -- Where an
Inner Gorge extends beyond a Class I WLPZ and slopes are greater than 55%, a
special management zone shall be established where the use of evenaged
Regeneration Methods is prohibited. This zone shall extend upslope to the first
major break-in-slope to less than 55% for a distance of 100 feet or more, or
300 feet as measured from the Watercourse or Lake Transition Line, whichever is
less. All operations on slopes exceeding 65% within an Inner Gorge of a Class I
or II Watercourse shall be reviewed by a Professional Geologist prior to Plan
approval, regardless of whether they are proposed within a WLPZ or outside of a
WLPZ.
(k) Year-round tractor road
use limitations --
(1) Tractor Roads shall
not be used when operations may result in Significant Sediment
Discharge.
(l) Extended
Wet Weather Period -- No Timber Operations shall take place unless the approved
Plan incorporates a complete Winter Period operating Plan pursuant to
14 CCR
§
934.7, subsection (b).
(1) Unless the Winter Period operating Plan
proposes operations during an Extended Wet Weather Period with low antecedent
soil wetness, no Tractor Roads shall be constructed, Reconstructed, or used on
slopes that are over 40% and within 200 feet of a Class I, II, or III
Watercourse, as measured from the Watercourse or Lake Transition
Line.
(m) Tractor Road
Drainage Facility Installation -- All Tractor Roads shall have drainage and/or
drainage collection and storage facilities installed as soon as practical
following Yarding and prior to either (1) the start of any rain which causes
overland flow across or along the disturbed surface within a WLPZ or within any
ELZ or EEZ designated for Watercourse or Lake protection, or (2) any day with a
National Weather Service forecast of a chance of rain of 30% or more, a flash
flood warning, or a flash flood watch.
(n) Treatments to stabilize soils -- Within
the WLPZ, and within any ELZ or EEZ designated for Watercourse or Lake
protection, treatments to stabilize soils, minimize soil erosion, and prevent
Significant Sediment Discharge shall be described in the Plan as follows.
(1) Soil stabilization is required for the
following areas:
(A) Areas exceeding 100
contiguous square feet where Timber Operations have exposed bare
soil.
(B) Approaches to tractor
road Watercourse crossings between the Drainage Facilities closest to the
crossing.
(C) Any other area of
disturbed soil that threatens to discharge sediment into waters in amounts that
would result in a Significant Sediment Discharge.
(2) Soil stabilization treatment measures may
include, but need not be limited to, removal, armoring with Rip-rap,
replanting, mulching, seeding, installing commercial erosion control devices to
manufacturer's specifications, or chemical soil stabilizers.
(3) Where straw or Slash mulch is used, the
minimum straw coverage shall be 90%, and any treated area that has been reused
or has less than 90% Surface Cover shall be treated again by the end of Timber
Operations.
(4) Where Slash mulch
is packed into the ground surface through the use of a tractor or equivalent
piece of heavy equipment the minimum Slash coverage shall be 75%.
(5) For areas disturbed from May 1 to October
15, treatment shall be completed prior to the start of any rain that causes
overland flow across or along the disturbed surface that could deliver sediment
into a Watercourse or Lake in quantities deleterious to the Beneficial Uses of
water.
(6) For areas disturbed from
October 15 to May 1, treatment shall be completed prior to any day for which a
chance of rain of 30% or greater is forecast by the National Weather Service or
within 10 days, whichever is earlier.
(7) Where the natural ability of ground cover
is inadequate to protect Beneficial Uses of water by minimizing soil erosion or
by filtering sediment, the Plan shall specify protection measures to retain and
improve the natural ability of the ground cover to filter sediment and minimize
soil erosion.
(o)
[Section reserved for future use.]
(p) [Section reserved for future
use.]
(q) Site Preparation -- Site
Preparation activities shall be designed to prevent soil disturbance within,
and minimize soil movement into, the channels of Watercourses. Prior to any
Broadcast Burning for Site Preparation, burning prescriptions shall be designed
to prevent loss of large Woody debris in Watercourses, and vegetation and duff
within a WLPZ, or within any ELZ or EEZ designated for Watercourse or Lake
protection. No ignition is to occur within any WLPZ, or within any ELZ or EEZ
designated for Watercourse or Lake protection. When burning prescriptions are
proposed, the measures or burning restrictions which are intended to accomplish
this goal shall be stated in the Plan and included in any required burning
permit. This information shall be provided in addition to the information
required under
14 CCR
§
936.4.
(r) [Section reserved for future
use.]
(s) Exemption notices -- No
Timber Operations are allowed in a WLPZ, or within any ELZ or EEZ designated
for Watercourse or Lake protection, under exemption notices except for:
(1) Hauling on existing roads.
(2) Road Maintenance.
(3) Operations conducted for public
safety.
(4) Construction or
reconstruction of approved Watercourse crossings.
