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FINAL REPORT 2/21/13
Soil Conservation Plan
For
The Humbug Off-Highway Vehicle Recreation Area
Happy Camp/Oak Knoll Ranger Districts
Klamath National Forest
For Information Contact: Joe Blanchard
Soil Scientist
Klamath National Forest
(530) 841-4591
2
Soil Conservation Plan
For
The Humbug Off-Highway Vehicle Recreation Area
Introduction
This Soil Conservation Plan covers the development of the Humbug OHV area, which is
located on the Klamath National Forest (KNF) approximately 9 miles northwest of
Yreka, CA. The recent Record of Decision (July 2010) for the Travel Management EIS
designates a 5 acre staging area and approximately 21 miles of motorized trails.
Development of the staging area includes fencing the perimeter of the site, construction
of new ingress/egress, graveling the parking area, boulder placement to control vehicle
access, installation of a double vault toilet, construction of loading ramp, installation of
information boards and site identification signing, reclamation of two old
ingress/egresses, and construction of a sediment basin. Maintenance of the trail system
may include actions such as improving the trail tread, construction of minor reroutes,
improving trail drainage with the construction or reconstruction of water bars and
catchment basins, cleaning out catchment basins, and trail brushing.
This Soil Conservation Plan has been prepared to meet California State Parks - Off-
Highway Motor Vehicle Recreation Division, Grant and Cooperative Agreement
requirements for Soil Conservation for specific projects where ground disturbing
activities are proposed and for which funding is requested. The goal of the Humbug Off-
Highway Vehicle (OHV) Soil Conservation Plan is to demonstrate how the Soil
Conservation Standard is being met or will be met in the project areas funded with grant
funds. Best Management Practices (BMPs) for OHV Facilities and Use (R5 FSH
2509.22 Water Quality Management Handbook) will be used to achieve the California
State Parks 2008 Soil Conservation Standards. The soil standard specifically requires
management of OHV activities to avoid impacts to both on-site and off-site resources,
including water quality.
Work to monitor and improve the Humbug OHV trail system has been in place since
2010. A work order was completed in 2010 that installed erosion control measures and
arched culverts. From 2010 to 2012 all of the trails designated through the Travel
Management EIS were monitored as an initial assessment of trail conditions using the
GYR form (see Appendix A and B form details). Results of this initial survey were used
to prioritize future maintenance and monitoring needs.
Protocol for assessment, maintenance and monitoring are identified below.
Protocol for Assessment:
A. Water and mechanical erosion protocols will be followed as outlined in the U.S.
Forest Service Revised OHV Trail Monitoring Form (GYR Form) and Training
Guide, July 30, 2004. The GYR form will be used to meet assessment protocols.
(See GYR Form for rating definitions in Appendix B)
B. Water and sediment control measures would be assessed using the GYR Form.
C. Tread condition will be assessed using the GYR Form.
3
D. Off-site impacts due to water and wind carried sediments will be assessed by
visual inspections of boundaries, estimates of quantities will be performed if any
are observed to determine if significant impacts are occurring.
E. Watercourse crossings will be assessed using the GYR Form.
Protocol for Maintenance:
A. In consideration of A through E above: Maintenance work will be done in
accordance with the BMPs 4-7.1-4-7.9 as described in the R5 FSH Handbook
2509.22, the Trail Management Handbook FSH 2309.18, Standard Specifications
for Trail Maintenance and Construction EM 7720-104, the Trail Construction and
Maintenance Notebook 0723-2806-MTDC, and the maintenance standards and
guidelines in A Field Evaluation of the Use of Small Trail Tractors to Maintain
and Construct OHV Trails on National Forests in California, USDA-Forest
Service Pacific SW Region, August 22, 2001
B. Maintenance schedules will be established utilizing monitoring reports developed
as a result of the GYR and TRACS trail condition surveys and other periodic
inspections.
Protocol for Monitoring:
A. The objectives for monitoring to determine:
a. Extent and severity of erosion occurring.
b. Conditions or combination of conditions causing accelerated erosion.
c. Where erosion is occurring.
B. Monitoring parameters include:
a. Informal monitoring of conditions by volunteers, visitors, and staff.
b. Formal monitoring by trained staff during inspections of specific trails
using the GYR Form, photo-points, and trail logs.
c. Formal monitoring by trained staff of open water crossings using the GYR
Form.
