after June 15, 1996, slope gradient of less than 20% and flows directly into fish
stream, Pacific Ocean, or lake known to support fish.
- High value fish-bearing stream
- A stream identified as a high value fish-bearing stream for the purposes of sections 225(3)(a) and 226(3)(a) of the Act.
- High value stream
- A high value-fish-bearing stream, and a stream in a community watershed. Identified threatened or endangered fish. Threatened or endangered fish species as determined by Deputy Minister (MELP), and as identified by Deputy Minister (MELP) and chief forester. Known information identified by inventories or assessments contained in higher level plans, or made available by government a minimum of 4 months before submission of operational plan.
- Lake class
- Designation by DM for lakes with riparian class of LI that indicates width of lakeshore management zone and allowable practices within zone.
- Lakeshore management area (LMA)
- Area established adjacent to lake with riparian class of L1, consisting of riparian reserve
zone and lakeshore management zone.
- Lakeshore management zone
- Portion of LMA established by DM around lake with riparian class of LI that is outside
any riparian reserve zone or, if there is no reserve zone, adjacent to lake.
- Marine sensitive zone
- Herring spawning areas, shellfish beds, marsh areas, aquaculture sites, juvenile
salmonid rearing areas and adult salmon holding areas.
- Riparian management area (RMA)
- Area adjacent to a lake with a riparian class of L2, L3 or L4. Area consisting of riparian reserve zone, if any, and riparian management zone.
- Riparian management zone
- Portion of RMA outside of riparian reserve zone or, if there is no reserve zone, adjacent
to stream, wetland or lake.
- Riparian reserve zone
- Portion of RMA or LMA located adjacent to stream, wetland or lake. Safe passage of fish through culverts for the purposes of spawning, rearing or migration.
- Stream culvert
- Culvert used to carry stream flow in an ephemeral or perennial stream channel from one
side of the road to the other.
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Operational Plan Notice, Review and Comment Requirements
(Operational Planning Regulation)
Review and comment [s 4(6-8)]
Before a SP is submitted for approval, make the following available for review and
comment:
- cultural heritage impact assessments,
- visual impact assessments,
- classification of streams, wetlands and lakes, and
- terrain stability assessments.
Before roads under a FDP or AMP are constructed or modified, make available for
public review and comment the results of cultural heritage impact assessments, visual
impact assessments, and classification of streams, wetlands and lakes.
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Plan Content and Development Requirements for Riparian Management
(Operational Planning Regulation)
FDP [s 15(6)(c), s 28]
Assessment of riparian class for streams, wetland and lakes.
Longer term FDP (after first 5 years) [s 16(b)(iv)]
Known riparian class for streams, wetlands and lakes.
LP [s 33(3)(b-c)(e)(g)(i)]
For streams and wetlands:
- width of riparian reserve zone,
- width of riparian management zones.
For lakes:
- riparian class,
- known lake class,
- width of lakeshore management zone or riparian management zone.
Timing of any in-stream operations.
If harvesting proposed for areas adjacent to streams and wetlands, strategies for:
- felling, yarding and debris management, and
- protecting the streambank and minimizing damage to understory.
SP [s 39(3)(b)(c)]
SMP [s 54(2)(a)(b)]
For streams and wetlands:
- riparian class,
- riparian reserve zone,
- riparian management zone,
- proposed forest practices for reserve zone and management zone.
For lakes:
- riparian class,
- known lake class,
- riparian reserve zone,
- width of lakeshore management zone,
- width of riparian management zone,
- proposed forest practices for reserve zone and management zones.
AMP [s 62(3)(c)(d)]
Assessment of riparian class for streams, wetlands and lakes.
Classification of lakes, provided by the DM. RUPs for grazing
[s 69(1)(i)(k)(i)]
Strategies for wetlands and riparian areas. Measures to prevent destabilization of streambanks and lakeshores by livestock.
LP [s34(2-3)]
Landings must not be located within 30 m of a streambank;
DM may waive this requirement if:
- there is no other practicable location for the landing; and,
- locating the landing closer to the stream will not create a high risk of sediment delivery to the stream.
LP [s 35]
Proposed location and design of stream crossings must:
- protect stream channel and streambank immediately above and below stream crossing; and
- minimize any disturbance to stream channel or streambank.
SP [s 44]
Only remove or modify trees from riparian reserve zone for:
- recovery of windthrown or damaged trees*,
- sanitation treatments*,
- recreational facility management,
- managing fisheries and wildlife values*,
- reducing windthrow potential by topping/pruning;
- full suspension yarding corridors,
- removal of danger trees, or,
- any other similar activity*;
Removing or modifying trees for (*) purposes requires approval of DEO.
