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Central Valley Chinook Salmon
HISTORIC STREAM HABITAT DISTRIBUTION
Table A. General Information about Spawning Habitat & Habits of the
Four Salmon Runs in the Central Valley
Upstream Migration Season (Run) |
Typical Spawning Habitats |
Spawning Habits |
Approximate Elevation Salmon Reached |
| Fall |
Lower
rivers and tributaries, valley floor and foothill reaches. |
Spawn
soon after entering natal streams, limited by deteriorated physical condition and ripeness
of eggs. |
To
1000 feet elevation, based on the McCloud River (H. Rectenwald and R. Yoshiyama,
pers.comm.) |
| Late-Fall |
Upper
mainstem rivers including the upper mainstem reaches of the Sacramento River and major
tributaries (currently blocked by Shasta Dam), and perhaps other valley stream such as the
American River and southern San Joaquin Rivers. |
Spawn
upon entry into stream, limited by deteriorated physical condition and ripeness of eggs.
Largest of the Sacramento River salmon. Juveniles require summer cold water flows. |
Unknown |
| Spring |
Higher
streams, with adequate spring fed run-off or snow melt runoff to keep summer water
temperatures low. Historically abundant in the San Joaquin system. |
Hold
in the stream for several months before spawning. Smaller bodied fish enables access to
higher reaches. |
~1500
feet or ~2500 feet to 3000 feet if spawned earlier |
| Winter |
Spring
fed headwaters where cold constant summer flows exist. This includes the Little (Upper)
Sacramento, Pit River, McCloud River , Fall River (blocked by Shasta Dam)and Battle Creek. |
Hold
in the stream for several months before spawning. Smaller bodied fish enables access to
higher reaches. |
Headwater
reaches. |
Table B. Historic Chinook Salmon Habitat
Distribution 1
Central Valley, California
1. This table is to be used in conjunction with GIS maps prepared for EFH by Tierra
Data Systems.
2. These historic distribution sites are in addition to those noted in the Current
Habitat Distribution Table and EFH Maps.
3. See also: "Central Valley Chinook Salmon - Bibliography by Subject", under
Historic Conditions, for more references.
(Streams listed from north to south)
Stream/Tributary |
Historic Runs |
Historic Upper Limit of Run / Comments(Streams listed from north to south) |
Historically
available (mi) |
Presently
accessible (mi) |
| Upper
(Little) Sacramento - River |
fall
late fall
winter
spring |
To
site of present Box Canyon Dam ( Lake Siskiyou). Runs would congregate at the falls at
Sims, ~ 31 miles upstream of Shasta Dam. Only western North American river to support four
runs of salmon. |
52 |
0 |
| Hazel
Creek |
n/a |
Confluence
with the Upper (Little) Sacramento near Sims, upstream distribution not mentioned. |
n/a |
0 |
| Pit
River |
fall
spring
winter |
To
Pit River Falls (RM75), some may have ascended to the mouth of the Fall River |
76
(99 miles total) |
0 |
Hat Creek |
winter
spring |
Winter
run in the headwaters, spring run to the present day vicinity of Cassel. |
7 |
0 |
Burney Creek |
winter |
To
Burney Falls ~1 mile upstream of the Pit River Confluence, habitat and conditions for
spawning from the falls downstream.. |
1 |
0 |
Kosk Creek |
winter |
Stream
has suitable habitat and conditions for spawning. Historic upstream range not mentioned. |
n/a |
0 |
Fall River |
spring
winter |
Ascend
to the source (spring fed) of the river ~ 15 miles. |
15 |
0 |
| Squaw
Creek |
n/a |
Historic
upstream range not mentioned although salmon use is known. Has suitable spawning beds and
two or three smaller tributaries. |
not mentioned |
0 |
| McCloud
River |
spring
fall
winter |
Upstream
to the Lower Falls, ~6 mile upstream of present day Lake McCloud. |
43 |
0 |
Squaw Valley Creek |
spring |
Approximately
5 miles upstream, could support ~ 830 redds (Sept. 1938) |
n/a |
0 |
Star City Creek |
spring |
Historic
upstream range not mentioned in available references |
n/a |
0 |
Claiborne Creek |
spring |
Historic
upstream range not mentioned |