C. Monitoring site selection will be determined by:
a. Past monitoring results and available budgets. Note: Staff time for
monitoring may be funded through the OHV Ground Operations grant
b. Past maintenance records and institutional knowledge of past practices and
occurrences.
c. Results from the Initial assessment of Humbug OHV Trails and Open
Riding Area.
D. Monitoring schedules will be determined by:
a. Known historic weather patterns.
b. Visitor use patterns.
c. Availability of trained staff.
4
E. Data collection will be performed by staff that has been trained by the Klamath
National Forest staff to ensure quality assurance/quality control and compliance
with USFS standards.
F. Data management will be performed by the Klamath National Forest staff.
G. Monitoring methods for trails will consist of:
a. Monitoring methods will be followed as outlined in the U.S. Forest
Service Revised OHV Trail Monitoring Form (GYR Form) and Training
Guide, July 30, 2004 (See GYR Form in Appendix B)
b. Annual monitoring will be performed for trails that are high-risk and high
maintenance. These include any trails with sections rated in the “red”
condition class or more than half of the total length rated in the “yellow”
condition class. Also to be included in annual monitoring are trails with
stream crossings rated as “yellow” and the Humbug Open Riding Area
(See Appendix B for a list of trails included in annual monitoring).
c. Trails that have been rated as mostly in the “green” condition class are
considered more stable and will be monitored on a three year rotation (See
Appendix B for a rotation schedule).
H. Monitoring methods for the Humbug Open Riding OHV Area will consist of:
a. Photo points of the parking area, sediment basin, and hill slope above the
parking area
b. Checklist for the following items:
1. Sediment basin is functioning to trap erosion from hillslope and
no sediment is leaving the Open Riding Area.
2. No evidence of hazardous spills in the parking area
3. Sanitation facilities are functioning properly
Design and Construction Elements
A. Appropriate level survey and environmental review will be completed prior to
construction.
B. Work will be done in accordance with the BMPs 4-7.1-4-7.9 as described in the
R5 FSH Handbook 2509.22, the Trail Management Handbook FSH 2309.18,
Standard Specifications for Trail Maintenance and Construction EM 7720-104,
and the Trail Construction and Maintenance Notebook 0723-2806-MTDC.
Monitoring and Soil Conservation Standard Report
The monitoring report will be submitted annually. For trails selected for the yearly
monitoring report the following will be included:
A. Historical Condition; consider the previous trail improvement and monitoring
work for each trail:
5
a. Humbug OHV Trail maintenance work completed by Trails Unlimited in
2010. Includes write-up, map, and photos (Details on file at the KNF
Supervisors Office).
b. Initial Assessment of all trails and the Humbug Open Riding Area from
2010 to 2012 using GYR Forms. Includes maps detailing condition of
trails as “red”, “yellow”, or “red”, Data sheets, and photos. See
Attachments A and B.
c. Any other monitoring documentation.
B. Change Analysis
a. Determine the percentage of “green”, “yellow”, and “red” condition for
each trail and compare to the Initial Assessment or most recent data.
b. Documentation of any changes to water crossings on the affected trail
system and pre and post monitoring results.
c. Documentation of any changes to drainage structures (drainage dips, water
bars, reverse grades, etc) on the affected trail system and pre and post
monitoring results.
d. When annual maintenance was last performed and justification if it was
missed.
C. Findings:
a. Document the trend in condition of trails, water crossings, and the open
riding area.
b. Assess the need for maintenance to reverse negative trends or risks to
water quality.
c. Document any maintenance or construction activities and how trails,
crossing, and the open riding area are affected
d. Document resource benefits found from any maintenance or construction
activities.
D. Conclusions:
a. Recommend maintenance or trail improvement projects for sections of
trails, crossings, the open riding area
b. Recommend immediate corrective action if adverse effects to water
quality are found. Corrective actions may include, but are not limited to:
i. Temporary or permanent erosion and sediment control treatments
ii. Barriers and signing to redistribute use
iii. Temporary closure of trails or areas until completion of corrective
action
iv. Partial or total closure and restoration of trails or areas
v. Reduction in the amount, type, or season of OHV use
c. State goals for next year.
Compliance Action Plan:
Soil and watershed conditions within OHV use areas will be protected by a variety of
different management tools. In addition to the GYR monitoring process described in the
6
sections above and the appendices, these additional components are an on-going part of
the Forest’s OHV program. These components include public education through signing
and through the KNF website, enforcement of trail closures by law enforcement,
coordination with the local OHV user group, and ongoing OHV improvement projects.
