W2001 WLP - British Columbia · W2001 – Roberts Lake 1 I. MANDATORY CONTENT FOR A WOODLOT LICENCE...

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Sage Mountain Resources Ltd. 2008 Fairway Drive Campbell River, B.C. V9H 1R6 Phone: (250) 286-1063 Email: [email protected]

Authorized Licensee Signature: Erika Higgins

[Signature]

[Date] May 16, 2011

Authorized Licensee Signature: Dan Higgins

[Signature]

[Date] May 16, 2011

W2001 – Roberts Lake i

Disclaimer

Recognizing the special nature of management on a woodlot licence, this disclaimer forms part of

the Woodlot Licence Plan (WLP) for Woodlot Licence Number W2001 and advises that:

the decision to operate under one or more of the Default Performance Requirements

provided in the Woodlot Licence Planning and Practices Regulation (WLPPR) is the sole

responsibility of the woodlot licence holder, and involved no detailed oversight or advice

from the prescribing registered professional forester,

this disclaimer is signed on the explicit understanding and information provided by

government that the use and achievement of a Default Performance Requirement meets

the expectations of government with respect to the management of woodlot licences,

the undersigned Registered Professional Forester certifies that this Woodlot Licence Plan

and the supplemental information fulfills the standards expected of a member of the

Association of British Columbia Forest Professionals and that I did personally supervise

the work.

Signed __________________________________________ Seal:

Name (Print) ________Wolfram Wollenheit_______________

RPF # ____3004_______ Contact phone number (250)-337-5588

Email _ [email protected]______

TABLE OF CONTENTS

W2001 – Roberts Lake i

I. MANDATORY CONTENT FOR A WOODLOT LICENCE PLAN

(WLP) ................................................................................................... 1

PLAN AREA .................................................................................................. 1

MAP AND INFORMATION ......................................................................... 2BIOGEOCLIMATIC ZONES AND SUBZONES .................................................................................................. 2

SCENIC AREAS............................................................................................................................................ 3

COMMUNITY WATERSHEDS........................................................................................................................ 3

LICENSED WATER SUPPLY INTAKES AND INFRASTRUCTURES .................................................................... 3

TEMPORARY OR PERMANENT BARRICADES TO RESTRICT VEHICLE ACCESS................................................. 3

AREAS WHERE TIMBER HARVESTING WILL BE AVOIDED............. 4

AREAS WHERE TIMBER HARVESTING WILL BE MODIFIED ........... 4

PROTECTING AND CONSERVING CULTURAL HERITAGE

RESOURCES ....................................................................................... 7

WILDLIFE TREE RETENTION STRATEGY............................................. 9INDIVIDUAL WILDLIFE TREES ........................................................................................................ 9

WILDLIFE TREE RETENTION AREAS............................................................................................. 10

MEASURES TO PREVENT INTRODUCTION OR SPREAD OF

INVASIVE PLANTS ......................................................................... 12

MEASURES TO MITIGATE EFFECT OF REMOVING NATURAL

RANGE BARRIERS.......................................................................... 12

STOCKING INFORMATION FOR SPECIFIED AREAS ......................... 12

PERFORMANCE REQUIREMENTS......................................................... 13SOIL DISTURBANCE LIMITS ........................................................................................................... 13

PERMANENT ACCESS STRUCTURES ............................................................................................. 13

USE OF SEED .................................................................................................................................... 13

STOCKING STANDARDS .................................................................................................................. 14

WIDTH OF STREAM RIPARIAN AREAS........................................................................................... 14

WIDTH OF WETLAND RIPARIAN AREAS ....................................................................................... 14

TABLE OF CONTENTS cont’d

W2001 – Roberts Lake ii

WIDTH OF LAKE RIPARIAN AREAS................................................................................................ 14

RESTRICTIONS IN A RIPARIAN RESERVE ZONE .......................................................................... 15

RESTRICTIONS IN A RIPARIAN MANAGEMENT ZONE ................................................................ 15

WILDLIFE TREE RETENTION.......................................................................................................... 15

COARSE WOODY DEBRIS ................................................................................................................ 16

RESOURCE FEATURES .................................................................................................................... 16

APPENDICES ............................................................................................... A

II. SUPPLEMENTAL INFORMATION REQUIRED TO BE SUBMITTED

IN SUPPORT OF THE PROPOSED WOODLOT LICENCE PLAN. I

1. REVIEW AND COMMENT...................................................................... IADVERTISING ...................................................................................................................................... I

REFERRALS .......................................................................................................................................... I

COPY OF WRITTEN COMMENTS RECEIVED................................................................................... I

REVISIONS MADE AS A RESULT OF COMMENTS RECEIVED ....................................................... I

2. CONSULTATION WITH FIRST NATIONS ..........................................II

3. EXEMPTIONS ..........................................................................................II

4. RATIONALE IN SUPPORT OF PROPOSED ALTERNATIVE

PERFORMANCE REQUIREMENTS .............................................. IIISTOCKING STANDARDS .................................................................................................................. III

SOIL DISTURBANCE LIMITS ............................................................................................................. V

WIDTH OF STREAM, WEtland and Lake RIPARIAN AREAS ............................................................. V

RESOURCE FEATURES ...................................................................................................................... V

5. WILDLIFE TREE RETENTION AREAS STAND ATTRIBUTE

TABLE ............................................................................................... VI

W2001 – Roberts Lake 1

I. MANDATORY CONTENT FOR A WOODLOT LICENCE

PLAN (WLP)

PLAN AREA

This plan covers the entire 725 ha included in Woodlot License W2001. The Woodlot Licence area consists entirely of Crown land located north of Campbell River, in the

vicinity of Roberts Lake on the north side of the Island Highway. Access is provided by

spur roads off the Island Highway as well as by the Elk Bay Forest Service Road, which

bisects the area in a northern direction. The eastern unit of the Woodlot Licence area

straddles the eastern shore of Roberts Lake and Cecil Lake, while the western unit

follows the Island highway, extending north and upslope.

