MASTER PLAN
Appendices
BIG
CHICO CREEK ECOLOGICAL RESERVE
I Introduction:
This document:
· Provides basic information about the Reserve,
· Articulates the vision and goals of the Reserve,
· Identifies issues and constraints that will shape appropriate activities on the site,
· Provides policies and implementation strategies for management,
· Outlines procedures and policies for the use of the property.
This document is dynamic and will change as circumstances warrant. Additional information on the Big Chico Creek Ecological Reserve can be found at the BCCER Website.
The Big Chico Creek Ecological Reserve (BCCER) is managed by
the Research Foundation of the California State University, Chico, for purposes
of education, research, and natural resource protection. The BCCER contains
diverse wildlife sustained in unique and critically important habitats. The
BCCER also contains a number and variety of cultural resources, including
historical sites and features indicative of exploration, mining, logging,
homesteading, and ranching, as well as prehistoric sites and features
representing ancient and historic Native American habitation and other land
uses. In order to manage and preserve the resources for future research and
interpretation, provisions are included in this plan for protection of these
resources.
The BCCER is located ten miles
north of Chico; it is the largest tract of land managed by the CSUC Research
Foundation and shares a boundary with Chico's most important recreational area,
Bidwell Park. The Reserve ranges in elevation from 700 to 2,160 feet and
includes approximately 4.0 miles of Big Chico Creek The Reserve contains a wide
diversity of habitats which support over 140 different wildlife species,
including a number of listed species and species requiring large tracts of
undisturbed habitat. Thirteen percent of the wildlife and 27 percent of the
fish that are known or expected to occur on the Reserve are federal or state
listed species. The key to maintaining species populations is preservation and
enhancement of suitable habitat. To preserve and enhance habitat managers have
to know specific requirements and, in many cases, that requires research.
Finally, no species can be protected on a single piece of property, so
educating others about critical habitat is essential. These three components
define the three main purposes of the Reserve: Habitat Preservation, Research,
and Education. It is critical that the Reserve be carefully managed to meet the
stewardship goals of the Reserve and the needs of the university, while
maintaining the good will of the neighboring property owners and the wider
community.
The mission
of the CSU, Chico Research Foundation’s Ecological Reserve System and
especially the Big Chico Creek Ecological Reserve is to preserve critical
habitat and to provide a natural area for environmental research and education.
The
Big Chico Creek Ecological Reserve is committed to preserving the natural
environment, the species that comprise the native biota, the natural processes
that have always operated in the environment and the cultural resources that
are part of its heritage.
The Big Chico Creek Ecological Reserve will be carefully
managed to meet the stewardship goals of the Reserve with the understanding
that it is part of a larger ecosystem. The Reserve will strive to meet the
needs of the University and maintain the goodwill of neighboring property
owners and the wider community.
To preserve and enhance habitat, the requirements of the
species that live in the Reserve and what effects disturbances have on the
habitat and its inhabitants must be understood along with the dynamics of the
ecological processes. The facilitation of research is critical to such an
understanding.
The Reserve serves as a resource for California State
University, Chico, providing
professional
opportunities for faculty and educational opportunities for students.
Encouraging educational access to the Reserve by regional schools and the
public through outreach to the population of the region will enable future
generations to realize the importance of such natural resources as the Big
Chico Creek Ecological Reserve.
The
BCCER also serves as a resource for public access and community activities
compatible with the goals of the Reserve; to the extent possible, public and
community access should be integrated with the educational goals of the
Reserve.
For this vision to come to fruition it will be necessary
to seek funding from all constituents and friends of the Reserve.
a. Goal: To educate ourselves, our students, and the community to appreciate and understand ecological systems as part of becoming informed citizens and effective leaders in a democracy. The Big Chico Creek Ecological Reserve will be an educational resource serving as an outdoor laboratory, a natural museum, and an outdoor classroom.
b. Objectives and desired future conditions:
c. Implementation strategies
1. Maintain an active website and other forms of communication in order to facilitate information flow to interested parties.
