Experiential Science Projects
  • Projects
    • Use and Curriculum fits
  • Aquatic
    • Study area
    • Spook Creek >
      • Spook Creek, hydrocarbons
      • Spook Creek: E-coli from Walmart
      • Spook Creek: Impacts of filling a wetland
      • Spook Creek: Oil storage and pollution
      • Spook Creek: Envirothon
    • Porter Creek >
      • Porter Creek, green belt, subdivision,
      • Porter Creek Water Board Interventions
      • Porter Creek: Stream shape
      • Porter Creek: ground water
    • Hidden Lake >
      • Hidden Lake Water Balance
      • Hidden Lake Algael Bloom
      • Hidden Lake: Fish Escapes
    • McIntyre Creek >
      • McIntyre Creek: Subdivision proposal
      • McIntyre Creek: Salmon Spawn
      • McIntyre Creek: Interpretation trail
    • Yukon River >
      • Yukon River: Rock the River
      • Yukon River: Structure of standing waves
    • Ibex River >
      • Ibex River: Salmon restortation
      • Ibex River: Environmental Monitoring
      • Ibex River: In Stream Incubators
    • Ford Lake >
      • Ford Lake: Water Balance
      • Ford Lake: Wetland drainage
      • Ford Lake: Red Winged Balckbird Census
    • Cowley Lake >
      • Cowley Lake: Bathometric Survey
      • Cowley Lake: Water level, balance
      • Cowley Lake: Community projects
      • Cowley Lake: Paleoliminology
    • Marwell Creek >
      • Marwell Creek: Salt Deposited with Winter Snow
      • Marwell Creek: Hydrocarbons and aquatic quality
      • Marwell Creek: Escarpment and Hertiage
    • Takhini River >
      • Takhini River: Recreation impacts
      • Takhini River: Salmon Spawn areas
    • Estuary studies >
      • Ganges Creek Estuary
      • Campbell River estury health
  • Terrestrial
    • Haines Junction Forestry >
      • Haines Junction Forestry: Seedling growth
      • Haines Junction Forestry: Fire regeneration
      • Haines Junction Forestry: Bais in measurement
      • Haines Junction Forestry: Blow-down at clearcut margins
      • Haines Junction Forestry: natural seedlings
      • Haines Junction Forestry: Spruce beetle infestation
      • Haines Junction Forestry: infestation in logs
      • Haines Junction Forestry: Community involvement
      • Haines Junction Forestry: Spruce beetle trail signage
      • Haines Junction Forestry: Forest structue analysis
    • Arctic Institute >
      • Arctic Institute: Forest sturcture, hare impacts
    • Whitehorse Forestry and Terresterial studies >
      • Whitehorse Forestry: Fire regeneration
      • Whitehorse Forestry: Planting seedlings
      • Whitehorse Forestry: Phenology on Escarpment
      • Whitehorse Forestry: Plant succession in slides
      • Whitehorse Forestry: Growth rates
      • Ground cover studies in Fire Smart areas
      • Fire scar histories Dendrochronology
      • Whitehorse Forestry: EMAN plot in regen area
      • Carbon Sequestering Studies
    • Teslin Forestry >
      • Teslin Forestry: Studies of Different Harvest Practices
      • Teslin Forestry: Forest volume
    • Hinton forest structure analysis >
      • Hinton forest: Forest regen following burn or clear cut
      • Hinton forest: Harvest practices near riparian zones
    • SaltSpring Island forestry >
      • SaltSpring Island forestry: sustainable harvesy forest
      • SaltSpring Island forestry: EMAN Plot in ecological reserve
      • SaltSpring Island forestry: Deer impacts on forest regeneration
    • Prince Rupert forestry >
      • Prince Rupert forestry Seedling survival in wet soils
    • Caves >
      • Cave mapping
      • Impacts of clear cutting on caves
    • Impacts on Land >
      • Litter Analysis
      • Imacts of ATVs on non-motorized trails
      • Snowmachine trails impacts on plant growth
  • Wildlife
    • Mammals >
      • Caribou attracted to salt on the road
      • Caribou and fire smart areas
      • Caribou use of a potential development area
      • Hare census by turd counts
      • Hare impact on seedling survival
      • Deer impacts on seedling regeneration
      • Moose brows census
      • Red Squirrel territories
      • Mice and genetics
    • Birds >
      • Museum preparation of bird samples
      • Woodpecker use of beetle killed forest
      • Sea bird census while sailing
      • Red-winged Blackbird Census
      • Bird banding with mist nets
    • Fish >
      • Salmon growth rates and food conversion: Automatic feesders
      • Salmon fry and complex river systems
      • Mapping redds on the Ibex
      • Char escapes on Porter Creek/ Hidden Lake
      • Trout populations on Long Lake
    • Insects >
      • Aquatic Invertebrate populations analysis
      • Water quality through aquatic invertebrate populations
      • Mosquitoe life cycle
    • Frogs >
      • Spotted Frog Census
    • Wildlife study protocols >
      • Motion activated camers