The Woodlot Licence is between 150 and 500 m in elevation and the terrain is variable.

For the most part, the slope gradient is between 10% and 40 %, segmented by rocky

benches and rock outcrops. Only in the north of the western unit and in the east of the

eastern unit is the terrain quite steep (60% - 100%) and it continues to climb in elevation.

The Woodlot Licence is located at the foot of Menzies Mountain, which rises to over

1200 m in elevation.

Recent harvest activities were carried out by Western Forest Products and WWK Forestry

Limited Partnership (before the creation of the Woodlot Licence), resulting in extended

cut blocks along the Island Highway and in the centre of the eastern unit. The forest

cover of the remaining area originated after logging activities that occurred in the 1920s

to 1930s and the 1960s to 1970s. In general, the stand ages are either around 80 years or

around 40 years. Old growth stands exist only as remnants on poor rock knobs, or as a

veteran layer of a selectively logged stand. On good sites the older second growth stands

feature merchantable volume and value.

In general, the species composition is a combination of Douglas fir as the leading species

with minor components of western hemlock and redcedar. Deciduous stands are rare and

do not amount to more to 2% of the forest cover. Lodgepole pine occurs either as a

minor stand component, or in as a major component in small areas on bluffs and shallow

rocky soils.

The recreation site polygon at the north end of Roberts Lake is excluded from the

Woodlot Licence area. Here, the main recreation features are the beaches, trails and

campground where the Mennonite Church hosts the “Camp Bob” every summer. Other

activities include fishing, water sports, hiking, wildlife viewing and hunting. At the south

end of the lake there is another recreation site, as well as the Roberts Lake Resort.

Other features of the Woodlot Licence are two ungulate winter ranges (UWR) for deer,

one in each unit as well as a research installation (1 experimental plot) in the western

unit.


MAP AND INFORMATION

Table 1: Map and Information Content

Information Item Map Text N/A

Forest cover

Topography; (unless exempted by DM)

Location of streams, wetlands and lakes as shown on forest cover maps, terrain resource inventory maps and fish and fish habitat inventory maps.

Riparian classification of streams, wetlands and lakes if shown on maps

Identification of fish streams

Biogeoclimatic zones and subzones (unless exempted by DM)

Public utilities (transmission lines, gas & oil pipelines, and railways)

Existing roads

Special Situations that may not Apply to the WL area

Resource Management Zones, Landscape Units or Sensitive Areas

Wildlife Habitat Areas (unless exempted by DM)

Scenic Areas

Ungulate Winter Ranges

Community Watersheds

Fisheries Sensitive Watersheds

Community and domestic water supply intakes that are licensed under the Water Act and any related water supply infrastructures

Contiguous areas of sensitive soils

Temporary or permanent barricades to restrict vehicle access

Private property within or adjacent to the woodlot licence area

Resource features other than wildlife habitat features and archaeological sites (unless the location of the resource feature is not to be disclosed)

All of the applicable information required to be addressed under section 8(1) of the

Woodlot Licence Planning and Practices Regulation (WLPPR), and checked above, is

discussed in the following text of this section and/or is identified on the WLP maps in

Appendix 1 and 2.

Biogeoclimatic Zones and Subzones

The Woodlot Licence is located within the “Very Dry Maritime” variant of the Coastal

Western Hemlock biogeoclimatic zone (CWH xm2) where the average rainfall can range

from 1100 to 2700 mm/year. In the uppermost ranges, both units contain a sliver of the

adjacent biogeoclimatic variant, the “Submontane Moist Maritime” (CWHmm1). As

such, parts of the woodlot licence area are located near the transition to a wetter, cooler

subzone, with more influence of hemlock and amabilis fir. However, the aspect of the

eastern and western unit is west and southwest respectively, which may somewhat

compensate for the tendency toward a moister climate.


Resource Management Zones, Landscape Units or Sensitive Areas

The Woodlot Licence is located within Resource Management Zone 31 as described in

the Vancouver Island Land Use Plan. This area is also included in the approved Sayward

Landscape Unit Plan. There are no sensitive areas established within the Woodlot

Licence.

Scenic Areas

As identified in the Sayward Landscape Unit Plan and as established by order in 2005,

the Woodlot Licence area contains scenic areas with retention (R) and partial retention

(PR) visual quality objectives (VQO). See ‘Areas Where Timber Harvesting Will be

Modified’ in this plan for management strategies relating to visual quality objectives.

Community Watersheds

No part of the Woodlot Licence is located within a community watershed.