2. Provide tours to show prospective instructors the potential of the Reserve for their classes.
3. Create maps of important resources and uses.
4. Maintain a database of all research projects done on the Reserve and pertinent adjacent lands.
5. Maintain roads and trails to facilitate access by classes. Development of roads and trails may be considered, but only after careful study.
6.
a. Create an introductory university level module in order to
provide background information about the reserve that could be used by classes
in any discipline.
b. Create a similar module for K-12 classes.
7. Establish an annual symposium for faculty researchers and reserve personnel to share information and ideas for maximizing the educational and research values of the Reserve.
8. Create an interpretive center in the vicinity of the Henning House. Some suggestions could include: a “green” building showcasing alternative energy and resource use strategies and a small natural history museum, a display explaining the purpose of the Reserve and its resources, a small nature trail, and interpretive signage.
9. Consider workshops in subject areas relevant to the goals of the Reserve.
a. Goal: To promote and
accommodate research activities on the BCCER
b. Objectives and desired future conditions:
c.
Implementation strategies:
C.
NATURAL AND CULTURAL RESOURCE PRESERVATION AND ENHANCEMENT
a. Goal: To preserve natural and cultural resources of the Reserve in order to maintain both ecological processes and biological diversity; maintain the physical integrity and sociological sensitivity of historical and archeological sites, and protect the Reserve from undue encroachment or damage by human activities.
b. Objectives and
desired future conditions:
Natural Resources:
1. Inventories and maps of natural resources.
2. Avoidance of activities that might damage natural resources.
3. Holistic management for flora and fauna - on an ecosystem rather than species level; maintain the Reserve as part of a larger ecosystem.
4. Management of Reserve should be in expectation of fire and other natural phenomena.
5. Re-establish or expand populations of native species; eliminate or reduce exotics.
6. Encourage research on topics that yield information facilitating management decisions.
Cultural Resources
1. Avoid activities that might damage cultural resources.
2. Provide a long term plan for evaluation and mitigation of sites.
3. Establish connections with groups or individuals interested in the heritage.
c. Implementation strategies
1. Inventories and maps of natural and cultural resources should be ongoing.
2. Create fire management plan that integrates Reserve objectives with fire safety.
3. When feasible, eliminate fencing within the Reserve boundaries.
4. Encourage other agencies to maintain biological corridors to other protected areas.
5. Eliminate traditional cattle grazing; consider short term grazing as a management tool.
6. Reintroduction of native grazers should be encouraged.
7. Limit management treatments to relatively small areas at one time.
8. Replace exotic species with native species when possible.
9. Restore wet meadows and floodplains degraded by gullying; construct waterbars.
10. Place cut brush in areas where gullying is likely.
1. Educational, research, or recreational activities must not compromise the principal Reserve goal of natural and cultural resource preservation and enhancement.
2. There are natural impediments/problems/challenges to doing fieldtrips on the Reserve. Perhaps the greatest is the rugged nature of the terrain, which makes access difficult. Anyone planning to use the Reserve should be aware of the natural hazards that exist in this remote, rugged environment. Due to the limited number and exits of roads, becoming trapped by a rapidly advancing wildfire is a serious possibility. Other natural hazards include high, cold winter and spring flows of Big Chico Creek, sheer cliffs and the falling rocks or landslides they generate. In hot weather, sunstroke, heat exhaustion and dehydration are hazards. Poison oak, wildlife (bear, mountain lion, rattlesnake), wasps, lyme disease (tick transmitted) and plague (flea transmitted) are among additional hazards.
3. Field trip group size is limited due to road access and parking.
4. External constraints to activities are neighboring property owners, potential fires, environmental regulations, off-site conditions, or incursion onto the reserve by livestock and recreational activities.
5. Governmental regulations may apply to some research activities on the Reserve.
6. Public access is an issue to be considered as various types of recreational activities are allowed at the Reserve, including hunting and fishing. If carefully overseen to avoid significant impact on the Reserve’s resources, these recreational activities can be an integral part of Reserve management.
