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Basinwide Visual Estimation Technique BVET

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Presentation on theme: "Basinwide Visual Estimation Technique BVET"— Presentation transcript:

1 Basinwide Visual Estimation Technique BVET
2015

2 What is BVET? Stream habitat inventory method A two-stage technique
Hankin and Reeves (1988) Dolloff et al. (1993) A two-stage technique visual estimates & measurements Products calibrated estimate of stream area inventory of habitat attributes

3 BVET Basics Visual estimates in every habitat unit
Pool Riffle Visual estimates in every habitat unit Measurements at pre-determined intervals

4 BVET Habitat: 5 Steps Complete ‘header information’
Select random number & measurement interval Walk upstream, stopping to record estimates at upstream end of each habitat unit At randomly selected unit perform visual estimates, then measurements (paired sample unit) Proceed upstream estimating in every unit and measuring at pre-determined interval Repeat steps 4 and 5 until stream end is reached

5 Step 1: Header Information
Stream: Full stream name per USGS quad map District: Forest Service District name Quad: Name of USGS 1:24,000 quadrangle on which survey start point is located Date: Record start date of survey Recorder & Observer: Full names – no ab. DO NOT change mid-survey Start GPS: Map datum = NAD83 CONUS Coordinate System = UTM Start location: Detailed written description of starting point Notes: Signs of human activity, water condition, weather, hazards, etc.

6 Header Information on iPad

7 Step 2: Random Number & Interval
Stream < 1.0 km Measure every 5th unit Random # 1-5 ex) random number = 3 Paired sample at 3, 8, 13, 18, 23, etc. Stream > 1.0 km Measure every 10th unit Random # 1-10 ex) random number = 3 Paired sample at 3, 13, 23, 33, 43, etc. Need a minimum of 3 fast water, 3 slow water pairs More paired samples = smaller confidence intervals

8 Step 3: Estimates for all units
Habitat Type & Number Distance Estimated Width Depth Substrate Percent Fines Large Wood Hemlock Large Wood

9 1. Five Habitat Unit Types
Fast water Turbulent 1. Riffle: <12% gradient 2. Cascade: >12% gradient flat to convex bottom Non-Turbulent 3. Run <12% gradient flat bottom Slow water Turbulent or Non-Turbulent 4. Pool concave bottom Non-Turbulent 5. Glide flat bottom Special situation Underground: dry channel

10 Fast Water Riffle Run Cascade

11 Fast Water

12 Slow Water Pools Glides

13 Slow Water

14 Unit breaks - clear Riffle Pool Riffle Pool

15 Unit breaks - fuzzy Riffle Glide

16 Unit Number Group slow water: (pools & glides)
Group fast water: (riffles, runs, & cascades) riffle run cascade pool glide P1 G2 P3 P4 G5 G6 P7 R1 R5 C4 R2 RN3 R6 Quick quiz: Random number is 5: Where are 1st fast water and slow water paired samples?

17 2. Distance Meters from start of survey to upstream end of unit
Measured with a hipchain P2: 29.3 P1: 10.2 R1: 22.3

18 Hipchain

19 3. Estimated Width Average Wetted Width Take entire unit into account
P2: 3.0 P1: 2.5 R1: 1.5

20 4. Depths Maximum Depth Average Depth Deepest point
Average of several points Change to units

21 Riffle Crest Depth Measure at upstream end of FAST leading into SLOW; record in FAST data

22 Measuring crest depth Add rc line

23 5. Substrate Dominant Subdominant 9 size classes
Covers most surface area in unit Subdominant Covers second most surface area in unit 9 size classes

24 Substrate Size Classes
1. Organic dead organics 2. Clay sticky 3. Silt slippery 4. Sand silt- 2mm gritty 5. Small Gravel 3-16mm sand to fingernail 6. Large Gravel 17-64mm fingernail to fist 7. Cobble mm fist to head 8. Boulder >256mm bigger than head 9. Bedrock solid rock

25 How to measure substrate
Substrate size classifications are based on the b-axis or the second longest axis A A= longest axis C= shortest axis B C Quick quiz: Identify the three axis positions

26 6. Percent Fines Percent of total area covered by sand, silt, or clay

27 7. Large Wood (LW) Dead, down, and within bankfull channel
>1.0 m long, >10 cm diameter Four size classes 1. <5 m long, cm diameter 2. <5 m long, >55 cm diameter 3. >5 m long, cm diameter 4. >5 m long, >55 cm diameter Rootwad – count separately from attached LW

28 8. Hemlock Large Wood (LW)
Identifiable as hemlock Already counted in LW Data; this is a separate count of only Hemlock Dead, down, and within bankfull channel >1.0 m long, >10 cm diameter Combine all 4 size classes

29 LW quick quiz:

30 Congratulations! You know what to estimate in every unit What’s next??
Paired Samples

31 Step 4: Paired samples Every paired pool Every paired riffle
Actual wetted width Every paired riffle Hemlock abundance Hemlock condition Measured Widths Bankfull channel width (& Avg. bankfull depth) Riparian width (left & right) Gradient Rosgen Water temperature Photo

32 1. Hemlock Abundance Estimate the total number of standing hemlocks (live or dead with DBH >10 cm) in the riparian zone (water’s edge to 30 m up the streambank; visually estimated) as you walk between paired sample units None = no hemlocks Few = 1-10 Some = 1-50 Many = >50 hemlocks

33 2. Hemlock Condition Estimate the condition of standing hemlock trees in the riparian zone as you walk between paired sample units Healthy/Light Infestation (0-25% needle loss) Infested (25-75% needle loss) Dead (>75% needle loss)

34 3a. Actual (measured) Width
Average wetted width Measure with a tape measure Measure in at least three locations

35 3b&c. Bankfull Channel & Riparian Widths
Bankfull channel width bankfull to bankfull Riparian Width 2-times maximum bankfull depth to landform (flood depth)

36 3b&c. Channel and Riparian Widths
Left Riparian Width Bankfull Channel Width Right Riparian Width 2X Max Bankfull Depth

37 Riparian width measurement

38 4. Gradient Percent slope of the water surface
Measure with a clinometer Riffles, runs, cascades

39 Be careful measuring gradient

40 5. Rosgen

41 6. Water Temperature Place thermometer in flowing water
Out of direct sunlight if possible Record at measured riffles

42 BVET review Visual estimates in every habitat unit
Measurements at pre-determined intervals

43 Stream Features Waterfalls, Dams, Roads, Trails, etc.
Serve as landmarks Record distance, GPS, DETAILED description See features in manual for details

44 7. Photos Face upstream Use wading rod for scale Get a wide angle
Take at paired fast water units and features/crossings BAD – can’t see channel GOOD – can see channel

45 GPS Waypoint Labels S## Start location P## Pause location
S## Start location P## Pause location E## End location T##b Tributary with name shown on quad map W##b Waterfall B##b Bridge Fd##b Ford D##b Dam V##b Culvert O##b Other ## = digits of stream ID b = use b, c, d, etc to create unique labels when additional waypoints on the same stream are needed

46 Ending the Survey Stop when you reach Record At home base
Property boundary Dry stream for > 500 m Channel < 1.0 m wide for > 500 m Record Time and date Reason for stopping GPS coordinates and written description Be sure header info completed At home base Back-up data Record on master list/map that survey is complete Download GPS


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