SP [s 45]
Retain sufficient numbers and distribution of trees along:
- class S4, S5, or S6 streams,
- streams which are direct tributaries to S1, S2, or S3 streams, or
- streams flowing directly into a marine-sensitive zone
to maintain stream bank or channel stability, or shade over temperature sensitive
streams.
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Establishing RMA Class and Widths
(Operational Planning Regulation)
STREAMS [s 72, 73]:
RMA Stream Criteria Reserve Mgmt. RMA
Class Width (m) Zone Zone Total
S1 > 20 fisheries stream 50 20 70
community watershed 50 20 70
S2 5 - 20 fisheries stream 30 20 50
community watershed 30 20 50
S3 1.5 - 5 fisheries stream 20 20 40
community watershed 20 20 40
S4 < 1.5 fisheries stream 0 30 30
community watershed 0 30 30
S5 > 3 non fish bearing stream 0 30 30
S6 <= 3 non fish bearing stream 0 20 20
If a stream has, on average:
- over a 1 km length,
- a channel width of 100 m. or greater, and
- an active floodplain width of 100 m. or greater,
the stream has no reserve zone, but has a management zone of 100 m. or the width of the active flood plan, whichever is greater.
For these streams, DM, with agreement of DEO, may require a reserve zone.
DM, with agreement of DEO, may vary the width of reserve zone or management zone for any stream or
portion of stream.
If DM, with agreement of DEO, proposes to vary the width of reserve zone or management zone or requires a reserve zone in an area located within the boundaries of a claim, lease, or permit under the Coal Act, Geothermal Resources Act, or Mineral Tenure Act, agreement of a DEMPRO is required.
WETLANDS [s74, 75]:
RMA Wetland Criteria Reserve Mgmt. RMA
Class Size(h)
W1 > 5 n/a 10 40 50
W2 1-5 Within following biogeoclimatic zones:
ponderosa pine 10 20 30
bunch grass 10 20 30
interior douglas fir 10 20 30
(very dry hot, very dry warm,
or very dry mild)
coastal douglas fir 10 20 30
coastal western hemlock 10 20 30
(very dry maritime, dry maritime
or dry submaritime)
W3 1-5 Within biogeoclimatic zones other 0 30 30
than those of W2
W4 0.25-1 Within following biogeoclimatic zones:
ponderosa pine 0 30 30
bunch grass 0 30 30
interior douglas fir 0 30 30
(very dry hot, very dry warm,
or very dry mild)
0.5-1 Within following biogeoclimatic zones:
coastal douglas fir 0 30 30
coastal western hemlock
(very dry maritime, dry maritime,
or dry submaritime)
W5 >= 5 consists of 2 or more
individual wetlands with 10 40 50
overlapping RMAs
- Upland terrain within a bog dominated or muskeg dominated wetland larger than 1000 ha in boreal, subboreal or hyper maritime climates does not require a reserve zone or management zone; the DM, with agreement of DEO, may require a reserve zone or management zone.
- District manager, with agreement of DEO, may vary widths of any reserve zone and management zone.
- If the DM, with agreement of DEO, proposes to vary the width of reserve zone or management zone or requires a reserve zone in an area located within the boundaries of a claim, lease, or permit under the Coal Act, Geothermal Resources Act, or Mineral Tenure Act, agreement of a DEMPRO is required.
LAKES [s 76, 77]:
RMA LAKE CRITERIA RESERVE MGMT RMA
CLASS SIZE(h) ZONE(m) Zone(m) TOTAL(m)
L1 > 5 > 5 ha. or so designated 10 established RZ + MZ
by the district manager. by DM
L2 1 - 5 Within the following
biogeoclimatic zones:
ponderosa pine 10 20 30
bunch grass 10 20 30
interior douglas fir 10 20 30
(very dry hot, very
dry warm, or very dry mild)
coastal douglas fir 10 20 30
coastal western hemlock 10 20 30
(very dry maritime, dry
maritime or dry submaritime)
L3 1 - 5 Within biogeoclimatic 0 30 30
zones other than
those for L2
L4 0.25 - 1 Within the following
biogeoclimatic zones:
ponderosa pine 0 30 30
bunch grass 0 30 30
interior douglas fir 0 30 30
(very dry hot, very dry
warm,or very dry mild)
L5 0.5 - 1 Within the following
biogeoclimatic zones:
coastal douglas fir 0 30 30
coastal western hemlock 0 30 30
(very dry maritime, dry
maritime or dry submaritime)
A lake greater than 1000 ha. does not require a reserve zone; the DM, with agreement of DEO, may require a reserve zone.
The DM, with agreement of DEO, may vary reserve zone or management zone widths of any lake or portion of a lake.
If the DM, with agreement of DEO, proposes to vary the width of the reserve zone or management zone or requires a reserve zone in an area located within the boundaries of a claim, lease, or permit under the Coal Act, Geothermal Resources Act, or Mineral Tenure Act, agreement of a DEMPRO is required.
