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Greater Bear Creek Area Watershed
Executive Summary
What
is a Watershed?
About the Watershed
Resource Concerns
Goals & Objectives
Implementation
Resource Planning
Committee
Technical Advisory Committee
Additional Contributors

Mission
Statement
The
planning committee of the GBCAW will implement a plan to foster active
cooperation from landowners/stakeholders to improve and protect natural
resources in the Bear Creek Watershed through education and financial
incentives.
What
is a Watershed?
A watershed is the area of
land that catches rain and snow and drains or seeps into a marsh, stream, river,
lake or groundwater. Rain water or snow melt flows across cropland fields and
livestock facilities, sometimes taking soil particles, livestock waste,
fertilizers and pesticides with it, AND water flows off roofs, parking lots and
streets in urban areas carrying potential pollutants with it. All of this water
ends up in lakes and streams. Overall, a healthy watershed is vital for a
healthy community.
Work on the Greater Bear Creek Area Watershed plan began in
2005. Local residents approached the Soil and Water Conservation Districts (SWCDs)
in Adams and Hancock Counties asking for assistance. A local planning committee
was formed, and work began on identifying and inventorying natural resource
concerns. The purpose of an overall plan is to be able to access technical and
financial assistance to address those natural resource concerns.
About
the Watershed
The Greater Bear Creek Area Watershed drains approximately
570 square miles in portions of northern Adams and southern Hancock counties in
west central Illinois. Bear Creek itself is 43.0 miles long with approximately
854 total stream miles in the Bear Creek watershed itself. There are several
additional streams included in this plan, that drain directly into the
Mississippi River. According to the 2006 census, the population of Adams and
Hancock counties combined was 86,312.
Land use in the watershed is predominately cropland, with
areas of woodland and pasture found on sloping areas along drainage ways. The
major crop rotations consist of corn-soybeans, corn-soybeans-wheat, and
corn-soybeans-wheat-meadow for virtually all land slope classes where erosion is
occurring above tolerable levels. Almost 94% of the land is in farms.
Livestock is prevalent in the GBCAW. Hancock County ranks 2nd in the
state for the number of beef cows and Adams ranks 3rd. In numbers of
hogs and pigs, Hancock County ranks 8th and Adams County ranks 13th.
|
Land Use |
Acres |
|
Agriculture (corn,
soybeans, wheat, other small grains & hay, other agriculture |
229,275 |
|
Grassland (rural
grassland) |
63,014 |
|
Forest (upland,
coniferous, and partial canopy/savannah upland |
34,541 |
|
Urban |
14,623 |
|
Wetland (shallow &
deep marsh, seasonal, floodplain forest, swamp, and shallow water) |
15,078 |
|
Other (surface water,
barren land, clouds and cloud shadows) |
8,468 |
|
Totals |
364,999 |
Water
quality monitoring has shown that some stream segments in the GBCAW are
impaired. The chart below shows the stream segments, the impairments, causes,
sources and related impacts.
Impaired Stream Segment |
Causes |
Sources |
Related Impacts |
|
KI 02
(Main Bear Creek below the convergence of the North Fork and the South Fork)
Primary
Contact (swimming) Not Supported |
Fecal
Coliform
|
Source
Unknown, but could be Improperly functioning septic systems; livestock
facilities
|
The
main concern regarding fecal coliform is public health. Waterborne diseases
may be transmitted to humans through drinking or contact with pathogen-laden
waters. |
|
Manganese |
Agriculture
Sediment & soils
Hydromodification; removal of riparian vegetation; physical habitat
alteration |
Since
manganese is a naturally occurring element, it is difficult to determine
what is natural & what can be contributed to sediment entering the stream. |
|
KI 03
(Main Bear Creek from the convergence of the South Fork upstream to the
Adams/Hancock County Line)
Aquatic
Life – not supported
Overall
Use – partially supported |
Manganese
|
See
above |
See
above |
|
Physical Habitat Alteration |
Hydromodification; removal of riparian vegetation; physical habitat
alteration; stream bank modification |
Removal
of riparian vegetation can destabilize stream banks and contribute to
erosion. Stream-side vegetation is needed to provide shade and lower water
temperatures. Modifying the stream flow can increase flow and flooding and
erosion. |
|
KI – 06
(Upper reach of Bear Creek in Hancock County)
Aquatic
Life – partially supported
Overall
Use – Partially Supported |
Habitat
Alteration |
Agriculture
Channelization
Habitat
Modification
Removal
of stream-side vegetation |
See
above |
RESOURCE CONCERNS
Resource concerns identified by the local planning committee, listed in order of
priority, are:
1.
Soil Erosion
2.
Nutrients and Pesticides
3. Stream Bank
Erosion
4. Livestock
Waste
5. Invasive