Because of the remoteness of the BCCER, visitors are encouraged to carry first aid kits and exercise caution in undertaking any potentially hazardous activities.
VII History, Natural History, and Management Considerations:
Natural History of the Reserve
The property has a long domestic grazing history, part of it being formerly named the Red Angus Ranch. In the early 1900’s sheep, angora goats, and cattle intensively grazed the property for approximately 30 years. Sheep and goats accessed the property year round and cattle grazed during spring-summer. In addition, the property was hunted for deer and bear. Around 1940, sheep and most of the goats were removed. Cattle continued to graze the area primarily during spring and summer (January-May). Portions of the ranch have burned in 1961, 1978, 1983, 1993, and 1999 with the 1961 fire burning the most acreage within the Reserve. In 1982, the property was enlisted in the California Department of Fish and Game Private Lands Management Program as part of the Musty Buck Gun Club, managed for hunting black-tailed deer, wild turkeys and quail. Past grazing practices, early fire suppression, and poor timber management have combined to reduce the quality of wildlife habitat.
Since protection and enhancement of the Big Chico Creek fishery are high priorities for the project funders and property managers it is useful to know that, historically migratory fish dominated Big Chico Creek in this area. Those include three anadromous species, the spring-run Chinook salmon, steelhead rainbow trout, and Pacific lamprey. Before populations were decimated by downstream and ocean events, migratory salmonids were probably the dominant fish in the foothill zone. Unfortunately, there are no accurate records of historical populations of fish. Sporadic estimates of run size for spring run Chinook in Big Chico Creek have been done since 1956 and are reproduced in Table 1. Only scattered anecdotes of people catching or observing steelhead and lampreys exist. The California Department of Fish and Game (CDFG) has planted both spring run Chinook and steelhead trout in Big Chico Creek on a casual basis at least as far back as 1959. In the 1980s, CDFG began making attempts to count adult spring run Chinook and sporadic attempts to trap down-migrant juveniles. By then populations of spring run Chinook and steelhead trout were extremely low and continuing sporadic hatchery plantings made evaluation of the sustainability of populations difficult.
Observation and sampling by CDFG biologists in 1983 and 1984 showed large populations of Sacramento sucker, hardhead, California roach, Pacific lamprey, and riffle sculpins to be present. Also found were modest populations of Sacramento pike-minnow, low populations of rainbow trout (probably steelhead), and a few brown trout. (The July-September timing of the sampling precluded finding salmon.) In October 1986, CDFG employees used the piscicide, rotenone, to kill all fish in the foothill zone of Big Chico Creek. Subsequent to the piscicide treatment, excess fry from the Feather River Hatchery were planted at Ponderosa Way to try to re-establish populations of anadromous salmonids. Each spring from 1987 to 1992, 100,000 to 500,000 Spring run Chinook salmon fry were planted. In years 1987, 1988, and 1990 from 50,000 to 100,000 steelhead fry were planted. Although surveys by CDFG were not consistently done, lay observers noted that few, if any, of the planted fish returned to Big Chico Creek to spawn.
Table 1. Historical Estimates of Spring Run Chinook Size for Big Chico Creek (California Department of Fish and Game, 1998).
|
Year |
Estimate |
Year |
Estimate |
Year |
Estimate |
|
1956 |
500 |
1971 |
0 |
1986 |
NE |
|
1957 |
248 |
1972 |
NE |
1987 |
NE |
|
1958 |
1000 |
1973 |
50 |
1988 |
NE |
|
1959 |
200 |
1974 |
100 |
1989 |
7 |
|
1960 |
NE |
1975 |
NE |
1990 |
0 |
|
1961 |
NE |
1976 |
NE |
1991 |
NE |
|
1962 |
200 |
1977 |
332* |
1992 |
0 |
|
1963 |
500 |
1978 |
NE |
1993 |
38 |
|
1964 |
100 |
1979 |
NE |
1994 |
2 |
|
1965 |
50 |
1980 |
NE |
1995 |
200 |
|
1966 |
50 |
1981 |
NE |
1996 |
2 |
|
1967 |
150 |
1982 |
NE |
1997 |
2 |
|
1968 |
175 |
1983 |
NE |
1998 |
369 |
|
1969 |
200 |
1984 |
0 |
1999 |
27 |
|
1970 |
NE |
1985 |
0 |
2000 |
27 |
Methods for estimation were neither consistent nor well documented, particularly in early years.