Licensed Water Supply Intakes and Infrastructures

There are no licensed water supply intakes or associated infrastructure within the

Woodlot Licence area. The closest water intake is at the south end of Roberts Lake

servicing the Roberts Lake Resort

Temporary or permanent barricades to restrict vehicle access

Permanent barricades to restrict vehicle access are not established at the existing

entrances to the Woodlot Licence areas. Initially there are no plans to erect permanent

barricades or gates, but as the tenure’s road system develops vehicle access may be

limited if criminal activities are noticed. The purposes of such gates or barriers would be

to reduce the risk of forest fire, to minimize wood theft including firewood, poaching,

vandalism, and to prevent garbage dumping. Temporary barriers will be implemented

during harvest operations and road construction in compliance with current legislation, to

facilitate public safety and to protect equipment and materials.

Other features and resource values relevant to the management of the Woodlot Licence

not mentioned specifically in the text above are indicated on the attached maps

(Appendices 1 and 2).


AREAS WHERE TIMBER HARVESTING WILL BE AVOIDED

There are no areas in this Woodlot Licence where timber harvesting will be strictly

avoided.

AREAS WHERE TIMBER HARVESTING WILL BE

MODIFIED

Areas in this Woodlot Licence where timber harvesting will be modified to protect and

manage resources are shown on the map by shading, hatching or lines.

Ungulate Winter Range (UWR) and Oldgrowth Management Areas (OGMA):

The Woodlot Licence contains two areas that double as OGMA/UWR, which

have been identified in the Sayward Landscape Unit Plan and are established by

legal orders.

Felling will not occur within the OGMA/UWR except for road maintenance, road

deactivation, brushing and clearing of existing roads, removal of danger trees,

felling of guyline clearance, or tailhold anchor trees. Trees removed for safety are

to be retained on site for coarse woody debris. Road construction may be allowed

within the OGMA when no other practical option for road location is available.

Critical stream reaches have been established by legal order and are identified in

the Sayward Landscape Unit Plan. They are shown in bold red on the woodlot

licence plan map. The objective is to:

retain all windfirm trees with roots embedded in the streambank; and

for S4 streams, retain 50% of the stems, representative of species age

and size, within 10 m of the channel.

Riparian reserve zones (RRZ) are not planned for regular harvesting except as

specified by regulation, tree removal for the purpose of creating trails, clean up of

blowdown or carrying out a sanitation treatment. The riparian reserve zones are

allocated to streams, lakes and wetlands and are denoted in light red shading on

the map.

There will be no harvesting in the recently fertilized immature stands indicated on

the Woodlot Licence Plan Map for a period of ten years (Fall, 2020). Harvesting

may take place in mature stands (age class 4 and greater) where fertilization

overlapped from the intended treatment area.

Riparian Management Zones (RMZ): The table below (Table 2) outlines how

timber harvesting will be modified based on the stream and lake classification.

Depending on the present stand structure, terrain, windthrow risk and block

configuration, the retention level will be uniform, grouped or spatially distinct. In

general, understory and unmerchantable redcedar, and other conifers of good form

and vigour, will be maintained wherever possible to meet the intent of riparian


area management for all stream and wetland classifications. RMZs are denoted in

light green diagonal hatching on the WLP map.

Table 2: Modification of Harvesting in RMZs by Riparian Classification

RIPARIAN CLASS

INTENT OF MANAGEMENT SPECIES TO

RETAIN

RETENTION LEVEL POST HARVEST

(stems/ha)

S2

(Fish bearing or Community Watershed)

S2 = 5 - 20m)

Maintain the integrity of the RRZ

Assist in maintaining wildlife attributes within the RMA, such as wildlife tree cover, nesting and perching habitat and diversity of vertical forest structure.

25 - 100

S3


S3 = 1.5 - 5.0m)



0 - 100%

S4


up to 1.5m)

Maintain stream bank integrity

Provide shaded cover, LWD and litter

25 - 100% within 10 m of

channel retain 50% of stems, represent-

tative of species, age and size

S5(non-fish > 3m)

S6(non-fish 3m)

Minimize debris transport to lower reaches of stream

0 - 100%

Lake and Wetlands



Fd, Cw, Hw,

Pl, Pw, Dr and Ac

25 - 100%

Fd = Douglas fir, Cw = western red cedar, Hw = western hemlock, Pl = lodgepole pine, Pw = western white pine, Dr = red alder, Ac =

cottonwood

Scenic Areas: To ensure harvest areas are managed to be consistent with the

retention (R) and partial retention (PR) visual quality objectives (VQO) large

openings will follow the line and form of the landscape. Innovative visual forest

landscape design techniques, such as screening and green-up sequencing, will be

used to reduce visual impacts along highways and other foreground situations.

The assessment procedures outlined in the Visual Impact Assessment Guidebook

(2001) may be used to direct design and assist in evaluation, whereby the

categories of visually altered forest landscapes are defined as:

(a) preservation: consisting of an altered forest landscape in which the

alteration, when assessed from a significant public viewpoint, is

(i) very small in scale, and

(ii) not easily distinguishable from the pre-harvest landscape;


(b) retention: consisting of an altered forest landscape in which the


(i) difficult to see,

(ii) small in scale, and

(iii) natural in appearance;

(c) partial retention: consisting of an altered forest landscape in which the


(i) easy to see,

(ii) small to medium in scale, and

(iii) natural and not rectilinear or geometric in shape;

(d) modification: consisting of an altered forest landscape in which the

alteration, when assessed from a significant public viewpoint,

(i) is very easy to see, and

(ii) is

(A) large in scale and natural in its appearance, or

(B) small to medium in scale but with some angular

characteristics;

(e) maximum modification: consisting of an altered forest landscape in

which the alteration, when assessed from a significant public viewpoint,

(i) is very easy to see, and

(ii) is

(A) very large in scale,

(B) rectilinear and geometric in shape, or

(C) both.