Species
6. Human Waste
7. Timber
Management
8. Urban Sprawl
9. Pasture
Management
10.
Information/Education and Landowner Involvement
11. Wildlife
Management
12. Wetland
Management
Soil
Erosion
Sheet,
rill and gully erosion on agricultural lands is responsible for increased
sediment, nutrients and pesticides in streams as well as decreased soil quality
and productivity. Causes are agricultural production practices. One-third of
all cropland fields (approximately 75,000 acres) in the watershed have rill or
gully erosion occurring.
Nutrients and Pesticides
Over-application and the misuse of fertilizers and pesticides on both
agricultural lands and on lawns can cause increased nitrogen, phosphorus and
pesticide levels in streams, lakes and groundwater supplies.
Stream Bank Erosion
Eroding
stream banks along Bear Creek, its tributaries and streams draining directly
into the Mississippi River (854 total stream miles) are responsible for
increased sediment in streams, decreased water quality and impaired aquatic
habitat. The causes are stream modifications (including channelization),
increased runoff and stream flow velocities (due to agricultural production
practices and removal of natural stream-side buffers) and natural causes, like
fallen trees.
Livestock Waste
Confined livestock waste and the improper land application of the waste has the
potential to run off into streams, increasing nutrients and E. coli bacteria
content, and decreasing the oxygen supply. A decreased oxygen supply has a
negative effect on fish and other aquatic life. Unlimited grazing animal access
to streams can also contribute to loss of aquatic habitat. More data is needed
on acres receiving livestock waste application and the number of grazing animals
with access to streams.
Invasive Species
Invasive species degrade natural areas by shading and crowding out native
species, poison the soil with allelopathic chemicals, and increase soil erosion
by eliminating the herbaceous under story growth with its fibrous root systems.
This increased soil erosion lowers the quality of the water and aquatic habitat
in streams.
Human Waste
Improperly functioning septic systems can contribute to E. coli bacteria above
acceptable limits, decreased oxygen supply, and an increase in viruses and
parasites in water bodies. Illegal dumping can restrict stream flow, pollute
water, and is aesthetically unpleasant.
Timber Management
Grazing
by livestock in timber increases soil erosion potential and decreases timber
production and wildlife habitat. Invasive species in wooded areas shade out
native herbaceous plants therefore decreasing biodiversity and increasing the
potential for erosion. Increased erosion lowers water quality and has a
negative effect on aquatic habitat.
Urban Sprawl
Urban
development often means more impervious surfaces and increased runoff and
sediment from construction sites. Both the increased runoff and sedimentation
result in a loss of aquatic habitat. Urban residents and businesses often
misapply or over apply lawn fertilizers and chemicals, which in turn decreases
water quality. The disposal of leaves and grass clippings in urban streams can
kill existing vegetation, and increase bank erosion. Yard waste in streams can
cause water quality problems related to high nutrient levels and organic
loadings, reducing the dissolved oxygen content of the water.
Pasture Management
Overgrazing and unlimited livestock access to streams can be responsible for
increased soil erosion, sediment, E. coli bacteria and turbidity in streams, and
decreasing aquatic habitat. Lower forage quality, low or poor soil fertility
and invasive species decrease profit. Keeping pasture land profitable is
important. If it is not profitable, this marginal land could be converted to
cropland and increase soil erosion rates.
Information/Education and Landowner Involvement
Lack of
good information on the conservation and wise use of natural resources is often
the reason for many of the problems listed above. Providing sources of
information, along with available technical and financial resources, will allow
watershed residents to make wise decisions on their actions that affect water
quality and natural resource conservation.
Wildlife Management
The
destruction of woodland edge habitat and agricultural production practices have
caused a decline in upland game like quail and rabbit. These practices also
increase soil erosion and decrease soil quality. The fluctuating duck
population is a concern. Land clearing near streams and lakes is degrading the
nesting habitat for wood ducks.
Wetland Management
Agricultural production practices have decreased natural wetland areas. Wetland
areas help filter pollutants and recharge groundwater reservoirs. Urban
developments often have a negative impact on wetland habitats, and the resulting
increased water runoff causes flooding problems.
GOALS AND OBJECTIVES
|
GOAL 1 |
OBJECTIVES |
|
Reduce sediment
entering streams.