n/a |
0 |
Caluchi Creek |
spring |
Historic
upstream range not mentioned |
n/a |
0 |
| Sacramento
River -Mainstem |
fall
late-fall |
Historically
available habitat is measured from Rio Vista in the northern Sacramento - San Joaquin
Delta, upstream to the confluence of the Upper (Little) Sacramento and Pit rivers. Used as
a migration route for spring run and winter run, with scattered spawning of these runs
presently occurring on the mainstem up to impassable Keswick Dam. |
299 |
286 |
| Clear
Creek |
fall
spring |
Spring
run to the French Gulch area (~1400 ft elevation). |
25 |
16 |
| Stillwater
Creek |
fall |
Approximately
20 miles upstream in 1938, near present day vicinity of Mountain Gate. |
~20 |
~20 |
| Cow
Creek |
fall
spring
late-fall |
Historic
upstream range not mentioned in Yoshiyama et al. Presently, fall-run occur in the mainstem
up to where the South Fork joins and in the North (Little) Cow to the falls near the Ditty
Wells (Calif. Dept. of Forestry) Fire Station. Spring run have been reported in the South
Fork, even though adequate habitat is lacking (CDFG,1993). Other tributaries have bedrock
barriers which limit access: North (Little) Cow, Clover and Old Cow. Late-fall run salmon
occasionally occur in Cow Creek. |
n/a |
~15 |
| Cottonwood
Creek |
fall
spring
late fall |
Spring
run would ascend the South Fork above Maple Gulch.,and the Middle Fork up Beegum Creek
approximately 8 miles. |
79 |
79 |
| Battle
Creek |
fall
spring
winter |
Ascended
the North Fork to the Volta Powerhouse above Manton, and the South Fork near Hwy 36
crossing. Now access blocked by Coleman National Fish Hatchery weir. |
53 |
6 |
| Antelope
Creek |
fall
spring
late fall
(probably) |
North
Fork Antelope to the McClure Place or confluence with Judd Creek. South Fork Antelope to
Round Mountain Creek. The late fall run is sustained by the Coleman National Fish
Hatchery. |
32 |
32 |
| Mill
Creek |
fall
spring
late fall (occasional) |
Most
habitat located from mouth of Little Mill Creek (1500 feet) to Morgan Hot Springs (5000
feet- highest) . The upstream spawning and holding limit is near the Lassen National Park
boundary. The upper reaches water temperatures are higher due to influence of hot
springs. |
44 |
44 |
| Thomes
Creek |
fall
spring |
Fall
run when streamflow adequate. Eight miles upstream from the town of Paskenta supported a
small spring run. |
~30 |
~ 4 |
| Deer
Creek |
fall
spring |
Upstream
to Deer Creek Falls. Deer Creek has additional habitat available currently than
historically. Salmon were never known to have passed Lower Deer Creek Falls which was
bypassed with a fish ladder constructed in 1942-1943. |
34 |
38 |
| Big
Chico Creek |
fall
spring
late fall |
Probably
used opportunistically in the past. Upstream limit is Higgins Hole approximately .5 to 1
miles above the Ponderosa Way crossing. |
24 |
24 |
| Stony
Creek |
spring
fall |
To
the confluence of Stony and Little Stony Creeks, ~5 miles below Stonyford. Now blocked by
Black Butte Dam, diversions and low flows. |
54 |
~3 |
| Butte
Creek |
fall
spring
late-fall |
Spring
run ascended to the present site of Centerville Head Dam near DeSabla. A portion of the
spring run may have spawned in reaches further upstream. Historically the spring run was
larger than the fall-run, an exception in the northern Sacramento Valley. |
53+ |
53 |
| Feather River |
fall
spring |
Historically one of the major
salmon streams of the Sacramento River. The mainstem spawning beds extended 30 miles from
the river mouth up to Oroville. Oroville Dam now blocks access. |
mainstem =
64
Total = 211 |
64 |
West
Branch |
|
To the site of Stirling City. |
22 |
0 |
North Fork |
|
Past
the present day site of Lake Almanor ~ 6 miles. Surrounding tributaries were accessed
(>4,200 ft. elevation). Most of spring run stopped by Salmon Falls ~2 to 2.5 miles
above the town of Seneca. |
105 |
0 |
Hamilton
Branch |
|
Possibly ascended close to
present day Mountain Meadows Reservoir. |
|
|
East
