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![Page 1: Resource roads in British Columbia: Environmental challenges at the site level: Use of the FREP Water Quality Effectiveness Evaluation By Dave Maloney.](https://reader037.fdocuments.in/reader037/viewer/2022110323/56649d8a5503460f94a710cc/html5/thumbnails/1.jpg)
Resource roads in British Columbia: Environmental challenges at the site level:
Use of the FREP Water Quality Effectiveness EvaluationBy Dave Maloney and Brian Carson
Cranbrook, B.C.
November 7 and 8, 2012
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AcknowledgmentsAcknowledgments
Brian CarsonBrian Carson
Les SwainLes Swain
Steve Chatwin,Steve Chatwin,
Martin CarverMartin Carver
Pierre BeaudryPierre Beaudry
FLNRO/MoE regional and district stewardship staffFLNRO/MoE regional and district stewardship staff
FLNRO Resource Practices Branch staffFLNRO Resource Practices Branch staff
For more information on the:For more information on the:FREP program - FREP program - http://www.for.gov.bc.ca/hfp/frep/
WQEE protocol - WQEE protocol - http://www.for.gov.bc.ca/hfp/frep/values/water.htm
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Background: FREP context – FRPA constructBackground: FREP context – FRPA construct
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Policy Realm
FRPA
Professional Reliance
Effectiveness Evaluation
ObjectivesCompliance
andEnforcement
Plan & Practice
Requirements
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What are Effectiveness Evaluations / What are Effectiveness Evaluations / FREP?FREP?
A program to;A program to;Determine if forest and range policies and Determine if forest and range policies and
practices are achieving government’s objectivespractices are achieving government’s objectivesAssess the effectiveness of legislationAssess the effectiveness of legislationIdentify continuous improvement opportunitiesIdentify continuous improvement opportunities
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How does it work?How does it work?
Protocols guide the collection of dataProtocols guide the collection of data
Ministry staff collect and analyze the field dataMinistry staff collect and analyze the field data
Results are reported outResults are reported out
Guidance is provided if necessaryGuidance is provided if necessary
Policy changed if requiredPolicy changed if required
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Question:
Are forest and range practices effective in protecting water quality for fish habitat and drinking water purposes
Evaluate:
Effects of forestry and range - score
Identify:
Mitigation strategies
Water Quality Effectiveness Evaluation
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Characteristics of the Water Quality Methodology
Simple
Fast (20-30 minutes per site)
Repeatable (two different evaluators working independently will come up with same answer)
Able to address a wide range of terrain characteristics that occur throughout most Forest Regions of B.C
Provide recommendations for better management
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While geoscientists and regulators have been quick to recognize and study landslides as a source of turbidity, there has been less attention paid to surface erosion , which can have a substantial effect on water quality. In community watersheds, with ever more stringent levels of sediment tolerance, all sediment sources must be considered.
100 m3 fine sediment over one storm 5 m3 over one
hauling season
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The WQ protocol answers 4 simple The WQ protocol answers 4 simple questions associated with a questions associated with a
“disturbed” site“disturbed” site..
1.1. Does the road/site generate Does the road/site generate sediment?sediment?
2.2. How much sediment?How much sediment?
3.3. Does the road/site generated Does the road/site generated sediment reach the stream?sediment reach the stream?
4.4. How would you prioritize How would you prioritize road/site management activities road/site management activities to reduce water quality impacts to reduce water quality impacts from sediment?from sediment?
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Most sediment is generated where industrial roads are located over or in proximity to natural drainage ways
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Stream Crossings
Concentrated road drainage adjacent to creek
Blowdown in riparian zone
Range activities upstream of domestic water intakes
Mass wasting associated with forest and range activities
The following sites are assessed
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Once a sample sites has been selected, the Once a sample sites has been selected, the evaluator determines its drainage contributing evaluator determines its drainage contributing area and the individual components that would area and the individual components that would
contribute runoff and sedimentcontribute runoff and sediment
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WQEE Form WQEE Form #2#2
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Left cutbank
Right road surface,
Left road surface
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?OR
The Evaluator estimates the connectivity or portion of The Evaluator estimates the connectivity or portion of drainage produced on the site that will reach a natural drainage produced on the site that will reach a natural drainage. drainage. This will depend on area of catchment and potential for re-This will depend on area of catchment and potential for re-absorption of storm flow.absorption of storm flow.