Public Education:
As of Jan 1 2013, the KNF has released Motor Vehicle Use Maps (MVUM) to inform the
public of which trails are open for motorize use, including OHV use. If a route is not
shown on the MVUM, then it is not open to public motor vehicle travel. To help identify
routes that are available for motor vehicle use, signs have been placed on the entrances to
these roads and trails. However, since the MVUM includes the official information on
designation of motor vehicle routes, it is the user’s responsibility to reference the
MVUM, to stay on designated motor vehicle routes and follow terms of allowable use.
Law Enforcement:
Forest Service employees, including law enforcement employees and Forest Protection
Officers, will continually check with the public to encourage compliance and clarify
information printed on the MVUM. There will be a transition period to ensure that
information on the requirements stated on the MVUM is known by the public. The public
is asked to let their local Forest Service office know if they see some activity occurring
that does not seem to be allowed by the MVUM. The Klamath National Forest is working
with local and State governments to coordinate education and enforcement. Once the
transition period is complete, and Forest users know about the requirements stated on the
MVUM, violations will be issued. Violations of 36 CFR 261.13 are subject of a fine up to
$5,000 and/or 6 months imprisonment (18 U.S.C. 3571(e)).
Coordination with OHV User Groups:
The Forest has coordinated closely with the Siskiyou County Off-Road Riders (SCORR),
a 200 member local OHV club for many years. SCORR has been actively involved in the
Motorized Travel Management planning process since 2005. The club provided trail
inventory data, document review and comment, and assistance with the staging area
design. Eventually the Forest expects to enter into an agreement with the club for trail
maintenance.
Humbug Staging Area Development Project. In the fall of 2012, the Forest Service
initiated an environmental assessment to develop the 5 acre Humbug Open Riding Area.
The Forest Service proposes to add the following facilities within the open riding area: a
single, new entrance; a graveled parking area; a double vaulted toilet; a
loading/unloading ramp; two individual picnic/ camp sites with tables and fire rings; a
children’s riding area; signs; fencing and/or boulders to define use areas, a group picnic
area, and a sediment basin. Upon completion of NEPA, the Forest Service expects to
apply for construction funding from the California Off-Highway Motor Vehicle
Recreation Division. If successful, construction would occur in 2014.
Humbug Drainage - Trail Reroutes for Resource Protection Project. The Forest is
currently conducting an environmental analysis for this project. Five segments of
7
motorized trail #5596 would be relocated (vacated) from unsustainable locations (e.g.
unmaintainable over-steepened slopes) and relocated (rerouted) in order to provide a
sustainable motorized recreation opportunity. Upon completion of NEPA, construction is
expected to occur in the fall of 2013.
8
Soil Conservation Plan
Appendix A
Initial Condition Monitoring of Humbug OHV Rec Area
The initial condition for the Humbug Off-Highway Vehicle (OHV) Recreation Area was
assessed using the Forest Service Revised OHV Trail Monitoring Form (GYR Form) and
Training Guide from 2010 to 2012 in an effort to establish a baseline condition of
motorized trails established under the Motorized Travel Management process. The results
of the initial condition assessment of the trails in the Humbug area will be used to set
priorities for yearly monitoring and maintenance. The trails that are high-risk or high
maintenance will be monitored on a yearly basis. These include any trails with sections
rated in the “red” condition class or more than half of the total length rated in the
“yellow” condition class. Also to be included in yearly monitoring are trails with stream
crossings rated as “yellow” and the Humbug Open Riding Area. Trails that have been
rated as mostly in the “green” condition class are considered more stable and will be
monitored on a three year rotation.
Initial assessment Map of OHV Trails in the Humbug drainage using GYR rating
protocol
9
Summary of Initial Condition Data and Monitoring Schedule for Humbug Open Riding
OHV Area and Trails Located in the Humbug Drainage. Initial Condition Rating
Trail Number
Trail Designation
Initial Condition Monitoring Date
Length or Area
G (%)
Y (%)
R (%)
# of Y Stream Crossings
Monitor Annually?