Recreation: In 2006 the Campbell River Forest District established a set of

recreation feature polygons by legal order. Relevant to Woodlot Licence W2001,

such recreation features are located around Cecil Lake, and along the north and

south end of Roberts Lake. The order is accompanied by a rationale document

that addresses practical implementation and requires an assessment of potential

impacts of forest management to the present recreation features, as well to the

recreational setting and experience.

The licensee will consult with the stewardship forester of the Campbell River

Forest District, in case harvest activities are planned within or adjacent to the

recreation feature polygons as shown on the woodlot licence plan map. The

stewardship forester will be able to provide insight into the magnitude of the

present values and to clarify the original intent of the feature protection. The

subsequent block and harvest design will rely on professional judgement and the

assistance of specialists, if necessary.

Research: In the western unit of the Wooodlot Licence, there is a provenance trial

plot (EP0599.03), which is still active and requires a 75 m buffer. This buffer

needs to be measured from the boundary of the well-marked site. If harvesting is

planned to encroach this buffer, other than danger tree removal, the managing

researcher is to be consulted to avoid detrimental impacts to the research project.


PROTECTING AND CONSERVING CULTURAL HERITAGE

RESOURCES

Woodlot Licence W2001 lies within the traditional territories of three First Nations. A list

of these First Nations and their contact information is provided within Part II-1, ‘Review

and Comment’. In addition to the information sharing process that is implemented for

the approval of this plan, First Nations, and other interested parties, are welcome during

the term of this plan to review planned developments upon their own initiative.

Documentation of all consultation with First Nations is to be included within the

supplemental information (Part II) of the final submission of this plan.

The latest Archaeological Overview Assessment (AOA) available has been prepared in

March 2007 by Millennia Research Limited. W2001 is projected to have low potential

for the presence of CMTs. A moderate potential for midden occurrence is projected in a

minor area of the woodlot licence. If any operation is planned in the vicinity of these

locations, the licensee will follow the “Model Operationalization” guideline for the 2007

AOA in order to determine the requirement for further archaeological work.

In general, if the woodlot licensee or any personnel of the licensee finds evidence of

traditional use1 or cultural heritage values, the District Manager will be notified and all

work will cease within the immediate (30 m) area. The licensee will cooperate fully, as

requested by the District Manager or his or her designate.

The following results and strategies (Table 4) for managing cultural heritage values will

apply. These are based on known cultural heritage issues of interest to First Nations in the

Campbell River Forest District.

1 A forest resource use traditionally exercised by a First Nations people


Table 4: Results and Strategies for Cultural Heritage Resources

Cultural

Heritage Value

Results & Strategies

Result:

Enable continued access to red cedar for traditional use by local First

Nations.

Cedar:

Strategies:

Based on availability of stock and ecological suitability (e.g. Cw listed as

preferred species), a component of redcedar will continue to be planted in

the woodlot to ensure a long-term supply.

Naturally occurring young redcedar trees (including poles) will be retained

where operationally practicable.

Access will be allowed to monumental cedar trees for traditional use by

local First Nations. There are currently no known monumental cedar trees

(cedar trees greater than 250 years old and 1.0m DBH) within the woodlot

but the aforementioned recruitment strategies will allow opportunities for

future generations.

Result:

Enable continued access to traditionally used plants for traditional use

by local First Nations.

Traditionally

Used Plants:

Strategies:

When local First Nations have indicated specific interest in traditional

use plants, the licensee will identify the presence of such plants in

planned harvest areas and communicate this to the interested First

Nations prior to cutting permit submission. This is to allow for review

by the local First Nations and for the collection of traditional use plants

by local First Nations prior to harvest. Interested local First Nations

will also be notified of traditionally used plants, particularly those

indicated to the licensee as scarce or not abundant, if identified on the

Woodlot Licence area.

A no-pesticide use policy is implemented in this Woodlot Licence.

Manual brushing and early planting of large stock is the preferred

method to overcome brush problems.

Result:

Harvest plans will seek to conserve and protect identified CHR.

Cultural Heritage

Resources

Strategies:

The Licensee will share information with local First Nations upon

request and will be available for field reviews.

Work will cease within a 30m radius if evidence of a previously

unrecorded CHR resource is identified during operations.


WILDLIFE TREE RETENTION STRATEGY

Note: The proportion of the Woodlot Licence area that is occupied by wildlife tree

retention areas is specified in the “PERFORMANCE REQUIREMENTS” section of this

Woodlot Licence plan.

INDIVIDUAL WILDLIFE TREES

a) Species and Characteristics:

Desired species are (in order of preference): Fd, Cw, Hw, Pl, Pw, Dr, and Ac with a

minimum dbh of 50cm. The following table describes the species and characteristics of

individual trees that will guide the selection of wildlife trees to be retained from

harvesting.

Table 5: Wildlife Tree Value and Characteristics for All Species

HIGH (at least two of the listed characteristics)

MEDIUM LOW

CH

AR

AC

TE

RIS

TIC

S

Internal decay (heartrot or natural/excavated cavities present)

Crevices present (loose bark or cracks suitable for bats)

Large brooms present

Active or recent wildlife use

Current insect infestations

Tree structure suitable for wildlife use (e.g. large nest, hunting perch, bear den, etc.)