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The Evaluator then estimates the portion of fine sand, silt and clay in eroded/ erodible material
0.5
1.0
0.2
Glaciofluvial terraceAblation Till
Lacustrine
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When observed within the sampling area, volumes of newly failed slopes (or recently incised gullys) are estimated along with the portion reaching a stream
Width
DepthLength
Estimated 20 % of slide material reaches Creek
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Estimating the depth of surface erosion expected on road surfaces considers degree of use, slope and quality of surfacing material (units in meters)
Road Use2-10% slope
Road Surfacing Quality
Paved or Coarse Ballast only
Good Average Poor
Heavy use , all season road
0 0.002 0.005 0.01
Moderate use, all season road
0 0.001 0.002 0.005
Light seasonal use (4 x4 and occasional logging truck)
0 0.0005 0.001 0.002
Deactivated (and unused)
0 0.0002 0.0005 0.001
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0.25 m3/year
0 m3 /year
0.50 m3/year
0 m3 /year
Left Road ditch
Stream Crossing site (left bank)Stream Crossing site (left bank)
Total estimated annual sediment contribution to stream from this site = 0.75 m3 per year
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Volume of Fine Sediment (m3)
Score Description of Site Associated Level of Management
<0.2 m3 Very Low Site does not generate significant amounts of sediment. Site reflects best management practices. Good
Poor
0.2-1 m3 Low Site generating some sediment but would still be within the range that would be considered normal for background levels of stream turbidity. Site reflects good management practices
1-5 m3 Moderate Site generating levels of sedimentation that would be measurable and, under special situations, of interest to watershed managers. Improvements could be considered but are not mandatory.
5-20 m3 High Site generating unacceptable levels of fine sediment and have a significant impact on water quality in a watershed. Action mandatory.
>20 m3 Very High Site very high levels of sediment with major consequences for water quality within a watershed. Action Mandatory.
[1] Note that an increase in discharge of receiving waters will result in a decrease in the magnitude of the turbidity effect .
Scoring
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Management option to reduce sediment generationManagement option to reduce sediment generation
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Results
2008-20112008-2011
•785 cutblocks785 cutblocks
•3423 assessments3423 assessments
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Roads paralleling stream
(usually old alignments)
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Too large an area drained by culvert
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Long grade approach to bridge with rutted road surface carrying surface water onto bridge
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Road surface generated discharge is concentrated rather than diffused from road alignment
Permitting large grader berms that Permitting large grader berms that concentrate water generated on road towards concentrate water generated on road towards
natural drainagesnatural drainages
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Designing swale in road before bridge so surface water diverted before reaching stream
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Building bridge slightly above road grade and armour disturbed soils subject to concentrated flow
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Using coarse material for road surfacing
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Armouring culvert outlet and areas where concentrated surface flow is expected
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Ensure windfirm trees within riparian reserve zone
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Minimizing disturbance of S5 and S6 stream
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Reseeding reclamation mix on areas with disturbed soils
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Using temporary and permanent water Using temporary and permanent water barsbars
Surface water is deflected off road before it has a chance to concentrate
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Staying off roads when wet
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Using signage to indicate sensitive stretches of road
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Introduce stream discharge: Receiving waters have different rates of discharge, and the dilution effect will vary proportionally
0.1 m3/sec 10 m3 / sec
1 m3 of fine sediment delivered to this stream will raise the turbidity by 10 NTU.
1 m3 of fine sediment delivered to this stream will raise the turbidity by 0.1NTU.
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Severity of ill effectsSeverity of ill effects
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Thank you