RECREATIONAL
TRAILS: EROSION CONTROL DESIGN/REPAIR TECHNIQUES
AND RATIONALE FOR SINGLE-USE TRAILS
Suzanne Mittenthal, Ph.D.
A.
SINGLE-USE TRAILS SERVE USERS MOST EFFICIENTLY.
At present, the nation's
trails aren't being used, they're being used up! Trail
conditions are deteriorating in public forests all
over the U.S. Conflicts between users are erupting,
as use levels on the nation's park and forest back country
trails exploded in the last century. Management has
been on a laissez-faire basis, with historically little
or no maintenance. A multiple-use management policy
allowing high-impact users such as horseback, mountain
bike, and ATV riders on most trails has caused widespread
damage on a majority of trails.
Impact (consumption)
varies greatly according to user type. Hiking has
the lowest impact of all uses, is the least "consumptive"
or erosive of soil and trail surface, and serves the
greatest number of users with the least maintenance
cost. Mountain bike use has much higher impact: bike
wheels leave a continuous track and dig deep when ascending
or braking, and bikers tend to go around protruding
stone or wood water diversion devices in their desire
to speed down trails. Horses dig divots in all but the
hardest surfaces, creating deep pock-marking in wet
weather. Except on rock, horses pulverize tough, dry
surfaces, which turn to mud when wet. Horses add pollution
in the form of wastes and alien seeds--and hikers are
asked to "leave no trace." Horse trails are very high
maintenance (Boone).
User conflicts are inevitable
as a result of crowding and the growing awareness that
the high-impact users are the source of the destruction.
They are not just the result of user antipathy. Lack
of maintenance and non-separation of users results in
deflection of dissatisfaction to users from managers,
who really bear the responsibility for degraded conditions.
User groups have different,
incompatible, goals for use of forest trails.
· Bike users: physical challenge, aerobic workout,
and thrill of a sport, in a natural setting. Eroded
trails can be considered part of the challenge (Bjorkman).
· Horse users: enjoyment of riding, Western culture,
natural setting for the sport. Eroded trails can be
considered part of the culture, may not interfere with
the view from the horse.
· Hikers: require a more direct, close-up interface
with nature, experience the forest for its own sake;
bad trails ruin the experience, impede their progress,
or actually endanger them.
Asymmetry of Aggravation
Principle Mandates Single-Use Trails: High-impact
users aggravate all, but are harmed by none; low-impact
users aggravate none, but are harmed by all. ATVs destroy
trail surfaces and forest peace for all other users.
Multiple-use trails unfairly impact hikers, destroying
the footbed and vegetation close to the trail. With
hikers' goals unattained; they are accused of being
selfish if they complain or ask for single-use trails.
An outcomes-based approach
to trail management must be taken. Campaigns to
"educate" users to accommodate to deteriorating trail
conditions and declarations that "multiple-use"--one
size fits all--trails should satisfy all users are not
sufficient. Proper maintenance of high-impact sport
trails is expensive, and requires regular maintenance.
Horse and bike miles should be reduced to the number
of sustainable trail miles. Managers have a responsibility
to provide users access to trails only if they are able
to protect the resource and not diminish other users'
enjoyment. Wider, hardened trails, usually requiring
machine maintenance, are treatments that distance hikers
from the natural experience. For these reasons, single-use
trails are the only justifiable management plan.
B.
APPROACH TO COST-BENEFIT ANALYSIS OF TRAIL PROBLEMS
Recreational trail planners
and users must acknowledge the different needs and trail
installation and maintenance costs of the three user
groups: hiker, horseback rider, and biker.
1. Analyze the Source of Trail Problems.
· Effects of specific
users
· Poor design: too-steep
grades? improper drainage?
· Lack of maintenance
2. Assess Amount of Use: Numbers, Types, Trips/Hours.
3. Identify Cost of Maintenance Per Mile Per User
for Each Type of Use and Impact.
4. Analyze the Function of Each Trail in the System.
· Determine which
trails receive highest use from each user group.
"L.A.C." teams are useful for making political decisions,
but are not appropriate for this evaluation of trail
functions. Some may serve as "access" routes to destinations
for all groups, and require overlapping "multi-use"
for some distance.