Largest tree on site (height and/or diameter) and/or veterans

Locally important wildlife tree species

Large, stable trees that will likely develop two or more of the characteristics listed under HIGH

Trees not covered by HIGH or MEDIUMcategories

From: Wildlife Tree Committee recommendations available at: http://www.for.gov.bc.ca/hfp/wlt/wlt-policy-02.htm

Given the nature of the historic logging and the thrifty second-growth stands present in

the Woodlot Licence area few trees in a given stand may have ‘high’ value attributes.

One tree per hectare will be the minimum threshold for retention with preference given to

trees onsite with the highest wildlife value. Trees may be left as dispersed individuals or

as a groups either internally or externally to harvest areas.


Conditions under which Individual Wildlife Trees may be Removed:

The following specific conditions will influence the decision of where individual wildlife

trees may be removed:

worker safety;

the significance of forest health risk to surrounding stands;

the ability to retain other wildlife trees to perform as suitable wildlife habitat; and

the availability of wildlife trees and CWD in adjacent areas.

Unsafe high value wildlife trees will be protected by no-work zones or re-design of

cutblock or road configuration if they exhibit a combination of the following

characteristics: wildlife tree value category HIGH applicable, DBH > 50 cm, wildlife tree

class 2 – 8, > 20 m high, conks or decay present, wildlife use present (nesting, cavities,

recent feeding, denning), species Fd, Cw, Hw, Pl, Dr or Ac. All workers involved with

the removal of potential wildlife trees will be informed of applicable standards prior to

fieldwork to help mitigate unnecessary removals.

b) Replacement of Individual Wildlife Trees:

Individual trees will be replaced if they are of ‘high’ wildlife value. Replacement trees

will be selected using criteria outlined above with a preference for selecting trees that

have two or more high wildlife tree value characteristics.

WILDLIFE TREE RETENTION AREAS

a) Forest Cover Attributes:

Wildlife tree retention areas (WTRAs) are preferentially located in fully constrained

areas for long-term retention such as riparian reserve zones (RRZ) and OGMA/UWR.

The minimum proportion of the Woodlot Licence area for long-term wildlife tree

retention is 58 ha (8.0%) as per Section 52(1) of the WLPPR. The presently allocated

OGMA/UWR and RRZ for W2001 are shown on the 1:5000 WLP maps and occupy 65

ha or approximately 9% of the Woodlot Licence area, so that no additional wildlife tree

retention area is required.

The forest cover of the OGMA/UWR is dominated by Douglas fir stands with minor

hemlock component on moderate to poor sites. The stand ages are either around 80 years

or 300 years. The forest cover in the RMZ is mixed with second growth stands on

moderate to good sites. The species component spans from alder leading stands, to

cedar/hemlock and Douglas fir/hemlock stands. Stand ages range from 60 to 120 years.

A table describing each OGMA area is given in Appendix II – 5.

Through on-going observation, there will be potential for identifying and locating nesting

trees, and other important habitat trees for retention. No nesting sites or bear dens

requiring specific habitat or tree retention have been identified to date.


b) Conditions Under which Trees may be Removed from Wildlife Tree Retention

Areas:

The goal is to maintain all stems within streamside reserves and WTRAs. However, the

following stand-specific issues will influence the decision of where salvage may be

appropriate for WTRAs include:

worker safety;

the significance of forest health risk to surrounding stands;

the ability of the retained wildlife trees to perform as suitable wildlife habitat; and

the availability of wildlife trees and CWD in adjacent harvest areas.

Salvage is not permitted within WTRAs that are also designated as OGMAs. Salvage of

windthrown timber; or salvage where forest health issues pose a significant threat to areas

outside the WTRAs, is permitted in WTRAs that are not also designated as OGMAs.

Such salvage would be permitted should higher level plans be amended to remove areas

from the OGMA designation, or within WTRA that are identified concurrently with

future operation planning within the woodlot licence area.

Individual danger trees may be felled but not removed if the stem is completely within

the WTRA.

c) Replacement of Trees Removed from Wildlife Tree Retention Areas:

Given the nature of the adjacent stands and existing WTRAs, the felling of danger trees

within a distance from harvest edges as defined in the specific cutting authority will not

be a common occurrence or threaten the long-term integrity and usefulness of the

WTRAs. As such, no strategy for the specific replacement of individual trees within

WTRAs is presented.

Where salvage/harvesting is planned and authorized within a wildlife tree retention area,

a suitable replacement WTRA of at least equivalent quality will be identified

concurrently to achieve the retention target. Where all or part of a WTRA is salvaged, the

salvaged area should be replaced with other suitable habitat in the nearest possible

location. If a WTRA suffers windthrow, but is not salvaged, it needs not be replaced.

Replacement areas must have equal or better wildlife values. Attempts will be made to

incorporate important features such as snags, marking, perch and nesting trees, dens, and

other significant wildlife features.


MEASURES TO PREVENT INTRODUCTION OR SPREAD OF

INVASIVE PLANTS

The introduction or spread of invasive plants, specifically scotch broom, into the Woodlot

Licence area through the use of standard practices is possible.