      • Indirect counts: plants, turds, tracks etc
      • Frog identification protocols
      • Radio collar tracking
      • Mark Recapture protocols
  • Marine
    • Intertidal studies >
      • Intertidal monitoring through shorekeepers
      • Intertidal monitoring: Mapping results on Google Earth
      • Inventory of marine intertidal organizims
    • Sub tidal studies >
      • Fish diversity counts while diving
      • Anemone census while diving
      • sea star census while diving
    • Marine populations >
      • Shore crab mark recapture census
      • Varnish clam census
      • Barnnacle census on rocky shorelines
      • Oyster spat growth and setting medimum
      • Tidal marine aquarium
    • Ocean Impacts >
      • Benthoic samples under booming areas and in open areas
      • Planton drags and population counts
    • Shoreline inventories >
      • Drift wood seasonal changesd
      • Plastic in drift wood piles
    • Fish studies >
      • Salmon fry and sea lice
      • Gee traps for salmon fry
      • Salmon enhancement processes
      • Campbell River complex for salmon habitat
    • Ocean dynamics >
      • Character of high energy shorelines
      • Character of protected shorelines
      • Long shore drift studies
  • Atmosphere
    • Air quality >
      • Air quality in Riverdale with inversions
      • PM 10 meter use
      • Ozone measurements
    • Atmospheris dynamics >
      • Charting air mass movements from weather data
      • Recording pressure changes driving from Skagway to Fraser
    • Measurments >
      • Establishing a school weather station
      • Data logging seasonal temperature records
  • Snow
    • Snow Profiles >
      • Snow profile measurements: stability
      • Snow profile measurements: subniven habitats
      • Snow profile measurements: Hydrology
      • Snow profile measurements: Seasonal event history
    • Snow habitat >
      • Track records: Caribou activity
      • Subniven small mammal tracking
      • Insects in snow
      • Winter track preservation
    • Snow characteristics >
      • Snow crystal structures
      • Snow sintering following disturbance: Quinzees
      • Altering metamorphism in snow profiles
      • Keeping snow on a skill hill
    • Snow and climate >
      • Temperature varriation across snow and ground
      • Lake freeze up, break up and ice thickness
      • Seasonal snow depth and water equivelance measurements
  • Energy
    • Energy production >
      • Energy production: In-stream generator
      • Energy production: Datalogger output from a solar pannel
      • Energy production: Wind generation
    • Energy conservation >
      • Energy conservation: Intelegent parkinglot controlers
      • Energy conservation: Keeping icecubes insulation
      • Energy conservation: heat sink measurements
    • Energy diversion
  • Recreation
    • Trail use and development >
      • Escarpment trail development
      • Spruce beetle activity trail
      • Escarpment trail signage
      • Development of Yurts near Mystery Lake
    • Winter activities >
      • Ski hill packing
      • Snowshoeing after caribou
    • Fitness assessment >
      • Fittness Journal with basic standards
    • Community recreation >
      • Trail use records, motion sensors and camera
      • Environmental Impacts of recational use
    • Water activities >
      • Flow rate measurements
      • In-stream incubation boxes installed
  • Gear
    • Aquatic gear >
      • Surber samplers
      • Stream flow dynamics: flow trough
      • Flow meters
      • V notch weir on culvert
      • Aquatic invertebrate identifcation key
      • Sucker Uppers
      • Diatom Identification Key
      • Plankton Drag
      • Paleoliminology sampling under ice
    • Terrestrial Gear >
      • Forestry gear >
        • Dendrochronology core holders
        • Go-no go gagues
        • 5 and 10 meter lines
        • DBH tapes
        • Collapasable Quadrat plots from tent poles
        • Clinometers in tangent readings
    • Soils Gear
    • Marine gear >
      • Seives for fine intertidal substrates
    • Snow gear >
      • Snow profile charts
      • Snow depth sticks
      • Snow-water equivelance by weight: total
      • Snow-water equivelance by weight: layer
    • Atmosphere gear >
      • Rainfall gagues
    • Wildlife study gear
The picture to the right shows the surber sampler worked into the stream bed, in this case rocks and gravel.  The rocks are scrubbed in the screen so that  up-steam sediments and invertebrates are carried into the screen.  Clean pebbles and rocks that wash into the screen in the screen and remove the larger rocks.  In quiet waters draw the sampler through bottom sediment.  If the sediment is muddy, wash the screen multiple times to clear away most of the fine sediments, leaving the macro-invertebrates and other objects behind. 