No historical estimates of steelhead spawners have been made for Big Chico Creek. There is currently an excellent population of rainbow trout in Big Chico Creek within the Reserve. No determination has been made of whether they are resident (trout) or migratory (steelhead).
Post-rotenone re-establishment of native non-salmonid fish populations in the region of the Reserve has been slow. While all the other original species have been observed somewhere upstream of Iron Canyon Fish Ladder (Bidwell Park), only the California roach, with its high fecundity and short generation time, has re-established populations comparable to those present before treatment (Maslin, 1997a). Sculpins are found upstream and an occasional sucker is observed in the Reserve, but the pike-minnow and hardhead have not been seen.
The history of other natural resources
is less well documented than the fishery. The property is within the extent
of the winter range of the Eastern Tehama migratory deer herd. This herd has
declined steadily since the mid-1960’s and dramatic declines have been recorded
since 1991 (Loft, E.R. 1998).
Acquisition
The Big Chico Creek Ecological Reserve consists of two properties, the first acquisition known as the Simmons Ranch and the second as the Henning Ranch. For several years the Simmons property was managed as part of the Musty Buck Hunting Club. Management of the lands as part of the hunting club has primarily involved cattle grazing and posting of signs.
The
firm of Campbell and Rhodes appraised the Simmons property in November 1998
at a value of $3,677,000. Its fair market value was determined to be $1,350
per acre. The transfer of the property from Dan Drake and Ed and Darwin Simmons
took place August 8, 2000. The original property of the Reserve was dedicated
on October 26, 2000. The acquisition of the Reserve was made possible by grants from the California Wildlife Conservation Board,
the first grant made under the Proposition 12 bond issue approved by California
voters in November 1999, the U.S. Fish & Wildlife Service's Anadromous
Fish Restoration Program, and the David & Lucile Packard Foundation, Conserving
California Landscapes Initiative. In the fall of 2000, the adjacent Henning
Ranch was purchased for $3,453,000.
Funding agencies and contributions:
Simmons:
$1,667,000
Wildlife Conservation Board
$
1,500,000 Packard Foundation
$
500,000 US Fish and Wildlife Service
TOTAL
$3,667,000
Henning:
$1,723,000
Wildlife Conservation Board
$
630,000 Packard Foundation
$
300,000 National Fish and Wildlife Foundation
$
100,000 California Deer Association
$ 700,000 River Network and Jack
Henning
TOTAL $3,453,000
The Reserve is made up of twelve Assessor’s Parcels as follows:
056-040-003 320.00 ac
050-040-003 120.00 ac
056-040-009 160.00 ac
056-040-010 631.14 ac
056-050-001 640.00 ac
056-050-002 160 .00 ac
056-050-003 350.94 ac
56-50-08 342.40 ac
56-10-18 82.31 ac
56-10-19 397.11 ac
56-40-14 158.66 ac
056-040-015 587.76 ac
Total area 3,950.00 ac
Big Chico Creek Ecological Reserve Site Characteristics
Under the County of Butte’s Zoning Ordinance the property is designated as “U” = Unclassified. The permitted uses include one single family dwelling per parcel agricultural uses. A portion of the property, that area closest to Highway 32, also has a SH = Scenic Highway designation. The General Plan classification is Grazing and Open Space, 20 and 40-acre minimum parcel size, one dwelling per 20 and 40 acres. Some of the property is under Williamson Act contract . The State Wildlife Conservation Board holds a conservation easement on the property that further limits uses and development potential of the property. It basically preserves all use of the property to wildlife and fishery conservation with some provisions for livestock grazing and recreational hunting and fishing under controlled circumstances.