Where it is known or reasonably expected that machinery will be transported from a

contaminated site, on or off the woodlot, cleaning of tires, tracks, buckets, undercarriage,

etc. will be completed prior to transportation. All newly constructed roads will be grass

seeded if scotch broom establishment becomes a concern. Seed mixtures used for the

above purposes or for those under Section 29 of the WLPPR will be assessed to ensure

that their use does not introduce additional invasive species. Additional species listed in

the Invasive Plants Regulation (reg. 18/2004) will be managed accordingly if identified

and located on the woodlot.

MEASURES TO MITIGATE EFFECT OF REMOVING

NATURAL RANGE BARRIERS

There are no rangelands present on or adjacent to the Woodlot Licence and no measures

or activities are proposed.

STOCKING INFORMATION FOR SPECIFIED AREAS

Alternative: The stocking information for specified areas are found in Appendix 3

Specified areas include:

areas subject to commercial thinning,

the removal of individual trees, or

areas subject to single/group tree selection or

other types of intermediate cutting and /or

areas subject to the harvest of special forest products.

For the purposes of this plan, commercial thinning, the removal of individual trees,

group selection, intermediate cutting or the harvest of special forest products may

take place anywhere within the woodlot except in designated areas where harvesting

will be avoided. The delineation of specific areas will be conducted in conjunction

with the pre-harvest mapping as per Section 33 of the WLPPR.


PERFORMANCE REQUIREMENTS

SOIL DISTURBANCE LIMITS

Alternative - WLPPR s.24(1)(a):

8% of Net Area to be Reforested except

a) up to a maximum of 30% in localised areas (standard unit basis) requiring site

preparation for brush or root rot control. In root-rot areas with suitable soils

destumping may be prescribed to control the spread of infection. In areas

dominated by heavy salal or salmonberry a light soil raking using an excavator

mounted brush rake may be prescribed to disturb salal/salmonberry roots. This

will create more plantable spots and facilitate seedling establishment and achieve

early brush control. The objective of this treatment is to minimize brush

competition during seedling establishment and to create a mixed substrate of soil

and forest floor, not a complete removal of the forest floor. These treatments may

result in dispresed scalps and gouges.

b) up to a maximum of 15% in wet site units with fluctuating water tables or

prolonged periods of standing water in the winter (CWHxm 11, 12, 13, 14, 15). In

these areas 400-600 mounds per ha may be created (where prescribed) using an

excavator bucket to create suitable micro sites. This will result in dispersed deep

gouges.

Further rationale is provided in the supplementary information included in this

plan. See Section II - 4.

PERMANENT ACCESS STRUCTURES

Default: WLPPR s.25:

The maximum area occupied by permanent access structures is as follows:

Cutblocks 5 ha – 7% of cutblock area

Cutblocks 5 ha – 10% of cutblock area

Total Woodlot Licence Area – 7% of Woodlot Licence area

USE OF SEED

Default - WLPPR s.32:

Adoption of Chief Forester’s Standards for Seed Use.


STOCKING STANDARDS

Alternative - WLPPR s. 35(1)(a):

The stocking standards, regeneration dates and free growing dates are detailed in

Appendix 3. Clarification and rationale is provided in the supplementary

information included with the plan. See Section II - 4.

WIDTH OF STREAM RIPARIAN AREAS


In general, the width of stream riparian areas will be as specified in Section 36(4)

of the WLPPR. However, if roads are located in a riparian area its widths are

reduced to the distance from the stream bank edge to the lower edge of the fill

slope for the roads and trails.

Clarification and rationale for the RMA reductions is provided in the

supplementary information included with the plan.

See Section II - 4.

WIDTH OF WETLAND RIPARIAN AREAS


In general the width of wetland riparian areas will be as specified in Section

37(3)(b) of the WLPPR. However, if roads are located in a riparian area its

widths are reduced to the distance from the wetland edge to the lower edge of the

fill slope for the roads and trails.



See Section II - 4.

WIDTH OF LAKE RIPARIAN AREAS


In general the width of lake riparian areas will be as specified in Section 38(2)(b)

of the WLPPR. However, if roads are located in a riparian area its widths are

reduced to the distance from the lake edge to the lower edge of the fill slope for

the roads and trails.



See Section II - 4.


RESTRICTIONS IN A RIPARIAN RESERVE ZONE

Alternative: WLPPR s.39

• Cutting, modifying or removing trees in a riparian reserve zone is limited to the purposes described in Section 39(1) of the WLPPR. For the purpose of cleaning up blow down timber, it is permitted to cut and remove down and leaning trees, without disturbance of stream channel and stream bank, except those logs that are required as large woody debris and for channel stabilization.

• For the purpose of Section 39(2.1) of the WLPPR, roads may be constructed in a riparian reserve zone if no other practicable alternative exists, or if otherwise constrained by terrain.

URESTRICTIONS IN A RIPARIAN MANAGEMENT ZONE

Alternative: WLPPR s.40

• Construction of a road in a riparian management zone is limited to the conditions described is Section 40(1) of the WLPPR.

• For the purpose of Section 40(1)(a) of the WLPPR, roads may be constructed in a riparian management zone if a road grade previously existed in this location, or if otherwise constrained by terrain.

• Restrictions and conditions on road construction, maintenance and deactivation activities, and on cutting, modifying or removing trees in a riparian management zone are as described in Section 40.