Monitor on 3 yr rotation
Open Riding Area
Open to cross country Travel
12/12/2012
5 acres 0 X
5594 Trails Open to Vehicles 50" or Less in Width
10/30/2012
2.58 miles
88 12 0 0 X
5595 *Closed 10/30/2012
1.12 miles
12 29 59 0 X
5596 *Closed 2/24/2012 2.57 miles
72 16 12 0 X
5597 Trails Open to Vehicles 50" or Less in Width
10/30/2012
0.43 miles
54 22 24 0 X
5598 Trails Open to Vehicles 50" or Less in Width
11/14/2010
0.89 miles
64 36 0 0 X
5599 Trails Open to Vehicles 50" or Less in Width
11/14/2010
0.74 miles
48 52 0 0 X
55100 Trails Open to Vehicles 50" or Less in Width
11/14/2010
1.88 miles
81 19 0 0 X
55101 Trails Open to Vehicles 50" or Less in Width
11/14/2010
2.43 miles
79 21 0 0 X
55102 Trails Open to Vehicles 50" or Less in Width
10/30/2012
0.84 miles
62 38 0 3 X
55103 Trails Open to Vehicles 50" or Less in Width
11/1/2010 1.71 miles
89 11 0 0 X
55104 Trails Open to Vehicles 50" or Less in Width
11/1/2010 0.41 miles
78 22 0 0 X
55106 Trails Open to Vehicles 50" or Less in Width
11/1/2010 0.29 miles
100 0 0 0 X
55108 Trails Open to Vehicles 50" or Less in Width
11/27/2012
0.57 miles
80 20 0 0 X
55109 Trails Open to All Vehicles
11/27/2012
3 miles 99 1 0 0 X
*Although designated in the 2010 Motorized Travel Management Record of Decision,
these trails are currently closed until additional mitigation measures are completed.
10
Results from the initial condition monitoring indicate that a majority of the OHV trails
located in the Humbug Drainage area are rated with predominantly “green” condition
class. For these trail segments water control is provided by waterbreaks to divert runoff
therefore preventing erosion on the trail surface. Additionally, sediment traps are fully
functional, tread wear is minimal, and unauthorized user-created trails are limited. Most
stream crossing were also rated in the “green” condition class, which means that the
approaches are short and have a gentle gradient, and the tread is stable with little signs of
erosion.
A few trails are rated with a high percentage of segments in the “yellow” condition class.
These trail segments either have presence of rilling on more than 1/3 of the distance
between waterbreaks, sediment traps are nearly full, or user-created unauthorized routes
are common. Stream crossing rated as “yellow” either have approaches that are short and
steep or long and gentle and minor erosion is evident. Yearly monitoring and regular
maintenance are needed to ensure that steps are taken to address “yellow” trail
conditions. The goal is to move as many segments into the “green” condition class as
possible and to prevent segments from deteriorating into a “red” condition class.
Three OHV trails in the Humbug Drainage have segments rated in the “red” condition
class. These trail segments have gully erosion due to breached or absent waterbreaks on
steep slopes. In all cases, sediment is filtered or deposited before reaching a watercourse.
These segments have not been degraded to the point where restoration is not possible
without re-routing to avoid steep sections or construction of waterbreaks. Resources such
as water quality and soil productivity have not been significantly impacted by these trail
segments, but steps need to be taken to fix these issues. Currently, trails 5595 and 5596
are signed and closed to OHV vehicles until mitigations have been implemented to
protect resources. The Humbug Drainage-Trail Reroutes for Resource Protection Project
is currently being analyzed to re-route the “red” segments of trail 5596. Trail 5597 has a
short segment in “red” condition class and is currently open to OHV traffic. Gullying on
this segment is occurring as a result of breaches in two waterbreaks. A plan is in place to
repair these two waterbreaks as soon as conditions allow in the spring of 2013.
Monitoring of the Humbug OHV Open Riding Area indicates that there is no current
resource damage at this site. Photo points and a checklist are in place to monitor the
condition of the parking area, sediment basin, and hill slope above the parking area once
development of the staging area is complete.
11
Soil Conservation Plan
Appendix B
GYR Form and Data Management Methods
This document details the OHV monitoring and data management practices and
procedures to standardize and organize monitoring efforts on the Klamath National
Forest
1. Determine what trails are scheduled for monitoring according to results of initial
assessment or monitoring data from the previous year.
Results from the initial assessment indicate that five trails will be monitored on a yearly
basis until these trails fulfill the following conditions: No sections rated as “red”, less
than 50% rated as “yellow”, no stream crossing rated as “yellow”. These trails include
5595, 5596, 5597, 5599, and 55102. The Humbug Open Riding Area will also be
monitored on a yearly basis because of the high concentration of use at that site. Nine
trails were rated with mostly “green” sections and will be monitored on a three year
rotation. These trails include 5594, 5598, 55100, 55101, 55103, 55104, 55106, 55108,
and 55109. Year 1 will include trails 55103, 55104, and 55106; Year 2 will include trails
5598, 55100, and 55101; Year 3 will include trails 5594, 55108, and 55109. The yearly
total miles of trail to monitor will be 8.11 miles in year 1, 10.9 miles in year 2, and 11.85
miles in year 3.