Branch of NF |
|
Upstream at least to Indian
Creek. |
|
|
Indian
Creek |
|
At least as far as Indian
Falls Near Hwy 89 and 70. |
|
|
Yellow
Creek |
|
Historic upstream range not
mentioned. |
|
|
Spanish
Creek |
|
Historic upstream range not
mentioned, substantial falls above the mouth. |
|
|
Middle
Fork |
|
Fish stopped at Bald Rock
Falls, just above Lake Oroville and Curtain Falls immediately above. |
14 |
0 |
Fall River |
|
Ascended ~ 1 mile upstream
from the confluence to Feather R Falls (640 ft). |
1 |
0 |
South Fork
|
|
To Forbestown, near the upper
limit of the South Fork arm of Lake Oroville. |
6 |
0 |
| Yuba
River |
fall
spring |
Historically
supported 15% of the annual fall-run in the Sacramento River system. Damaged by hydraulic
mining from 1850-1885. Englebright Dam is present upstream limit. |
mainstem = 21
Total = 77 |
21 |
North Fork |
|
To Salmon Creek, near Sierra
City. |
41 |
0 |
Middle
Fork |
|
The lower river, near where
the North Fork joins. Direct information on the distribution is lacking. |
14 |
0 |
South Fork |
|
1 to 2 miles upstream ,
perhaps spring run accessed the present town of Washington. Direct information on the
distribution is lacking. |
1.5 |
0 |
Dry Creek |
|
~5 to 6 miles |
5 to 6 |
0 |
| Bear River |
fall |
Fall run only, to the
present day Camp Far West Dam / Reservoir. Occasional use historically. |
16 |
16 |
| American
River |
fall
spring
late-fall (possibly) |
Mainstem
use and distribution on the American River damaged by hydraulic mining from 1850-1885.
Access now blocked by Nimbus Dam (below Folsom Dam). |
Total = 161 |
<28 |
North Fork |
|
To
Mumford Bar, perhaps upstream additional ~11 miles to falls at Royal Gorge (~ 4000 feet). |
56 |
0 |
Middle
Fork |
|
To the confluence with the
Rubicon River (1640 feet). |
22 |
0 |
South Fork |
|
Salmon
Falls was a probable barrier to fall-run fish but was blasted in 1935. The vicinity of
Eagle Rock (4600 ft), ~12 miles downstream of Strawberry, is the approximate upper limit
for salmon. |
55 |
0 |
| Cache
Creek |
fall |
At
least to Capay Dam site, probably only during wet years in this intermittent stream;
upstream extent poorly known. Access now blocked by Capay Dam, diversions, and low flows. |
~ 25-30 |
0 |
| Putah
Creek |
fall |
Near
the town of Monticello, probably only during wet years in this intermittent stream;
upstream extent poorly known. Access now blocked by Monticello Dam, diversions, and low
flows. Salmon spawners returned in winter 1998 near Davis and juveniles survived (P.
Moyle, UCD, pers. comm.). |
~ 15-20 |
~ 8 -15 |
| San
Francisco Bay |
all |
Historic
use by coho salmon and steelhead may have been more common than by chinook salmon due to
small size of most streams. Current spawning runs in many tributaries appear to be mostly
of fall-run hatchery origin and occur mainly during wet years. Most (82%) of the small
sloughs and marshes have been filled in SF Bay; diversions and pumps divert juveniles;
estuary function has been severely altered; urban streams are channelized, piped and
"flood controlled"; and pollutant loads have lowered habitat quality. Bay itself
continues to provide adult and juvenile migration and some juvenile rearing habitat for
all runs, though the bays surface area has been reduced by 37% due to filling. |
n/a |
See Current
Stream Habitat
Distribution
Table & Map
for best estimates of each stream |
Napa River |
fall |
Historic use quite likely by
small and/or sporadic runs (Leidy & Sisco). Now blocked by Kimball Canyon Dam. |
n/a |
n/a |
Sonoma
Creek |
fall |
Historic use possible by
small and/or sporadic runs (Leidy & Sisco). Now at least to the confluence with
Carriger Creek. |
n/a |
n/a |
Petaluma
River |
fall |
Historic use quite likely by
small and/or sporadic runs (Leidy & Sisco). |
n/a |
n/a |
San Pablo Creek |
fall |
Native
American archaeological sites adjacent to creek lend support to the conclusion that coho
and possibly chinook salmon used the creek prior to European settlement (Leidy, pers.