The main entrance to the preserve is via the Henning Ranch gate near the Woodland Park subdivision in Forest Ranch off of State Highway 32. The only other public road frontage is on an isolated segment of the Reserve adjacent to Hwy 32 one mile up hill from Ten-Mile House Road. Access to the main part of the property is via private dirt and gravel roads. A 60-foot road easement connecting to State Highway 32 was preserved through the parkland on the east side of Big Chico Creek, which connects to Highway 32. Musty Buck Ridge Road, from Ponderosa Way, accesses the western plateau of the Reserve from the north and west but is not a deeded right of use. The property has one 2,642 square foot residence, a barn and other small outbuildings. (See Appendix 2, Maps)
To the south, the Reserve borders Bidwell Park, the second largest municipal park (over 3500 acres) in the U.S. The city park and the ecological Reserve are mutually beneficial by combining to extend the protected habitat available to many wide-ranging species.
To the west and north along Musty Buck Ridge are private rangelands used for grazing and wildlife habitat. To the north in the canyon are several private residential holdings, then Sierra Pacific Industries forestlands into the rest of the watershed. An adjacent a piece of BLM land is also under consideration for inclusion in the Reserve. All of the current land uses in the surrounding areas are generally compatible with the Reserve’s primary goal of habitat preservation.
Owners of adjacent properties; BLM, Owen, Johnson, Crane, Schroder and Grossman have indicated an interest in working with the University Research Foundation on the potential for expansion of the Reserve. The Reserve essentially surrounds the Bickley property which is about 160 acres with one residential structure on it. An easement allows access to the owners of the Bickley property through the Reserve.
The Reserve is located in the foothill portion of the Big
Chico Creek watershed. The property is irregular in outline and extends a
maximum of 4.5 miles in a North/South axis and 2.0 miles East/West. The
narrowest part (where Big Chico Creek first enters the property) is only 0.5
mile East/West. Elevations range from 700 feet where Big Chico Creek exits the
property to 2160 feet at the northeastern property line. The eastern
approximately half of the property lies within Big Chico Creek Canyon with a
fairly narrow floodplain and terraces, then walls rising 1000 feet in about 0.5
mile, often including vertical cliffs. The western half can be described as
occupying the top of a gently tilted plain dissected by small headwater
streams. The south (lower) end of this plain is about 1700 feet, dissected in
spots to 1000 feet. The north (high) end is about 2000 feet, dissected to 1800
feet. Soils are relatively shallow, bedrock is exposed in many places, and
surface boulders are scattered over much of the area.
Geologic processes in the Reserve are dominated by the stream dissection of
gently sloping layers of rock to form steep canyons. The upper portions of
the Reserve are in the Tuscan Formation, about 4 million years old, composed
of layered ash, volcanic mud flows (lahars) and patches of alluvium. Some
of the lahars are very hard and form cliffs along the sides of the canyon.