2. For each of the trails chosen for monitoring, collect previous monitoring data from the
digital database. Results from the initial assessment are located on the shared T drive:
A line shapefile with each trail split into “green”, “yellow” or “red” sections can be found
at:
T:\FS\NFS\Klamath\Program\2500Watershed\2550SoilMgmt\WorkSpace\OHV\SoilCon
servationPlan\HumbugTrails.shp
A point shapefile with attribute data of specific monitoring results and linked photos can
be found at:
T:\FS\NFS\Klamath\Program\2500Watershed\2550SoilMgmt\WorkSpace\OHV\SoilCon
servationPlan\HumbugInitialAssessmentWaypoints.shp
3. Use the OHV Trail Condition Rating Form below, a GPS unit, and a digital camera to
conduct yearly monitoring.
4. Update the digital database with yearly monitoring data.
12
OHV Trail Condition Rating Form
Trail Name _____________________ Trail No. _________ USGS Quad __________________ Begin Segment ____________________ End Segment ____________________
RATING (GYR) _____ GPS Ref ______________________________ Rated By ________ Date ________ Reviewed By __________________ Date ________ Page ___ of ___
Section B = Begin E = End
SectionLength
G-Y-R Condition
Codes Cause Codes
Trail Gradient
Crossing Approach
L R Management Codes and Comments
Photograph Number(s)
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
B
E
13
Green Conditions Yellow Conditions Red Conditions G1 Water control is provided by enough functional
waterbreaks to divert runoff from the trail before it has the volume and velocity to cause erosion. Where present, rills occur on less than 1/3 of the distance between waterbreaks.
Y1 Waterbreaks do not divert all runoff from the trail because they are nearly filled to capacity and/or are partially breached, or spaced too widely. Where present, rills occur on more than 1/3 of the distance between waterbreaks
R1 Waterbreaks no longer divert runoff from the trail because they are full and/or have been breached, or are absent or spaced too widely. Gully or rill erosion may be present.
G2 No accelerated erosion off-trail. Runoff at
waterbreak outlets and on slopes adjacent to the trail is dispersed effectively. All sediment is filtered by vegetation or litter.
Y2 Rill erosion and/or sediment deposition occurs at waterbreak outlets and/or on slopes adjacent to the trail. All sediment is filtered or deposited before it reaches a watercourse with a scoured channel.
R2 Gully erosion occurs at waterbreak outlets or on slopes adjacent to the trail and/or sediment is transported to an intermittent or perennial watercourse.
G3 Sediment traps, where present, are all functional
and have adequate capacity for at least one season of use. Trapped sediment can be retrieved during normal maintenance.
Y3 Where present, most sediment traps are full or nearly full, but still functional. Most trapped sediment can be retrieved during normal maintenance.
R3 Where present, sediment traps have been breached and have a plume of sediment and/or a gully below the breach. Most sediment cannot be retrieved.
G4 Tread wear is minimal. Tread is generally incised
less than 6 inches. Tread wear is generally evident on less than 1/3 of the distance between waterbreaks or on less than 1/3 of the tread width.
Y4 Tread wear is evident. Tread is generally incised 6 to 12 inches and tread wear is generally evident on more than 1/3 the distance between waterbreaks and on more than 1/3 of the tread width. If present, “whoops” or “stutterbumps” and high berms are well-developed.
R4 Tread wear is severe. Tread incision is generally greater than 12 inches deep and tread wear is generally evident on the entire distance between waterbreaks. If present, deep “whoops” and “stutterbumps” force traffic off the trail.
G5 Tread width is generally no greater than 1.5 times
the design width for the designated use. Y5 Tread width is generally greater than 2 times the
design width for the designated use and appears to be increasing.
R5 Tread width is generally greater than 3 times the design width for the designated use and has caused or is causing severe resource damage.
G6 Unauthorized user-created trails are limited to
single tracks or single passes generally less than 300 feet long. Tracks are not eroded and have little effect on water control.