|
Reduce sheet and rill
erosion on cropland.
Reduce ephemeral
erosion on cropland. |
|
Reduce soil erosion
on pasture land caused by overgrazing or poor vegetative cover. |
|
Reduce soil erosion
on timber land caused by grazing livestock.
Reduce soil erosion
on timber land caused by invasive species.
Reduce gully erosion
in timber land. |
|
Reduce soil erosion
on urban land during new construction. |
|
Reduce stream bank
erosion. |
|
Improve soil health
by controlling soil erosion, reducing soil compaction and |
|
GOAL 2 |
OBJECTIVE |
|
Improve water quality
in streams.

|
Work with farm owners
and operators to apply only the nutrients needed for growing crops. |
|
Reduce nutrients
entering streams due to improperly functioning septic systems. |
|
Address needs of
Concentrated Livestock Feeding Operations with waste storage and proper land
application. |
|
Proper use &
application of pesticides by agricultural producers, businesses and
homeowners. |
|
Reduce manure
entering streams from small livestock operations by assisting with waste
storage and proper land application. |
|
Reduce illegal
dumping along roads and in ditches. |
|
GOAL 3 |
OBJECTIVES |
|
Improve the health of
desirable vegetation.

|
Reduce invasive plant
growth by controlling their growth in pasture and timber lands. |
|
Improve timber
management for woodland production and wildlife habitat. |
|
Improve pasture
management for feed value and environmental quality. |
|
GOAL 4 |
OBJECTIVES |
|
Improve conditions
for game and non-game wildlife in the watershed.

|
Improve wildlife
habitat by providing the needed habitat (food, water, shelter and space). |
|
Maintain existing
wetland areas and restore areas to their original wetland status. |
|
Improve water quality
for aquatic species. Includes controlling soil erosion, eliminating stream
modifications and removal of stream-side vegetation. |
|
GOAL 5 |
OBJECTIVES |
|
Provide opportunities
for education and landowner involvement.

|
Hold public meetings
to gather input on local resource concerns and priorities. |
|
Increase public
awareness of the watershed planning effort and benefits of a watershed plan. |
|
Identify ways to
reduce negative impacts of urban development. |
Strategies to
Improve Resources in the Watershed
STRATEGIES AND COST
SUMMARY
|
Water Quality Soil
Erosion & Sedimentation Healthy
Vegetation Wildlife Habitat Information/Education
|
|
GOALS |
IMPLEMENTATION STRATEGIES
&
ALTERNATIVES |
SITE OR TARGET AREA |
COST ESTIMATE/SOURCE OF FUNDING |
|
    
|
1. Promote No-Till and Strip-Till Farming Practices. Sponsor an Annual
No-Till Seminar with U of I Extension
Look for additional incentives to encourage no-till and strip-till.
Provide information on the benefits of no-till based on research data. |
Farm operators with Highly Erodible cropland soils |
$600.00 annually from IDOA and business co-sponsors |
|
  
|
2. Identify erosion “hot spots” & target these areas for residue
management & structural practices. |
Sub-watersheds identified as having high erosion rates.
|
Cost Estimate: $ 300.00 per acre benefitted, 85,000 cropland acres
needing treatment. Total: $ 25.5 million
Illinois Conservation 2000 program
USDA-Environmental Quality Incentive Program
USDA-Conservation Reserve Program
EPA – 319 grant
Landowners/operators |
|
  
|
3. Work with livestock producers to implement grazing systems. Utilize
existing programs (EQIP) and other programs that may apply. |
Highly erodible pasture soils.
Prioritize by sub-watershed based on pasture proximity to streams. |
Average $ 875.00/acre. ($ 1.33/ft. for interior fence, estimated 10
acres/paddock.)
Acres needing grazing system not known at this time. Will need to
inventory. |
|
   
|
4. Work with U of I Extension to provide information on rotational
grazing and pasture management.
|
$250.00 per seminar/workshop
|
|
    