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Timber Harvesting Practices Requirements
(Timber Harvesting Practices Regulation)
Marking reserve zones and management zones for streams, wetlands and lakes [s 5]
- Mark outer boundary of riparian reserve zones, and riparian management zones if
proposed operations for the zone are significantly different than that of the adjacent
portion of the cutblock.
- The DM may waive these requirements if operations are restricted to minor salvage.
Felling [s 7]
Do not fell timber onto a stream, lake, wetland, marine-sensitive zone or fisheries-
sensitive zone, unless it is the only practical way to fell the timber, or a logging plan
allows it. If LP not required, the DM may waive these requirements and place other
conditions on licensee.
Yarding and skidding [s 8]
Timber must not be yarded or skidded through or over streams or fisheries-sensitive
zones unless authorized in a LP. If LP not required, DM may waive these requirements
and place other conditions on licensee.
Maintaining streambank stability [s 11]
Do not remove stable, natural material in streams or embedded in streambanks, or root
systems that contribute to streambank stability and fish habitat unless a LP allows it.
Restriction of stream crossings and instream operations [s 13]
If LP not required, locate and design stream crossings so they protect stream channels
and streambanks immediately above and below stream crossings, and mitigate
disturbance to stream channels and streambanks.
Carry out construction, repair or removal of stream crossings and other in-stream
operations in accordance with timing windows and terms set by resource agencies and
approved by the DM.
Retention of streamside trees [s 14]
If LP not required, maintain along fish or community watershed streams less than 1.5 m
wide (and their tributaries) sufficient numbers and distribution of trees which provide or
contribute significantly to maintaining streambank or channel stability, or shade
necessary for fish and water quality.
Constraining slash and debris in and around aquatic environments [s 15]
Do not deposit harmful amounts of slash or debris where it could be transported into:
- lake,
- wetland,
- fisheries-sensitive zone or a marine-sensitive zone,
- fish stream or stream with known downstream domestic water users, or
- unstable gully or stream capable of transporting debris, and which is direct tributary to above waterways.
Restricted operation of machinery [s 16]
When carrying out harvesting, do not permit ground-based machinery within 5 m of a
streambank except:
- for carrying out fire fighting activities,
- in response to natural disasters,
- at stream crossings authorized by district manager, or
- if operations protect streambanks and minimize damage to understory vegetation.
DM may exempt this requirement if:
- machinery is operated
- to construct/maintain a range development or utility,
- to construct/maintain a work or to carry out activity within or adjacent to streams
- for purpose of controlling surface soil erosion, protecting streambanks, or managing fisheries or wildlife, or
- for a similar activity; or
- DM agrees
- no other practical option exists for carrying out operation, or
- operating machinery more than 5 m from streambank will create higher risk of sediment delivery.
Machinery must not be fueled or serviced within a RMA or LMA other than machinery that is:
- hand-held,
- required for fire-fighting,
- broken down and requires fueling or servicing to be moved,
- authorized in a LP to be fueled/serviced in area, or
- in absense of LP, authorized by DM to be fueled/serviced in area.
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Silviculture Practices Requirements
(Silviculture Practices Regulation)
Use of livestock [s 3(a)(c)]
If livestock are to be used for site preparation or brush control, take measures to protect
fish, wildlife and their habitat.
If livestock are used for site preparation and brush control, do not construct livestock
corrals within a RMA, or on a site that drains directly into a stream, lake or other
watercourse bearing fish or used as a potable water source.
Use of livestock in a RMA of a community watershed [s 4]
Do not use livestock to carry out site preparation or brush control within a RMA.
Pesticide restricted zone around streams in a community watershed [s 10]
Maintain a 10 m pesticide free zone around all streams in community watersheds.
Restricted operation of machinery [s 28]
When carrying out a silviculture treatment, ground-based machinery is not permitted
within 5 m of a streambank except under certain circumstances.
Refer to Timber Harvesting Regulation, s 16, except: fueling and servicing may be allowed if authorized under SP.
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Range Practices Requirements
(Range Practices Regulation)
Restrictions on location of range developments in a community watershed [s 3]
Do not construct within a community watershed:
- a range development that would encourage livestock to use an area within 50 m of a stream,
- a stream crossing of a livestock trail unless approved by DM,
- a cabin within 50 m of a stream, or
- a livestock corral within 50 m of a stream.
Restricted operation of machinery [s 6]
When carrying out an activity under a Range Act agreement, do not permit ground-
based machinery within 5 m of a streambank except under certain circumstances. Refer
to Timber Harvesting Regulation, s 16, except:
- add "if machinery is operated for livestock management" to list of reasons DM may exempt requirement; and,
- fueling and servicing may be allowed if authorized under a Range Act agreement.
