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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 bay’s 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 Mackay’s 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. (Delorme’s 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 Coalition’s website is http://www/igc/apc.org/nhi/s3rc/index.htmlWB00882_.GIF (263 bytes). Other potential sources of historic Bay stream habitat information are the Urban Creeks Coalition and Oakland Museum’s Natural Sciences Department (www.museumca.org/creeks).


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