comm.). Now blocked by San Pablo Dam / Reservoir. |
n/a |
n/a |
Walnut Creek |
fall |
Likely
supported chinook salmon (Leidy & Sisco). Now blocked by first drop structure near
Hwy. 24 crossing. |
n/a |
n/a |
San Leandro Creek |
fall |
A
run of chinook salmon was known to ascend to base of Lake Chabot Dam at least until the
late 1870s (Leidy & Sisco). Access blocked now by Lake Chabot Dam (below Upper San
Leandro Reservoir). |
n/a |
n/a |
Alameda Creek |
fall |
An
historical record from native American middens near Niles exist for chinook salmon. Now
blocked by concrete invert at BART crossing below Niles. |
n/a |
5.5 mi. |
Guadalupe River |
fall |
Historic
use by small and/or sporadic runs quite likely (Leidy & Sisco). Local restoration
group (Southbay Salmon & Steelhead Restoration) claims it supported chinook, coho and
steelhead for sport fishing as late as the 1940's. Headwaters were well-shaded. Access now
blocked by 13 ft. diversion barrier 14 mi. upstream. |
n/a |
9-14 |
Coyote Creek |
fall |
Historic
use by small and/or sporadic runs quite likely (Leidy & Sisco). Now blocked by LeRoy
Anderson Dam. |
n/a |
n/a |
| San
Joaquin River -Mainstem |
fall
spring
late fall |
Distance
includes from Mossdale in the southern Sacramento -San Joaquin Delta, upstream to the
confluence of the Merced River. This stretch lacks spawning gravels and serves primarily
as a migration corridor. |
50 |
50 |
| Mokelumne
River |
fall
spring
late-fall (possibly) |
12
miles upstream from Pardee Dam (1928) at the present site of Electra Powerhouse. Access
now blocked by Camanche Dam. |
69 |
46 |
Cosumnes River |
fall |
Falls
~ ½ mile below Latrobe Hwy Bridge. No dams are present to block access today. |
34 |
34 |
| Calaveras
River |
unknown |
Unknown,
historically marginal habitat, occurrence irregular. Recently a "winter run" was
observed from 1972-1984. Fall-run fish occasionally enter when suitable fall flows are
available. New Hogan Dam now blocks access. |
38 |
38 |
| Stanislaus
River |
fall
spring |
Mainstem
use on the Stanislaus River - 31 miles now lost above Goodwin Dam. |
113 total |
46 |
North Fork |
|
Up to Mackays Point or
~14 miles above the confluence with the Middle Fork |
14 |
0 |
Middle
Fork |
|
No substantial obstacles to
the reach above present day Beardsley Reservoir (3400 feet), the steep gradient may have
deterred salmon. |
21 |
0 |
South Fork |
|
Distribution unknown,
unlikely to have supported salmon populations |
n/a |
0 |
| Tuolumne
River |
fall
spring |
To
Preston Falls on the boundary of Yosemite National Park (~51 miles upstream from the
present New Don Pedro Dam). Fall-run fish historically comprised 12% of total fall run
spawning escapement for the Central Valley. Now blocked by La Grange Dam. |
99 total |
47 |
North Fork
|
|
Falls ~ 1 mile upstream of
the mouth |
1 |
0 |
South Fork |
|
Steep sections just above the
mouth likely obstructed salmon |
0 |
0 |
Middle
Fork |
|
Steep sections just above the
mouth likely obstructed salmon |
0 |
0 |
Cherry
Creek |
|
Perhaps spring run entered
this stream, distribution not mentioned |
0 |
0 |
Clavey
River |
|
Steep sections just above the
mouth likely obstructed salmon |
0 |
0 |
| Merced
River |
fall
spring |
Mainstem
for ~ 49 mi. , approaching the vicinity of El Portal (~2000 ft.). To Crocker - Huffman
Diversion Dam now. |
99 total |
43 |
South Fork |
|
South Fork ~ 7 miles to Peach
Tree Bar |
7 |
0 |
North Fork |
|
North Fork has a waterfall ~
1 mile upstream, therefore no fish mentioned in the North Fork |
