Title: Biological Stream Functions
1Biological Stream Functions
Eve Brantley, Alabama Cooperative Extension System
2Stream Functions
- Transport water
- Transport sediment
- Transport energy
- Aquatic organism habitat
- Terrestrial organism habitat
3- General stream characteristics
- River Continuum Concept
- Stream biology basics
- Floodplain functions values
- Importance of Restoration
4Restoration
- Projects need an interdisciplinary team stream
restoration is more than just altering the size
and shape of the channel.
5- Change in energy as streams flow from
- headwaters to mouths
6Stream Gradient
- Headwater streams are typically small with
greater velocity and a steeper gradient
7Stream Gradient
- As these streams flow downhill, they meet up with
other streams becoming a bigger slower moving
body of water with less gradient
8Stream Order
- Streams within watersheds are often classified
hierarchically - Segments can be categorized by their order in the
system
A stream to one person may be considered a river
by another, good communication tool
9- The smallest headwater streams are first order
Stream Corridor Restoration Principles,
Processes, and Practices, 10/98, by the Federal
Interagency Stream Restoration Working Group
(FISRWG)."
10- The union of two first order streams creates a
second order stream
Stream Corridor Restoration Principles,
Processes, and Practices, 10/98, by the Federal
Interagency Stream Restoration Working Group
(FISRWG)."
11- The union of two second order streams creates a
third order stream
The union of two streams of order n creates a
stream of order n1
Stream Corridor Restoration Principles,
Processes, and Practices, 10/98, by the Federal
Interagency Stream Restoration Working Group
(FISRWG)."
12- Headwater streams are orders 1 3
- Mid-sized rivers are orders 4 6
- Large rivers are orders 7 12
- About 85 of all stream miles in the U.S. are
first to third order streams close to 3 million
miles. - The Mississippi River is 12th order at its mouth.
13Stream Gradient
- The decrease in stream gradient and energy along
a streams route to its mouth is accompanied with
changes in habitat and ecological communities.
14The Concept of Connectivity
Headwater streams are especially susceptible to
watershed impacts
15River Continuum Concept
- Describes general changes in stream ecosystems
from headwaters to the mouth - Identifies connections between the watershed,
floodplain, and stream systems - Places site in context within a watershed,
helping define and focus restoration goals
Stream Corridor Restoration Principles,
Processes, and Practices, 10/98, by the Federal
Interagency Stream Restoration Working Group
16River Continuum Concept
17In Stream Habitats
18Riffles
- Characterized by rapid flow carrying small
particles in suspension, coarse sediments on
stream bed, and removal of finer sediments
19Importance of Riffles
- Areas of oxygenation
- Highly diverse substrate and habitat
- Diverse macroinvertebrate population
20Pools
- Regions of slower water current characterized by
the deposition of finer sediments
21Importance of Pools
- Refuge for fish during low flow, drought periods
- Rest stop and food area for fish
- Predator refuge for young fish
22What is living in the stream?
- Biological diversity abundance depends
- on diversity of available habitats
23Benthic Macroinvertebrates
- Benthic bottom dwelling organisms that live in,
crawl upon, or attach themselves to the substrate - Macroinvertebrate can be seen without a
microscope, no backbone
24- Common benthic macroinvertebrates include
- insects (stonefly, dragonfly)
- annelids (aquatic earthworms, leeches)
- crustaceans (amphipods, crayfish shrimps)
- mollusks (clams and snails)
- 4 Functional Feeding Groups
- Shredders
- Grazers
- Collectors
- Predators
25Shredders
- Commonly found in leaf packs
26Collectors Filter Feeders
- Filter organic matter from water column
Caddisfly nets (philopotamids) in the current.
Common below dams.
27Grazers
- Feeds on periphyton attached to rocks, large
woody debris
28Predators
29System changes with stream order
- Orders 1 - 3
- Riffles with intermittent pools
- Large substrate sediment size
- Riparian vegetation shades stream, minimizes
growth of algae and other aquatic plants - Coarse particulate organic matter from
surrounding watershed important for stream
ecosystem energy inputs
30- Cool water fish community
- Darters
- Shiners
- Macroinvertebrate community
- Shredders in leaf packs
- Collectors (filter feeders and gatherers)
31System changes with stream order
- Orders 4 6
- Ratio of riffles to pools decreases
- there are greater stretches of depositional areas
in the river - Substrate materials consist of more muds and
lighter sediments - Increased sunlight with wider channels, primary
productivity increases - Ecosystem shift to dependence on materials
produced inside the channel upstream
32- Shift in fish community
- Greenbreast darter
- Banded Sculpin
- Macroinvertebrate community
- Collectors (filter feeders)
- Grazers
33System changes with stream order
- Orders 7 12
- Few riffles areas are present
- Bottom sediments consist of loose muds, silt, and
organic detritus. - Bordered by marshes and swamps
- Increased dependence on primary productivity
- Continue receiving heavy inputs of dissolved and
ultra-fine organic particles from upstream
34- Warm water fish community
- Catfish
- Sunfish
- Macroinvertebrate community
- Increase in plankton
- Decrease in macroinvertebrate diversity
35What can cause a loss of aquatic habitat stream
function?