Livestock in a community watershed [s 7(3)(4)]
Do not use livestock in a riparian area of a community watershed if it results in fecal
deposits, trampling of vegetation, or detrimental exposure of mineral soil.
If dead livestock are discovered less than 100 m from a community watershed stream,
they must be moved within 24 hours.
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Road Design, Construction, Maintenance and Deactivation Practices
(Forest Road Regulation)
Selecting road location [s 3(2)(3)]
Locate roads outside a RMA, except for crossings, unless the DM agrees no other practical option exists, or locating the road outside the RMA will create a higher risk to sediment delivery.
Site data for watercourse crossings [s 6(1)(2)(a-d)]
For road layout and design, collect the following site data for proposed bridges and
major culverts:
- riparian class for streams or lakes,
- high water mark of water body,
- stream flow velocity and direction, and,
- description of waterbody bed materials.
Drainage design [s 8(1)(a)(c)(ii)(f)]
For drainage design specifications, include measures for:
- crossings of fish streams that provide safe passage for fish,
- bridges and culverts that prevent or mitigate channel/bank disturbance, and
- culverts that maintain stability of stream channel on all streams.
Road site preparation [10(1)(c)(6)(a-b)]
When clearing the clearing width of a road in areas where felled trees could reach
streams or lakes:
- directionally fell trees away from the stream or lake, and
- use felling and yarding methods that prevent streambank from destabilizing.
Do not deposit slash and debris into a watercourse, or onto an area where the material
could be transported to a watercourse.
Subgrade construction or modification[s 11(1)(e)(i-m)(6) (7)]
When constructing or modifying the subgrade of the road:
- locate borrow pits, quarries, waste areas and endhaul disposal sites in areas where eroded soil
- materials or other harmful materials will not entering streams;
- protect fill that might otherwise erode if it is located on the active flood plain of a stream;
- do not cross the stream with equipment at more than one location within the clearing width, unless authorized by the DM;
- Do not place ground-based equipment within 5 m of a streambank, unless:
- required for habitat restoration work,
- at a designed crossing site, or
- the DM agrees that:
- no other practical option exists, or
- locating the road more than 5 m from the streambank will create a higher risk of sediment delivery;
- remove gravel or fill from RMAs only with the approval of the DM and DEO;
- Do not fuel or service equipment within a RMA unless
- the equipment is hand held, or
- the fueling or servicing is:
- required for carrying out fire fighting activities,
- required to move broken down equipment, or
- authorized by the DM.
If, when constructing or modifying a road, a previously unidentified fisheries-sensitive
zone is found, stop or modify the activity that is in the immediate vicinity to the extent
necessary to not threaten it;
The DM need not be advised of the presence of the zone.
Drainage construction [s 12(1)(g-h)(m)]
When constructing a drainage system for a road:
- construct bridges and culverts to prevent or mitigate streambank disturbance and to avoid adversely affecting downstream water quality;
- construct crossings in fish streams at a time and in a way that provides safe fish passage and protects fish habitat immediately upstream and downstream of the structure; and,
- provide bridge or culvert material storage and equipment turnaround sites outside RMAs identified in operational plans if the normal clearing width cannot accommodate the sites.
Road inspection and maintenance [s 17(2)(a)]
Carry out road maintenance inspections at a frequency that takes into account the risk to
fish streams caused by the road's proximity to the streams.
Permanent deactivation [22(1)(a-b)]
When carrying out permanent deactivation of a road:
- remove existing stream culverts and restore channel and bank stability; and,
- if overflow of the stream channel is expected, back up stream culvert excavations with similarly sized cross-ditches on the downhill side.
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Cutblock and Road Review Regulation
Riparian reserve zones [s 5]
High value streams located in or immediately adjacent to cutblocks subject to a silviculture prescription or roads subject to a cutting or road permit submitted before June 15 1995 must have the following reserve zones:
Stream (m) Reserve (m)
>20 30
7-20 20
1.5-7 10
High value streams located in or immediately adjacent to cutblocks subject to a silviculture
prescription or roads subject to a cutting or road permit submitted after June 15 1995 must
have the following reserve and management zones:
Stream (m) Reserve (m) Management (m)
>20 50 20
5-20 30 20
1.5-5 20 20
<1.5 0 30
Under cutblock and road authorities, timber harvesting or road construction must not be
permitted in a riparian reserve zone (except for road construction at designated stream
crossings specified in an operational plan).
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Guidebooks and other relevant documents
Riparian Management Areas Guidebook
Fish Stream Identification Guidebook
Lake Classification and Lakeshore Management Guidebook
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For more information contact:
Ministry of Forests
Integrated Resources Policy Branch
1483 Douglas Street,
Victoria B.C.
V8W 2E7
Any comments? Send to Ben Chatterson (bechatte@mfor01.gov.bc.ca)
Last modified April 23, 1996