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|
Natural
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Altered
|
| |
Connectivity within natural range |
|
|
Magnitude |
Landslide dams may block migration to very small, e.g., a single tributary
or large areas, e.g., most of the Fraser River |
Dams and culverts block small and large areas, and thousands of blockages
are in place simultaneously. |
|
Frequency |
Migration blockages are rare, < once every thousand years in most
locations |
Not frequent, i.e., each blockage goes in once, but many areas blocked
simultaneously |
|
Duration |
Most landslide dams are temporary, lasting hours to days. |
Tens to hundreds of years to date |
|
Predictability |
Locations are not very predictable. |
Once in place the blockage is “predictable”. |
Sediment supply |
|
|
Magnitude |
Magnitude of sediment supply varies spatially and temporally, driven by
precipitation intensity, duration, and extent. |
Sediment supply generally increases due to land uses such as forestry,
grazing, or cultivation. |
|
Frequency |
Sediment supply is episodic. Some sediment enters a river system each year,
but location, amount, timing, type, size, etc. vary from year to year. |
Land uses such as forestry tend to increase the frequency of sediment
inputs to rivers. |
|
Duration |
Duration of sediment supply generally mirrors storm durations. |
Little change from land use |
|
Predictability |
Stochastic |
Stochastic, but more frequent |
Hydrologic regime |
|
|
Magnitude |
Spatial extent of storms and associated floods can be as small as a single
watershed, or as large as an entire region, e.g., the 1964 storm, in which
record floods occurred from northern California to southern
Washington. |
Typically reduced due to dams absorbing the peak flows |
|
Frequency |
Large floods or extreme low flows typically occur several times in a given
year. |
Peak and low flows are typically reduced at the seasonal and annual time
scale, whereas diurnal range may be increased at the daily time scale. |
|
Duration |
Ranges between hours, days, and weeks |
Rivers regulated by dams typically increase the duration of peak flows.
|
|
Predictability |
Highly predictable on an annual scale, e.g., whether they will
occur; less predictable at the monthly, weekly, or daily scale |
Greater predictability due to rivers being regulated by dams |
Thermal regime |
|
|
Magnitude |
Temperature extremes rarely exceed tolerances of most salmon
populations. |
Temperature extremes commonly exceed tolerances of many salmon
populations. |
|
Frequency |
No exceedence in most years at most locations |
Several times a year in most locations |
|
Duration |
Days to weeks |
Days to weeks |
|
Predictability |
Predictable |
Predictable |
Riparian vegetation |
|
|
|
|
|
|
Magnitude |
Small streams: Fires periodically kill riparian forest patches. Large
rivers: River erosion periodically removes patches of floodplain
forest. |
Fires and erosion rarely kill riparian forest patches, but logging and land
conversion kill a greater expanse of riparian forests. |
|
Frequency |
Small streams: fire reset vegetation at return intervals of 50–400
yr Large rivers: erosion reset forests at intervals of 1 to ~100s of
yr |
Logging: return interval of < 50 yr in most cases, riparian
protections recently enacted in some areas Land conversion: generally kills
forests once |
|
Duration |
Forests begin regeneration soon after disturbance. |
Logging: forests begin regeneration soon after disturbance. Land
conversion: often no regeneration, i.e., duration of decades to centuries |
|
Predictability |
Fire: unpredictable Erosion: predictable |
Predictable |
Nutrient regime |
|
|
Magnitude |
Millions of salmon returning |
Few to no salmon returning in many areas |
|
Frequency |
Annual |
Annual |
|
Duration |
Salmon returning in most months of the year |
Salmon returning in most months, but shorter spawning runs for many
populations |
|
Predictability |
Predictable |
Predictable |