Beneath the Tuscan Formation lies the Lovejoy Basalt, about 15 million years
old, very resistant to erosion and often forming cliffs. Below the Lovejoy
is the Chico Formation, about 75 million years old. It is sedimentary rock
composed primarily of sand and contains numerous marine fossils. Relative
hardness and permeability of the rock layers have a major influence on hydrology
and vegetation within the Reserve. Mass wasting, landslides, and slumps have
been major contributors to the current morphology of the canyon. Since the
Chico Formation is much softer than the Lovejoy Basalt, as the stream carved
its canyon it undercut the Lovejoy, allowing huge slabs and boulders of basalt
to tumble down into the creek to be left on the eroded surface of the sandstone
after the creek meandered away. As the canyon deepened, the hard Lovejoy formed
cliffs high up the walls. Pieces of the basalt, ranging from small cobbles
to large boulders, have fallen off the cliff faces to form talus slopes on
the gentler surface of the Chico Formation. Occasional huge slabs have calved
off the Lovejoy cliffs to generate debris flows that fanned out across lower
terraces. Between the Lovejoy and the Tuscan lies a layer about a foot thick
of tuff from a volcanic ash fall. Water seeping through the tuff weathers
it to clay, forming a slip surface that lets masses of Tuscan slump off the
top of the Lovejoy. Consequently, the floor and lower walls of the canyon
are covered with deposits of material from above, and the Chico Formation
is rarely visible except in parts of the active stream channel. Reserve lands
from the top of the Musty Buck Ridge west consist of gently sloping ridge
tops of exposed Tuscan dissected by headwater streams from Sycamore and Mud
Creeks. Some cliffs are present in the deeper canyons, but landslides have
been much less important than in Chico Canyon. (See Appendix 9)
The soils from the top of Musty Buck Ridge west are classified as moderately fine-texture loam and are generally very shallow. These soils are derived in place from weathering of the parent Tuscan. Bedrock is exposed in many areas and surface boulders are abundant. Soils within Big Chico Canyon may have generated on alluvium, landslide debris, talus, or local chunks of any of the parent rock types. Accordingly, they are extremely variable and can only be classified on a site-specific basis.
Big Chico Creek originates from a series of springs, at an elevation of about 5,400 feet, northeast of the City of Chico on the southwest flanks of Colby Mountain and flows 45 miles from its origin, crossing portions of Butte and Tehama counties, to its confluence with the Sacramento River, at an elevation of 120 feet, west of the City of Chico. The watershed also includes three smaller drainages to the north: Sycamore, Mud, and Rock Creeks. Closest to Big Chico Creek is Sycamore Creek, which originates at around 1,600 feet and is a tributary to Mud Creek. Mud and Rock Creeks, further north, originate between 3,600-3,800 feet. Mud Creek drains off Cohasset Ridge to the south, flowing 26 miles to its confluence with Big Chico Creek. Rock Creek drains the north side of Cohasset Ridge and flows 28.5 miles before it joins Mud Creek. Median discharge for Big Chico Creek in Bidwell Park about three miles downstream of the Reserve is 175 cubic feet per second (cfs) winter and 30 cfs summer. Since the stream reach between the Reserve and the stream gage experiences a great deal of ground infiltration in summer, median summer flow within the Reserve is probably greater than 30 cfs. The BCCER also contains intermittent tributaries of the Sycamore and Mud Creek sub-basins of the Big Chico Creek watershed and numerous springs and seeps. Fresh water at the Henning Ranch house is from a year round flowing spring.
The Reserve is located in an Interior Mediterranean Climate that is defined by its moist, cool winters and hot, dry summers (Critchfield, 1974). Yearly precipitation is extremely variable but averages about 40 inches, most of which falls as rain from November to May, although further upstream in the watershed colder winter storms can deposit large amounts of snow. Until this snow pack melts, usually by late spring, it adds to the regular base flow of Big Chico Creek. The temperatures for the area can drop well below freezing during the winter and commonly rise above 100°F during July and August.
A first point of access is gained by recorded easement to the Reserve chiefly by way of Ten Mile House Road at the “Green Gate" on Highway 32 about 10 miles east of Chico. It leads through two miles of Bidwell Park before entering the Reserve. Ten Mile House Road is a steep, unimproved dirt road with portions that become slippery or boggy in wet weather. When passable, it provides convenient access to two miles of the riparian band adjacent to Big Chico Creek in the Reserve. The road is gated with an informational sign at the Park/Reserve property line. The creek-side road extends through the Reserve where it passes into the Bickely property. This boundary is also gated and signed. The canyon road then exits the Bickley property back into the Reserve paralleling the creek to the Crane property gate.