(5) Temporary crossings of dry Class III
Watercourses that do not require notification under the Fish and Game Code
§
1600 et
seq.
(6) Harvesting recommended in
writing by CDFW to address specifically identified forest
conditions.
(t) Emergency
notices -- No Timber Operations are allowed in a WLPZ, or within any ELZ or EEZ
designated for Watercourse or Lake protection, under emergency notices except
for:
(1) Hauling on existing roads.
(2) Road Maintenance.
(3) Operations conducted for public
safety.
(4) Construction or
reconstruction of approved Watercourse crossings.
(5) Temporary crossings of dry Class III
Watercourses that do not require notification under the Fish and Game Code
§
1600 et
seq.
(6) Harvesting recommended in
writing by CDFW to address specifically identified forest conditions.
(7) The harvest of dead or dying conifer
trees subject to the following conditions:
(A) Retention of all trees in the core zone
of Class I and Class II-L Watercourses.
(B) Within any WLPZ, ELZ, or EEZ designated
for Class II or III Watercourse protection, a minimum of two dead, dying, or
diseased conifer trees per acre at least sixteen (16) inches d.b.h. and fifty
(50) feet tall shall be retained within fifty (50) feet of the Watercourse
Transition Line.
(C) Trees to be
harvested or retained shall be marked by, or under the supervision of, an RPF
prior to Timber Operations within the WLPZ or ELZ/EEZ.
(D) Within the WLPZ, or ELZ/EEZ, if the
Stocking Standards of
14 CCR
§
932.7 are not met upon completion of
Timber Operations, unless the area meets the definition of Substantially
Damaged Timberlands, at least ten (10) trees shall be planted for each tree
harvested but need not exceed the point count standards contained in
14 CCR
§
932.7(b)(1), as
appropriate.
(u) Salvage logging -- No salvage logging is
allowed in a WLPZ without an approved HCP, a PTEIR, an SYP, or an approved Plan
that contains a section that sets forth objectives, goals, and measurable
results for streamside salvage operations.
(1) This section does not apply to emergency
operations under
14 CCR
§
1052.
(v) Site-specific measures or nonstandard
operational provisions --
(1) In
consideration of the spatial variability of the forest landscape, the RPF may
propose site-specific measures or nonstandard operational provisions in place
of any of the provisions contained in this section. Site specific Plans may be
submitted when, in the judgment of the RPF, such measures or provisions offer a
more effective or more Feasible way of achieving the goals and objectives set
forth in
14 CCR §
936.9, subsections
(a) and (c), and would result in effects to the Beneficial Functions of
Riparian Zones equal to or more favorable than those expected to result from
the application of the operational provisions required under
14 CCR
§
936.9.
(2) Measures or provisions proposed pursuant
to
14 CCR
§
936.9, subsections (v) shall only be
approved when the Plan incorporates an evaluation of the beneficial functions
of the Riparian zone as set forth in subsection (3) below. In the event of
measures limited in applicability to specific sites, the submitter may instead
of an evaluation, obtain written concurrence from CDFW prior to Plan submittal.
RPFs may request a preconsultation for the site-specific Plan and the Director
may agree and request staff from responsible agencies.
(3) The evaluation of the beneficial
functions of the Riparian zone shall be included in addition to any evaluation
required by all other District Forest Practice Rules, may incorporate by
reference any such evaluation, and shall include the following components
scaled appropriately to the scope of the proposed measure(s) or provision(s)
and the beneficial functions potentially affected.
(A) The following are required components of
an evaluation conducted pursuant to
14 CCR
§
936.9, subsection (v)(3):
1. A description of the evaluation area. If
the evaluation area is different than the watershed assessment area described
pursuant to Board Technical Rule Addendum No. 2, the RPF shall briefly explain
the rationale for establishing the evaluation area.
2. A description of the current condition of
the Riparian zone within the evaluation area related to the beneficial
functions. The RPF may incorporate by reference any conditions described in the
Plan pursuant to
14 CCR
§
936.4, subsection (a). The RPF shall
use the best available information, at the appropriate scale, to describe the
existing vegetation, timber stand characteristics, roads, skid trails,
Landings, channel types, Unstable Areas, Flood Prone Areas, and overflow
channels.
3. An identification of
the beneficial functions that may potentially be affected by the proposed
measure(s) or provision(s).
4. An
identification of the potential Effects to the beneficial functions, both
positive and negative. The RPF may use a reasoned analysis to describe the
Effects and may assign ratings of high, moderate and low to those Effects that
may individually or cumulatively limit anadromous salmonid distribution and
abundance in the watershed.
5. A
detailed description of the site-specific measure(s) or nonstandard operational
provision(s) proposed. The description should address at a minimum the
relationships between the Riparian stand characteristics and ecological
functions, the relative importance of the beneficial functions of the Riparian
zone to the Watercourse, the cost effectiveness of the measure(s) or
provision(s), and the predicted consequences.