- Increase in sediment loads embeds substrate
- Increase in temperature, decrease in dissolved
oxygen - loss of riparian vegetation
- widening of channel / shallow water
- Loss of bed features (pools and riffles)
- straightening of channel
- pools and riffles fill in with increased sediment
36Water Quality Impairments - AL
- Draft 2002 Alabama 303(d) list
- 43 of Total Impaired Miles due to siltation
- Sources of impairment include pasture grazing,
urban runoff storm sewers, agriculture, and
unknown
37How do we know?
- Measure stream health through
- Visual Assessments
- Chemical / Physical monitoring
- Bioassessments
38Bioindicators
- Aquatic macroinvertebrates are used to assess the
relative health of a stream system and its
watershed - relatively immobile -they will take a hit with
water pollution - are easy to capture, relatively abundant and easy
to distinguish - have diverse communities with varying levels of
tolerance to pollution
39- Hanging Rock Creek, NC
- Feeding Type Upstream Downstream
- Shredders 17 1
- Collector/gatherer 21 20
- Scrapers/grazers 27 38
- Predators 14 18
- Filter-Feeders 21 23
Courtesy David Penrose
40Pollution Tolerance Levels
- Highly sensitive to pollution or stream habitat
alteration
41Pollution Tolerance Levels
- Wide range of tolerance to pollution or stream
habitat alteration
42Pollution Tolerance Levels
- Generally tolerant of pollution or stream habitat
alteration
43EPT Index
- This measures the total number of species within
the orders Ephemeroptera (mayfly), Plecoptera
(stonefly), and Trichoptera (caddisfly) - Mayflies, stoneflies, and caddisflies generally
require high levels of dissolved oxygen - A high EPT Index generally indicates a stream and
watershed with low disturbance and pollution
levels
44Adaptations to Living Underwater
- Oxygen Gradient
- Tube breathers (atmospheric O2)
- Cutaneous breathers (dissolved O2)
Rattailed maggot telescopic respiratory tube used
to obtain air from the surface
External gills of mayfly nymph obtain dissolved
oxygen from water
45Riffles
- Life in a riffle means special adaptations to
keep from drifting downstream - Clingers / Sprawlers
- Tarsal or anal claws
- (stonefly nymphs)
- Attachment discs
- (water penny / black fly)
- Streamlined bodies and orientation to flow
46Pools
- Adaptations to slow moving water (less dissolved
oxygen) - Dragonfly - anal gills ventilation by repeated
intake and expulsion of water from the rectal
chamber - Midges - possess a form of hemoglobin that
enables them to utilize small amounts of D.O.
Blood Worms
47Index of Biotic Integrity
- Comprised of fish community parameters or metrics
divided into categories - Species richness composition
- Trophic structure
- Indicator species
- Abundance and condition
- Assists in quantifying changes in ecosystem
health resulting from habitat degradation, flow
alteration, and poor water quality - There are regional differences in IBI metrics
48Cahaba River
49Need for Restoration
50Suspended Sediment Effects
- Clay particles can coat biologically active
surfaces of plants and animals - Can abrade and suffocate periphyton and
macrophytes - Reduced light penetration
- Disrupt respiration and behaviors (feeding and
reproduction)
51Suspended Sediment Effects
- Macroinvertebrates, fish eggs and fry in
interstitial spaces may suffocate - Migrating fish will avoid streams with high
turbidity
52Suspended Sediment Effects
- Some states have turbidity limits of 5 to 25 NTU
above background (Ala. 50 NTU) which translates
into about 3-7 mg/L of suspended sediment - 5 NTU has been shown to be deleterious to some
aquatic organisms
53- Loss of riparian vegetation means loss of
important 1-3 order habitat - Increased sediment loads embeds substrates, loss
of feeding and habitat area
54Restore Stream Functions
- Narrow stream channel
- Increase water velocity
- Deeper water depth
- Improved aeration
- Diversify bed features
- Diversity of substrate sizes
- Create pools and riffles
- Replant riparian corridor
- Energy source
- Stability for streambanks
- Shade
55Restore connection with floodplain
56Stream Functions
- Transport water
- Transport sediment
- Transport energy
- Aquatic organism habitat
- Terrestrial organism habitat
57Floodplain Functions
58Flood Hazards
59Floodplain Functions
- Floodwater Storage
- Sediment Storage
60Floodplain Functions
- Floodwater Storage
- Sediment Storage
- Channel Stability
61Floodplain Functions
- Floodwater Storage
- Sediment Storage
- Channel Stability
- Habitat
62Importance of Restoration
- With more pressure on streams from increased
urbanization, functions and values are impaired
or lost - degraded water quality
- loss of habitat
- loss of water storage conveyance capacity
- decreased recreational aesthetic value
63Loss of Water Storage and Conveyance Capacity
64Loss of Habitat Decreased Recreational Value
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