Picture
Making and Using a Surber Sampler

A surber sampler collects macro invertebrates from shallow riffles and/or runs. Flowing water carries the invertebrates into the collecting net as the benthos is disturbed.  Obviously, samplers of different sizes can accommodate different conditions (e.g. larger samplers can be used in deeper areas, smaller samplers sometimes work better in shallow streams with low velocity).   The sampler may also be used for qualitative sampling by dragging the sampler across a pond bottom.

How to make your own surber samplers:
This will require sewing, measurements, rod bending, drilling, hacksawing and welding


Materials
32 by 82 cm silkscreen mesh with a 500 micron openings
2 inch bias tape x 100 cm and 1 inch wide bias tape
¼ inch by 100 cm coated steel rod
5/16 redirod connector

Construction steps
Bend the rod into a rectangle 33 cm wide and 15 cm deep, joining at the mid point along the top side.  Cut the rod so the two top edge pieces match.  Drill a ¼ inch hole through the mid point of the redirod connector.  The two ends of the rectangle pass through these holes and weld them in place.
Cut the silk screen into a strip 32 cm wide by 56 cm long then cut two side panels 16 x 21 cm.  Sew the two side panels onto the longer strip, forming a box 15 cm x 33cm x 20 cm with an open top.  Cover the seams with 1 inch bias tape and sew in place.  Sew an edge of the 2 inch bias tape around the open end of the box.
Fold the bias tape around the ¼ rod frame and sew back onto the screen.  This will require sliding the screen along the rod as you get to the corners.  Hand sew the final section to close the screen.
Weld the 5/16 bolt on to the end of the 40 cm rebar to create a removable handle.  This can be twisted into the redirod connector and disconnected late.  You can make a longer handle for deeper sampling.


Picture
Picture
How to use a surber sampler
  1. Choose the Sampling Locations:  An appropriate riffle must be chosen in the reach. (Shallow runs can be chosen if riffles are not present or cannot be sampled.) Stream depth must be equal to or lower than the height of the surber sampler but the stream must also be deep enough that water can flow into the sampler. Stream velocity must be adequate for water to pull dislodged organisms into the net. The actual location in the riffle must be chosen at random. A Random number table can be used to pick coordinates in the riffle for the exact sampling location. If the location chosen does not meet the standards required for sampling, another site must be chosen. It is more important that the sampling procedure be done appropriately and consistently across all samples.
  2. Set the Surber Sampler:  The base of the sampler (all the way around) (Figure 1) must be firmly against or embedded into the substrate.  If space exists below the bottom of the frame, particularly along the back or the sides, organisms dislodged from the benthos may not be captured and diversity and/or abundance may be underestimated.
  3. Initial Benthic Disturbance:  When the sampler is firmly on the bottom, one or two individuals (depending on sampler size) will disturb the streambed in the area inside the samplers frame (Fig.1). Each large rock must be individually cleaned of all invertebrates. This can be done by hand or with a kitchen scrub brush. It is important to make sure that dislodged individuals either flow into the net or are cleaned directly into the net. Often, it is best to clean the rocks while holding them in the net of the sampler. Each large rock should be visually inspected to make sure that all organisms are removed.
  4. Final Benthic Disturbance: After large rocks on the streambed surface are cleaned and removed, the remaining finer substrates should be disturbed by hand or with some sort of tool The benthos is disturbed to a set depth (usually a few inches) depending on the characteristics of the benthos. The overall depth that the streambed is disturbed will vary depending on the site conditions. The sampling depth should remain constant across all sites and throughout the project. Armored streams require greater sampling depths. However, benthic invertebrates will not be carried into the sampling net from deep holes. When working in urban streams, be careful about disturbing the substrate by hand because sharp objects may exist in the substrate.
From  http://meadows.ucdavis.edu/files/AquaticMacroinvertebrateSampling.pdf
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