UWILDLIFE TREE RETENTION

Default - WLPPR s.52(1):

The proportion of the Woodlot Licence area that is occupied by wildlife tree retention areas is no less than the least of the following:

• The proportion specified for the area in a land use objective, or

• The proportion specified in the WLP, or

• 8%


UCOARSE WOODY DEBRIS

Default - WLPPR s.54(1):

Area on UCoastU – minimum retention of 4 logs per ha ≥ 5 m in length and ≥30 cm in diameter at one end.

URESOURCE FEATURES

Alternative - WLPPR s.56(1):

Ensure that forest practices do not damage or render ineffective a resource feature other than recreation resource features.

After consulting with those who are most familiar with the original intent of the associated GAR order, an assessment of potential impacts of a forest practice to the recreation resource features, as well to the recreation setting and experience, shall be completed before commencing the forest practice which is deemed to be consistent with the recommendations of the assessment.

For additional clarification regarding this alternative performance measure, see Appendix II – 4, found on page IV.

*****************************************************************

UNote:U Only the performance requirements in Part 3 (Practice Requirements) of the WLPPR for which an alternative can be proposed are shown in this Woodlot Licence Plan. The remaining performance requirements in Part 3 are not shown, nor are the performance requirements in Part 4 (Roads).

W2001 – Roberts Lake A

APPENDICES

Appendix 1: Woodlot Licence Plan Map (Western Unit)

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230 04A192 25230 04A192 25 A807 98230 0 AA807 98230 0 A