6. A schedule for implementing proposed
management practices.
7. A Plan for
monitoring consistent with
14 CCR
§
916.11.
(4) Measures or provisions proposed pursuant
to
14 CCR
§
936.9, subsections (v) shall only be
approved when they meet the following additional standards:
(A) They must be based upon the best
available science, and explained and justified in the Plan.
(B) They must identify potential significant
adverse impacts that may occur to listed salmonids or the beneficial functions
of the Riparian zone as a result of the proposed measure(s) or
provision(s).
(C) They must
identify Feasible systems, methods, procedures or approaches proposed to avoid
or mitigate identified potential significant adverse impacts to a level of
insignificance.
(D) They must be
written so they provide clear instructions and enforceable standards for the
Timber Operator;
(E) They must
provide that, where appropriate for implementation of the measure(s) or
provision(s), the Plan submitter is responsible for retaining an RPF to aid in
interpreting the Plan to the Timber Operator and Timberlands owner on a
continuing basis to help assure compliance with the measure(s) or
provision(s).
(F) They must
identify each standard prescription that would be replaced by the measure(s) or
provision(s) proposed.
(5) Guidance is provided below for site
specific Plans for Flood Prone Areas:
(A)
Site-Specific Plans for Watercourses with Flood Prone Areas or Channel
Migration Zones: This section is an optional approach to be used at the
discretion of the Plan submitter. When used, this section replaces requirements
found in
14 CCR §
936.9, subsection
(f)(3). The goal of this approach is to allow RPFs to develop a site-specific
Plan for salmonid habitat protection on a Flood Prone Area. Site specific Plans
are to lead to development of Properly Functioning Salmonid Habitat and can
include active management to restore the Beneficial Uses of the Riparian
zone.
(B) Timber Operations are
limited to the Flood Prone Areas beyond the outer margin of a CMZ.
(C) RPFs are to propose Riparian protection
zones and management practices that are designed for local
conditions.
(D) Site specific
assessments shall include:
1. Identifying the
issues that need to be considered for Watercourse and Riparian protections
[refer to Table 1 of "Flood Prone Area Considerations in the Coast
Redwood Zone" (Riparian Protection Committee Report, Cafferata et al.
2005)
2. Describing processes that
need to be considered for the issues identified above.
3. Developing a method to define a desired
trajectory for Watercourse and Riparian conditions in the context of the goals
of
14 CCR
§
936.9, subsection (a).
4. Defining how the proposed operations will
aid reaching the desired trajectories.
5. Disclosing assumptions being made at each
step and limits to both the science and the proposed management
activities.
6. Identifying how to
determine what needs to be monitored and how to conduct the
monitoring.
7. Supporting
documentation is required including but not limited to field data, NetMap
analysis, large wood modeling results, etc.
(E) As described in the "
Flood Prone
Area Considerations in the Coast Redwood Zone" (Cafferata et al.
2005), the site-specific Plan for Class I Flood Prone Area management shall
include:
1. an inventory of the Flood Prone
Area for all hydrologic, geomorphic, and biological functions present that can
be affected by Timber Operations;
2. a determination of the category of
inundation where management is proposed [i.e., very frequent (1-5 yr.
recurrence interval or RI), frequent (5-20 yr. RI), moderately frequent (20-50
yr. RI), or infrequent (50+ yr. RI)]; and
3. an appropriate analysis for functions
present in light of possible significant adverse impacts from management.
Analysis for hydrologic functions may include how the Flood Prone Area
vegetative roughness will change with Timber Operations. Analyses for
geomorphic functions may include how proposed operations will change bank
stabilization, amount of soil disturbance on the Flood Prone Area, and the
potential for channel avulsion. Analyses for biological functions may include
how harvesting will affect overflow channels, large wood recruitment, Stream
shading, Riparian microclimate, organic matter input, and terrestrial wildlife
habitat.
(F) Disclosure
and analysis requirements increase with increased risk associated with the
proposed level of activity and the increased frequency of inundation in the
Flood Prone Area. In particular, management proposed within the 20-year
recurrence interval Flood Prone Area in a watershed with coho salmon habitat or
restorable habitat requires detailed analysis.
(G) In addition to considering how proposed
prescriptions will affect Flood Prone Area functions at the Project level, site
specific Plans must consider a larger watershed perspective that includes
consideration of the Stream network and past activities in the watershed. Also,
consideration must be given to the current condition of the Flood Prone
Area.
(H) Information provided in
the "Flood Prone Area Considerations in the Coast Redwood
Zone" (Cafferata et al. 2005) is to be used for guidance in the coast
redwood zone.