|
5. Promote timber management through Field Days, newsletters, news
articles, and seminars.
Encourage & provide incentives for the development of forest management
plans and timber stand improvement. |
Entire Watershed
Oak-hickory forests
Bottomland hardwood forests |
$
1000.00
Cost - $ 10 per acre for plan and $ 60.00 per acre for
implementing plan
Acres needed: |
|
   
|
6. Work with livestock producers to exclude livestock from wooded
acres.
|
Wooded acres with livestock present.
It
is estimated that 25% of the forest acres in the watershed are grazed. |
$
80.00 per acre on 8500 acres, or $678,000. |
|
  
|
7. Control gully erosion in timber by reducing runoff upstream (soil
erosion control on cropland) and controlling down cutting in stream beds
(stream stabilization). |
|
Illinois Conservation 2000 program
USDA-Environmental Quality Incentive Program
USDA-Conservation Reserve Program
EPA – 319 grant |
|
   
|
8. Implement structural practices to control soil erosion and water
runoff in developing areas. |
New construction sites
Areas with high water runoff |
Protecting Water Quality in Urban Areas Grant
Adams County SWCD Road Protection Project
City & County ordinances
Cost: $3000 per year for 3 years for pilot and demonstration projects. |
|
Water Quality Soil
Erosion & Sedimentation Healthy
Vegetation Wildlife Habitat Information/Education
|
|
GOALS |
IMPLEMENTATION STRATEGIES &
ALTERNATIVES |
SITE OR TARGET AREA |
COST ESTIMATE/SOURCE OF FUNDING |
|
    
|
9. Work with homeowners to implement cultural practices to reduce soil
erosion and water runoff on their property. |
New & existing areas with water runoff problems – primarily Quincy and
the 3 surrounding townships |
Protecting Water Quality in Urban Areas Grant - $3000 per year for 3
years
Other programs yet to be identified |
|
   
|
10. Work with landowners to control stream bank erosion.
|
Target actively eroding streambanks in KI-02 and KI-03.
Determine stream segments that would benefit from a watershed approach
to bank erosion control.
Target streams that drain into Quincy Bay to help reduce sediment
delivered to the Bay. |
$25 / lineal foot of bank protected plus technical assistance
Estimated cost for structural erosion control measures is $500,000.00.
Technical assistance 20% of cost, or $100,000.00 |
|
  
|
11. Increase buffer strips and filter strips along streams through use
of continuous CRP and other programs.
|
KI-02, KI-03 |
Cost $200.00 per acre
Estimated acres: 200
Estimated cost: $ 40,000 for planting
Annual Rental Payments: $ 25,000 |
|
    
|
12. Encourage landowners to maintain brushy draws through intensive
information/education program.
|
KI-02, KI-03, |
Not yet identified |
|
Water Quality Soil
Erosion & Sedimentation Healthy
Vegetation Wildlife Habitat Information/Education
|
|
GOALS |
IMPLEMENTATION STRATEGIES
&
ALTERNATIVES |
SITE OR TARGET AREA |
COST ESTIMATE/SOURCE OF FUNDING |
|
    
|
13. Provide an educational campaign for urban residents on stream bank
erosion control and water run-off. Utilize materials developed by Adams
County SWCD through Protecting Water Quality in Urban Centers grants.
Pursue additional funding through the same program and others that may
apply.
|
Cedar Creek, Curtis Creek |
$25/lineal foot of bank protected for structural measures plus technical
assistance
Estimated 5000 lineal feet of bank protection needed
Total estimated cost: $ 150,000 |
|
  
|
14. Promote removal of fallen trees thru education and incentives. |
Landowners with property along streams, with the 1st priority
being main Bear Creek |
Associated costs would be $1,000 per day. Programs not yet identified |
|
 

|
16. Work with landowners and operators to develop
Nutrient Management Plans for cropland and pasture.
Also work with U of I Extension on information/education programs and
agri-businesses on soil testing and recommendations. |
Subwatershed(s) with highest nutrient loading potential |
$15 per acre
C-2000 NMP/EQIP
Workshops/seminars - $300 each |
|
   

|
15.
Reduce livestock access to streams through the use of existing programs,
pilot programs available and information/education in cooperation with U
of I Extension. Practices: stream crossings and fencing
|
Subwatershed with the highest number of cow/calf operations with access
to streams |
$
1.33 per foot for interior fencing
| |