A807 98230 0 DA807 98230 0 D

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EB10

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ELK BAY FSR

ELK BAY FSR

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EBH U100

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S4

S4

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Str 1

Str 2

Str 6

Str 9

Str 13

Str 6c

Str 5

Str 10

Str 13a

Str 7a S

tr 1

Str 10

Str 7

Str 3

Str 8

Str 2a

Str 4

Str 5a

Str 3

Str 11

Str 11

Roberts LakeL1

McNair LakeL1

Cecil LakeL1 W4W4

82

455FdCw223-27/27

858FdCwHw(Pl)223-27/27

438FdH(Dr)557-0/34

458FdH538-0/18

514

4FdHw448-33/32

61 515FdHw548-0/23

488HwFd557-0/30

883HwFd211-14/14

453FdCw223-27/27

460

512FdH(Dr)556-0/34

521FdH446-0/26

472/LFd953-0/21

517FdH656-0/29

582Pl(HFd)524-0/11

449HwDr(Fd)447-0/30

485Fd537-0/16

599/LFd952-0/23

990HwFd(Cw)216-24/24

542FdH(Cw)535-0/17

518FdH(Dr)536-0/20

496FdH434-0/23

466HwDr(Fd)447-0/30

454Fd224-27/27

505FdH(Dr)556-0/34

494FdH545-0/23

616Pl(Fd)525-0/9

519FdH(Pw)535-0/18

434FdH(Cw)437-0/18

464FdHw(CwDr)547-0/23

617

498

1096Fd(H)557-0/32

522FdH446-0/26

593

471PlFd524-0/10

511FdH436-0/25

576FdPlH724-0/12

549FdH537-0/17

461/LFdH(Pl)535-0/17

588PlFd524-0/11

580FdPl(H)834-0/14

605/LFd953-0/20

545FdH548-0/25

481FdH950-0/22

467FdHw(Cw)224-27/27

435FdH547-0/28

490FdH(Dr)537-0/22

524FdPlH425-0/15

527Dr327-0/18

1097FdH446-0/26

491Fd(H)548-0/25

486FdCw223-27/27

457Fd(Pl)222-18/18

507FdH537-0/17

587

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526FdH546-0/25

509FdH547-0/28

468Fd(HwCw)224-27/27

450FdCw223-27/27

610DrHFd436-0/20

525FdH425-0/14

499

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470Fd(Pl)214-32/32

482FdPl527-0/15

483Fd(H)446-0/24510

484Pl(Fd)534-0/18

504Fd(H)435-0/24

1095FdH547-0/27

500FdH557-0/33

1088PlFdH525-0/10

541FdH952-0/20

489FdH557-0/31

508DrCwH346-0/31

501H(FdCw)547-0/24

443HCwFd437-0/21

479

585HFdPl(Cw)735-0/11

493

1100FdH538-0/17

528

463/LPlFd524-0/13

439FdH444-0/27

604FdH932-0/12

459/LPlFd524-0/13

437CwH644-0/20

516Fd(H)545-0/26

1145Fd(Pl)214-32/32

469FdPlH526-0/12

497FdH(Cw)556-0/32

447Fd(H)528-0/13

452HwCw(Fd)211-14/14

442DrH(CwFd)336-0/22502FdH646-0/26

473Fd224-27/27

495

451FdCwHw(Pl)223-27/27

595

546

547FdH537-0/17

445

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448FdPl524-0/14

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523FdH434-0/19

441Pl(HFd)525-0/12

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503

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1099FdH556-0/33

520DrFdH337-0/25

601

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475FdH546-0/27

127Hw(FdCwDr)222-22/22

2221HwFd(Cw)223-22/22

444FdHw528-0/14

596FdPl723-0/12

476Pl(Fd)526-0/10

567HPlFd825-0/10

563PlFd523-0/9

506FdH547-0/28

531FdH436-0/18

574FdPlH724-0/12

597Pl(HFd)524-0/11

783HwFd438-0/19

559PlFd523-0/9

529CwH833-0/11

571FdHw(Pl)824-0/12

487PlFd424-0/12

1098PlFd424-0/12

474Fd224-27/27

2222FdH436-0/18

Crown

Crown

Crown

Crown

Crown

W2002

Sandy Beach

1+250

1+085

1+027

0+724

1+202

0+974

1+053

600

500

500

1x8

Highway 19

EP0599.03

REC3173

REC0303

REC0303

REC3173

200

300

400

500

600

700

600

200

300

200

300

200

300

200

200

200

300

200

200

300

400

315,100 315,200

315,300

315,300

315,400

315,400

315,500

315,500

315,600

315,600

315,700

315,700

315,800

315,800

315,900

315,900

316,000

316,000

316,100

316,100

316,200

316,200

316,300

316,300

316,400

316,400

316,500

316,500

316,600

316,600

316,700

316,700

316,800

316,800

316,900

316,900

317,000

317,000

317,100

317,100

317,200

317,200

317,300

317,300

317,400

317,400

317,500

317,500

317,600

317,600

317,700

317,700

317,800

317,800

317,900

317,900

318,000

318,000

318,100

318,100

318,200

318,200

318,300

318,300

318,400

318,400

318,500

318,500

318,600

318,600

318,700

318,700

318,800

318,800

318,900

318,900

319,000

319,000

319,100

319,100

319,200

319,200

319,300

319,300

319,400

319,400

319,500 319,600

5,56

6,40

05,

566,

500

5,56

6,60

0

5,56

6,60

0

5,56

6,70

0

5,56

6,70

0

5,56

6,80

0

5,56

6,80

0

5,56

6,90

0

5,56

6,90

0

5,56

7,00

0

5,56

7,00

0

5,56

7,10

0

5,56

7,10

0

5,56

7,20

0

5,56

7,20

0

5,56

7,30

0

5,56

7,30

0

5,56

7,40

0

5,56

7,40

0

5,56

7,50

0

5,56

7,50

0

5,56

7,60

0

5,56

7,60

0

5,56

7,70

0

5,56

7,70

0

5,56

7,80

0

5,56

7,80

0

5,56

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0

5,56

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0

5,56

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0

5,56

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0

5,56

8,10

0

5,56

8,10

0

5,56

8,20

0

5,56

8,20

0

5,56

8,30

0

5,56

8,30

0

5,56

8,40

0

5,56

8,40

0

5,56

8,50

0

5,56

8,50

0

5,56

8,60

0

5,56

8,60

0

5,56

8,70

0

5,56

8,70

0

5,56

8,80

0

5,56

8,80

0

5,56

8,90

0

5,56

8,90

0

5,56

9,00

0

5,56

9,00

0

5,56

9,10

0

5,56

9,10

0

5,56

9,20

0

5,56

9,20

0

5,56

9,30

0

5,56

9,30

0

5,56

9,40

0

5,56

9,40

0

5,56

9,50

0

5,56

9,50

0

5,56

9,60

0

5,56

9,60

0

5,56

9,70

0

5,56

9,70

0

5,56

9,80

0

5,56

9,80

0

5,56

9,90

0

5,56

9,90

0

5,57

0,00

05,

570,

100

0 10050Meters

.Sage Mountain Resources Ltd92K023NAD 8310Coast37 AA194420CWH xm2May 20, 2011

Licensee:Reference Map:Datum:UTM Zone:Forest Region:TSA:TSB:FIZ:P.S.Y.U.:Inv. Reg.:Comp.:BGC Zone & Variant:Date:

Drafted by:

Campbell RiverForest District

Woodlot Licence W2001Roberts Lake

1:5,000

Dec.: 18°09' E (01/2011)Ann. Change 12.2' W

Terrain Stabilty ClassClass V

Class IV

Water Licence

Recreation Feature

Identified Recreation Trail

Recreation Area

Identified Recreation Resource Feature

Experimental Plot

Ungulate Winter Range

OGMA

ÑØ

ÑÕ

Resource Values

W2001

Falling Corner

Permanent Landing

Temporary Landing

Station

Culvert

Bridge

Bridge out

Turnout

Swamp

Quarry

Gate/Barrier

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!/

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S1-S4 Fish Creek

S5-S6 Creek

FSZ Fisheries Sensitive Zone

NCD non-classified Drainage

Not Classified Creek

Critical Stream Reach

Contour 20m

Wetland

Lake

Management Zone

Reserve/WTP

Block

Adjacent Woodlot

W2001

Gravel Pit

Visual Quality ObjectiveR Retention

PR Partial Retention

M Moderation

Woodlot W2002

Visual Quality ObjectiveR Retention

PR Partial Retention

M Modification

Woodlot 2001

Terrain! Hydro Line

ð Gas Line

¨ Waterline

Fertilization Area, 2010

Highway

Road, existing

Road, engineered

Road, temporary

[ [ [ [ Road, deactivated

Road, overgrown

Trail, existing

Trail, engineered

Old Railroad Grade/Old Trails

MAP 1 of 2

Western Unit

Woodlot Licence Plan Map

W2001 – Roberts Lake B

Appendix 2: Woodlot Licence Plan Map (Eastern Unit)

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W2001 WLP - British Columbia · W2001 – Roberts Lake 1 I. MANDATORY CONTENT FOR A WOODLOT LICENCE...

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Transcript of W2001 WLP - British Columbia · W2001 – Roberts Lake 1 I. MANDATORY CONTENT FOR A WOODLOT LICENCE...