A second unimproved dirt road follows the top of Musty Buck Ridge. It can
be accessed via private property from three branches: near the airport, at
Richardson Springs, and from Ponderosa Way. Branches of this road follow all
the ridge tops. The Reserve has no formal access rights through the private
properties on Musty Buck Ridge. An abandoned jeep trail forks off the creek-side
road 0.1 mile upstream of the entrance gate, fords the creek and winds its
way up the canyon wall to join the Musty Buck Ridge Road. It is overgrown,
but could be developed for a hiking or ATV trail. A small, isolated segment
of the Reserve is located along Highway 32 about a half mile north of Ten
Mile House Road. This Reserve overlook includes a remnant of the old Highway
32, which provides a paved access to a scenic overview of the Reserve. The
road entrance to the Reserve is gated and an informational sign is attached
to it. A rough hiking trail leads from this overview down to join the creek-side
road 1.3 miles from the southern boundary of the Reserve.
The main entrance to the reserve is a partially paved and gated point fourteen miles from Chico on Highway 32, historically called 14 Mile House Road. It leads one half mile downhill to the reserve headquarters, the Henning House, and beyond the barn down to the creek.
Research currently underway on the Reserve will create maps of the major vegetation communities. The mosaic nature of these communities makes this task a rather formidable project. Students in advanced GIS classes will be invited to help with this undertaking.
The Reserve contains a high diversity of unique and critically important habitats, which support an excellent diversity of wildlife. Terrestrial habitats include blue oak woodland, mixed oak/pine woodland, scrub oak/Ceanothus chaparral, manzanita chaparral, mixed hardwood forest, black oak woodland and riparian areas. Where canopy cover allows, foothill grasslands are present throughout the woodland. Mediterranean annual species dominate the grassland and exotic range pests like medusa-head or yellow star thistle are common. Patches of perennial native grasses are also common. (Table 2)
Table 2. Native perennial grasses identified on the Reserve
|
Common Name |
Scientific Name |
|
Deer grass |
Muhlenbergia rigens |
|
Mexican muhly |
Muhlenbergia
mexicana |
|
Blue wildrye |
Elymus glaucus |
|
Creeping wildrye |
Leymus triticoides |
|
Purple needlegrass |
Nasella pulchra |
|
California melic |
Melica californica |
|
Torrey's melic |
Melica torreyana |
|
Woodland brome |
Bromus laevipes |
|
California brome |
Bromus carinatus |
The mosaic of terrestrial plant communities provides habitat for over 140
different wildlife species. Thirteen
percent of the wildlife that are known or expected to occur on the Reserve
are listed species (including Species of Special Concern). Due to the property’s
remoteness, little human disturbance, and limited hunting pressure, wildlife
have an excellent chance of developing healthy and sustainable populations
with proper habitat management.
There is also a diversity of aquatic habitats within the Reserve. Big Chico Creek contains deep bedrock pools with undercut rock ledges, scattered large boulders and abundant overhanging vegetation and woody debris. These pools are separated by relatively steep riffles dominated by emergent boulders and provided with abundant cover from torrent sedge and umbrella plant. The creek provides excellent habitat for spring-run Chinook salmon, steelhead and resident rainbow trout. California roach are abundant, providing food for the salmonids as well as kingfishers, herons, and mergansers. Additional aquatic habitat is found in 0.8 mile of the headwaters of Sycamore Creek, 1.5 miles of the headwaters of tributaries to Mud Creek and 6 small tributary streams to Big Chico Creek. These small streams provide both perennial and seasonal habitat for insects and amphibians.
The diversity of habitats on the Reserve provides suitable living conditions for a very diverse biota. With the exception of the Big Chico Creek fauna, current lists of plants and animals are based more on published distributions and knowledge of nearby areas than on observations within the Reserve. Field surveys of species diversity will be one of the top priorities for the first few years of research on the Reserve. (See Appendix 8)
Historical and Ongoing Research
Fourteen master's theses have been done on aspects of Big Chico Creek. The Big Chico Creek Watershed Alliance has completed an Existing Conditions Report for the Big Chico Creek Watershed, which includes a great deal of information about the Reserve area. Geosciences professor William Murphy has begun gathering data on groundwater chemistry. Professor Dawn Wilson, Biology Department, CSU, Chico and her graduate students are comparing the biology of western pond turtles in the Reserve with those along the Sacramento River. Botany graduate student, Colby Boggs, recently completed his master's research on canyon dudleya, (Dudleya cymosa) including a population within the Reserve. A graduate student compared fire damage to blue oaks (Quercus douglasii) in the Reserve where the 1999 fire burned downhill to that in Upper Bidwell Park where a backfire burned uphill. Professor Paul Maslin, Biology Department, is experimenting with native grass restoration.