Y6 Unauthorized user-created trails are common, well-defined, and generally greater than 300 feet long. Water control is inadequate. Areas with resource damage can be revegetated/restored with ordinary effort.
R6 Unauthorized user-created trails have caused severe resource damage such as gully erosion, eroded hillclimbs, or extensive damage to vegetation and/or sensitive habitat. Restoration will usually require a major effort (e.g., large equipment, topsoil replacement, etc.)
G7 Approach to watercourse crossing is short and
has a gentle gradient. Tread is stable, shows little evidence of erosion, and is at design width. No damage to riparian vegetation outside the tread.
Y7 Approach to watercourse crossing is short and steep or long and gentle. Tread may show some evidence of erosion and may show evidence of widening. Minimal damage to riparian vegetation.
R7 Approach to watercourse crossing is both steep and long and/or tread is unstable and shows evidence of accelerated erosion. Approach may be widening and damaging riparian vegetation.
G8 Other: (explain in notes) Y8 Other: (explain in notes) R8 Other: (explain in notes)
Cause Codes C1 Waterbreaks not constructed to design standards
C2 Waterbreak spacing is too wide for conditions
C3 Cascading runoff from a trail or road upslope
C4 Cascading runoff from an impervious surface upslope
C5 Wet area caused by a seep or spring
C6 Excess soil moisture at time of use
C7 Trail section is poorly located (describe)
C8 Trail gradient is too steep for the type and/or amount of use occurring
C9 Segment was not designed for the type or amount of use occurring
C10 Brush or log is blocking trail
C11 Rocks or roots exposed in tread
C12 Barriers (natural or constructed) to control traffic are lacking
C13 Mechanical erosion makes maintenance ineffective
C14 Storm intensity unusual or unique for the area (not for use in deserts)
Management Codes M1 Segment is overgrown with brush
M2 Signing is inadequate to control use and protect resources
M3 Barriers (natural or constructed) are inadequate or lacking
M4 Trail is not designated for type of use occurring
M5 Rutting or vegetation damage in meadow, spring, or wet area
M6 Damage to sensitive plant habitat or other sensitive area
M7 Unauthorized traffic in dry washes
M8 Vandalism (e.g. shooting signs, destroying barriers, etc.)
M9 Users lack an awareness of need for resource protection
M10 Land management agency presence is lacking
M11 Other:
M12 Other:
M13 Other:
M14 Other:
14
An example of an ArcMap screen print of Humbug OHV Trails data, zoomed in to Trail
55102. The line shapefile splits each trail into “green”, “”yellow”, or “red” sections. The
point shapefile contains specific monitoring data for each section. Many points are
hyperlinked with photos.
15
An example of an ArcMap exported Attribute Table data for Trail 55102. Data from the
OHV Trail Condition Rating Form are spatial reference by being entered into the GIS
database.
Point Date GYR
Cond Code
Cause Code
Trail Slope (%)
Crossing L
Crossing R
Rated By
Comments Photo Link
55102_1
10/30/2012
G 5-15 JHB Waterbars in place. Sediment traps constructed, not yet filled in
Yes
55102_2
10/30/2012
G 5FT, 5%
50FT, 10%
JHB ephemeral stream crossing, in good condition
Yes
55102_3
10/30/2012
G 5 JHB
55102_4
10/30/2012
Y7 C7 5FT, 50%
5FT, 50%
JHB Steep approach on intermittent crossing
Yes
55102_5
10/30/2012
G 5 JHB
55102_6
10/30/2012
Y7 C7 15FT, 5%
15FT, 5%
JHB Grantic soil moved 5ft into channel
Yes
55102_7
10/30/2012
G 5-25 JHB Restoration area-unathorized trail well marked and effectively blocked
Yes
55102_8
10/30/2012
Y6 C12 20FT, 3%
100FT, 5%
JHB unathorized hillclimb trail takes off near crossing and has 50% slopes. Needs to be marked and blocked
Yes
55102_9
10/30/2012
Y4 C12 10 JHB 6" ruts caused by truck traffic on trail
Yes
55102_10
10/30/2012
G 15 JHB
55102_11
10/30/2012
Y1 C2 20 JHB Water channeled in a gully (looks like remnant from before trail work)
Yes
55102_12
10/30/2012
Y1 C2 15-20
JHB Not enough waterbreaks to prevent rill erosion on trail
Yes
55102_13
10/30/2012
Y1 C2 20 JHB Not enough waterbreaks to prevent rill erosion on trail
Yes
55102_14
JHB
16