0 |
0 |
| Upper
San Joaquin River |
fall
spring |
About
half way up Mammoth Pool Reservoir. The historically available habitat distance includes
the mainstem river above the confluence with the Merced River. Mainstem = 53 mi. above and
121 mi. below impassable Friant Dam. Polluted drainage, barriers, and low flows now
prevent access above Merced River. |
174 total |
0 |
| Fine Gold Creek |
|
Upstream ~ 6 miles |
6 |
0 |
| Cottonwood Creek |
|
Upstream ~ 2 miles |
2 |
0 |
| Willow Creek |
|
Upstream distribution unknown
~ 1 mi. |
1 |
0 |
| Kings River |
spring |
To the North Fork ~12 miles upstream past present day Pine Flat Reservoir. |
84 |
0 |
Footnotes:
1. Primary Sources: Yoshiyama, R.M., E.R. Gerstung, F.W. Fisher, and
P.B. Moyle. 1996. Historical and present distribution of chinook salmon in the Central
Valley drainage of California. pp. 309-361 in: Sierra Nevada Ecosystem Project: Final
report to Congress, vol. III. Centers for Water and Wildland Resources, University of
California, Davis. Davis CA. Updated with personal communication from Dr. Ronald
Yoshiyama. Also: Leidy, R.A. and J. Sisco. 1999. Historical distribution and
current status of steelhead (Oncorhynchus mykiss irideus), coho salmon (O.
kisutch), and chinook salmon (O. twaschyscha) in streams of the San Francisco
Estuary, California. San Francisco Estuary Institute. Expanded with personal communication
from Robert Leidy, U.C. Davis doctoral student. Secondary Sources: California Dept.
of Fish and Game. 1993. Restoring Central Valley streams: a plan for action ;
interviews with local biologists, as noted below. For
more details, see also: Central Valley Chinook Salmon - Bibliography by Subject
(see under Historical Conditions); and Contacts and Expertise list, both prepared
by Sari Sommarstrom & Assoc. (1999).
2. Lengths of all stream reaches known or presumed to have been
traversed or utilized by salmon in the drainage are included (from Yoshiyama et al. 1996).
Smaller tributaries were not listed in Yoshiyama et al. article since not enough
information was available and authors desire to be conservative in their estimates
(R. Yoshiyama, pers.comm.). Where possible, some additional streams have been added based
on new sources (see below) for this Table.
3. Length between the mouth of the stream and the current upstream
limit (from Yoshiyama et al. 1996).
4. Stillwater Creek - Estimate provided by Harry Rectenwald, CDFG
Biologist, Redding, CA. 1998.
5. Rough estimate from map, scale = 1:150,000. (Delormes Northern California Atlas and Gazetter.) Not estimated in
Yoshiyama et al.
6. Thomes Creek - Estimate provided by Terry Healey, Fisheries Biologist, CDFG,
Redding, CA.1998. Non-natal rearing juveniles found 13 km upstream near the Rawson Rd.
crossing (information provided by Professor Paul Maslin, CSU Chico, 1998.)
7. Bay Area impacts described in: San Francisco Estuary Project. 1994.
Comprehensive conservation and management plan for San Francisco Estuary. Prepared for EPA
by the Assoc. of Bay Area Governments, Berkeley CA. @ 500 pages. South Bay fish expert is
Dr. Jerry Smith of San Jose State Univ. for more details on historic fish runs and
streams. Southbay Salmon & Steelhead Restoration Coalitions website is http://www/igc/apc.org/nhi/s3rc/index.html . Other potential sources of historic Bay stream habitat
information are the Urban Creeks Coalition and Oakland Museums Natural Sciences
Department (www.museumca.org/creeks).
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