(I) The site-specific
Plan for Class I Riparian management must:
(1) have Review Team agencies
pre-consultation and receive concurrence from the Review Team agencies,
including CDFW, and
(2) include a
monitoring component.
(6) Guidance is provided below for site
specific Plans for fire hazard reduction:
(A)
For site-specific Plans that address WLPZs having conditions where
catastrophic, stand replacing wildfire will result in significant adverse
Effects to salmonid Species, Riparian habitat or other wildlife Species, the
site specific Plan shall address measure(s) or provision(s) that create fire
resilient forests, promote reduced fire intensities, and retain Functional
habitat following a wildfire. Site specific Plans proposed for fuel hazard
reduction shall contain information demonstrating the potential for severe fire
behavior and likelihood of stand replacing fires. Fuel reduction measure(s) or
provision(s) shall be designed to reduce fire behavior to levels appropriate
for the region and Riparian area. Measure(s) or provision(s) include, but are
not limited to, activities that eliminate the vertical and horizontal
continuity among all vegetative fuels layer (Surface Fuels, Ladder Fuels and
crown fuels), focus on reducing surface and Ladder Fuel hazards, and
simultaneously meet goals and objectives of
14 CCR
§
936.9 subsections (a) and
(c).
(7) No site-specific
measure(s) or nonstandard operational provision(s) proposed pursuant to
14 CCR
§
936.9, subsection (v) may be
prescribed by an RPF or approved by the Director in lieu of the following
Rules:
(A) The Rules contained in Subchapter
2 (Application of Forest Practice Rules); Article 2 (Ratings and Standards) and
Article 11 (Coastal Commission Special Treatment Areas) of Subchapter 4 (Coast
Forest District Rules); Article 2 (Ratings and Standards) of Subchapter 5
(Northern Forest District Rules); Article 2 (Ratings and Standards) and Article
11 (Coastal Commission Special Treatment Areas) of Subchapter 6 (Southern
Forest District Rules); and Subchapter 7 (Administration) of Chapter 4,
Division 1.5 of
Title 14 of the California Code of Regulations; or
(B) Any Forest Practice Rule pertaining to
the width of the special treatment area adjacent to a wild and scenic river
declared pursuant to PRC §
5093.50,
et seq.; or
(C) Any Forest Practice
Rules or parts of Rules that incorporate practices or standards specified in
the FPA.
(8) The Director
shall not accept for inclusion in a Plan any site-specific measures or
non-standard operational provisions as described in this section where the CDFW
or where two or more agencies listed in PRC §
4582.6
and
14
CCR §
1037.3 have submitted written
comments which lead to the Director's conclusion that the proposed measures or
provisions will not meet the goal of this section and the agencies participated
in the review of the Plan, including an on-the-ground inspection.
(9) Site-specific measures or nonstandard
operational provisions proposed pursuant to
14 CCR
§
936.9, subsection (v) shall not be
considered alternative practices pursuant to
14 CCR
§§
897 or
934.9, in lieu practices or
site-specific practices pursuant to
14 CCR
§
936.1, or Alternative Prescriptions
for the protection of Watercourses or Lakes pursuant to
14 CCR
§
936. 6.
(10) Board staff and the Department shall
work with agencies, stakeholders, and appropriate scientific participants
(e.g., Monitoring Study Group, Technical Advisory Committee) in a transparent
process to:
(1) describe and implement two
pilot Projects, including monitored results, using site-specific or
non-standard operational provisions; and
(2) provide recommendations to the Board for
consideration for adoption to provide detailed guidance for the application of
site-specific or non-standard operational provisions. The pilot Projects and
guidance shall address cumulative and Planning Watershed impacts, and the
guidance may address the appropriate standard site-specific or non-operational
provisions shall meet. A report on the progress of the pilot Projects and
implementation guidance shall be presented to the Board within 18 months of the
effective date of this regulation.
(w) Except when expressly required by
14 CCR
§
936.9, subsections (w)(1)-(5) below,
the provisions of
14 CCR
§
936.9 shall not apply to a Plan that
is subject to:
(1) a valid incidental take
permit issued by CDFW pursuant to § 2081(b) of the F&GC that addresses
anadromous salmonid protection; or
(2) a federal incidental take statement or
incidental take permit that addresses anadromous salmonid protection, for which
a consistency determination has been made pursuant to § 2080.1 of the
F&GC ; or
(3) a valid natural
community conservation plan that addresses anadromous salmonid protection
approved by CDFW under §
2835 of the F&GC ;
or
(4) a valid Habitat Conservation
Plan that addresses anadromous salmonid protection, approved under § 10 of
the Federal Endangered Species Act of 1973; or
(5) Project revisions, guidelines, or take
avoidance measures pursuant to a memorandum of understanding or a planning
agreement entered into between the Plan submitter and CDFW in preparation of
obtaining a natural community conservation plan that addresses anadromous
salmonid protection.