Fire has been an important ecological factor in the Sierra –Cascade foothills. The seasonal availability of precipitation ensures abundant fuel coupled with a dry period in which it can burn. Lightning strikes and, more recently, human activities provided an ignition source. Fire is essential to the health of many foothill vegetation communities. Most of the Reserve west of Big Chico Creek burned in the Musty Buck Fire of 1999, resulting in extensive root sprouting of many woody species including California bay, scrub oak, live oak, and deer brush. Many seedlings of buck brush, manzanita, and gray pine have been observed subsequent to the fire. Buckbrush and deerbrush are important food items for deer feeding only on newly developed shoots, which are most abundant on younger plants. As chaparral matures available browse grows beyond the reach of deer (Biswell and Gilman 1961). In addition, many chaparral plants have evolved adaptations that allow them to survive, reproduce, and thrive in a system that frequently burns. Historically, blue oak/pine woodlands burned at 2 to 18 year intervals with an average fire frequency of 7.8 years (Stephens 1997).
Livestock grazing is often blamed for reducing habitat quality for wildlife, especially those species dependent on riparian areas. Obviously, intense grazing, such as occurred for approximately 30 years on the Reserve, is the most destructive. However, Kie and Boroski 1995, found the effect of cattle grazing to be minimal on black-tailed deer upland home range and time spent feeding. This may be a result of different habitat preferences between cattle and deer (Barrett 1982). Substantial literature has been written regarding the effects of cattle grazing on riparian areas and bird communities. Generally, the results of grazing are species and site specific. In arid environments, cattle tend to congregate in riparian or seep areas causing intense competition with other wildlife, reducing cover and forage, eroding the streambank, and increasing sedimentation in creeks. Cattle also affect the ecology of the community in more subtle ways. Unpalatable plants have a selective advantage over palatable plants, often contributing to the invasion of noxious weeds. Soil is compacted by the high weight/area of hooves, decreasing the survival of burrowing animals and the rate at which precipitation is absorbed into the soil thereby increasing surface runoff and erosion and reducing soil availability to plants. Site-specific cattle grazing can be used as a habitat management tool. Turning cattle onto a range when an undesirable plant is setting seed and taking them off before a more desirable plant begins to seed can help shift the balance of forage species. Grazing can also be used to help reduce fuel load and keep wildfire controllable.
Physical Improvements and Previous Enhancements
The property has been primarily used as rangeland for about 100 years. Except for the Henning Ranch structures, the only physical improvements are minimal roads and fences. Most are in need of repair or removal with site restoration. (See Appendices 12 and 13).
Current Issues and Constraints
Proximity to Bidwell Park creates public pressure for unauthorized recreational access on habitat and Reserve wildlife populations in the park. The concept of creating a public hiking trail from the Sacramento River through Bidwell Park and upstream to the crest of the mountains has achieved some public attention. Such a trail, were it to be permitted through the Reserve, could compromise the mission and proper functioning of the Reserve as detailed in this plan.
Hunting.
The history of access for hunting on parts of the Reserve
as well as restrictions on acquisition funds require some hunting access
to be provided. An annual hunting management plan has been prepared by California
Department of Fish and Game staff and hunting activities will be monitored
by Department of Fish and Game biologists and wardens as well as Reserve staff
(Appendix 14).
Fishing is restricted by DFG regulations. Because
the Reserve is critical spawning and rearing habitat for both spring-run Chinook
and steelhead, DFG wardens and Reserve staff will carefully monitor potential
activity (Appendix 14).