5. Develop a Cost-Benefit-Based Rehabilitation and
Maintenance Plan.
· Allocate trails
to single-use systems, on basis of function survey,
condition, and cost of expected repairs and maintenance.
· Ensure that methods
adopted suit both terrain and users; this requires
surveillance and feedback. Using gravel on trails that
users (horses) won't walk on is counterproductive.
· Repair existing
trails before destruction is irreversible; close
trails if necessary until repaired.
· Stop practice of
abandoning ruined trails; this sets wrong example
and encourages development of additional user trails.
Limiting miles of high impact use enables managers to
concentrate funds and volunteer efforts on maintenance.
The goal is the preservation of the natural resource,
the primary goal of the resource planner and manager.
C.
CONSTRUCTION OF EROSION CONTROL MEASURES: DRAINAGE
Protection of recreational
trails involves two factors: limiting the impact of
users on trail surfaces, and limiting the erosive effects
of water on trails. Both can be controlled somewhat
by managing--directing or diverting water drainage--on
trail surfaces.
1. General Design Principles:
· Build drainage features into trails as they
are constructed; don't plan to add later when problems
develop.
· All drainage design principles apply to
all user types.
· Surfaces require much more hardening for
the high-impact users, greater width, and usually
machine-maintenance.
· Water-diverting designs involve trail
dips, tilts, or reverse grades which actually
route the trail and water off the slope,
then redirect the trail back up.
· Water bars are no longer advised: placed
in the "fall line" of the trail, they fill up with leaves
or silt; newer deep trench types get cut through. Both
eventually become ineffective if not cleared or repaired.
Trail/water-diverting designs need little/no
maintenance.
· Modifying existing straight-line trails
with drainage dips is time-consuming. The pay-off
is, of course, that such improvements extend the life
of trails by decades.
· Drainage concepts are simple, but application
requires training. Different grades and types of
slopes demand different techniques. It takes practice
to develop one's eye to see where to apply drainage
dips, side sloping of the trail, reverse grades, or
switchbacks with water channels at the turns, and how
to apply these principles to open grassy slopes as well
as forest.
2. Tread Wear on Flat Surfaces: Some tread wear
is inevitable. Ways to prevent the wearing of deep ditches
over time on flat surfaces:
· Locate trails on edges of slopes, so the tread
can deepen slowly without ditching. · Locate trails
at edge of meadows, if at all possible.
· Artificial underlays or graveling may be necessary,
as soil pulverized in dry weather on a flat surface
becomes mud when it rains.
· Line cross-path drain channels with logs; keep
channel free of gravel for passage of water.
3. Trails on Slopes.
· Out-slope trail surface (angled slightly
sideways), so water drains off to the side instead of
being channeled down the trail. Do not line edges
of trails with cribbing. Trails tend to deepen and
channel with wear over time; out-sloping may need renewal
over the years.
· Switchbacks are used to wind a trail
across and down a slope, to lengthen it and reduce the
grade. On grassy slopes, turns should be designed to
occur at rock outcroppings, bushes, or any structure
to prevent short-cutting and keep hikers on the trail.
The number of turns in the switchback should always
be kept to a minimum, to reduce short-cutting.
4. Diverting Water OFF Trail:
· Install drains at bend of switchback
above turn to channel water off the trail, using stone,
treated timber or available logs. This results in a
step down at the turn for the user. Stone or strong
timbers anchored with rebar must be used for horse trails.
Sometimes slope allows water to fan off the bend.
· Use self-cleaning Reverse Grade dips,
5-foot diversions of the trail stepped down slope then
5 feet back up again. Water leaves the trail as the
trail is stepped back up. Send the trail around a tree,
or disguise the dip with a pile of rocks and a fern.
· Grade dips: lowering of trail below
grade for 10 feet, with a tilt down slope. Watch for
naturally occurring dips, which can be accentuated,
to drain water off long, straight trails.
5. Cross Drains: Prevent, divert, or slow water
drainage across trail from up the slope.
· Pack gullies above the trail with logs
across the flow to slow water moving across the trail;
pack the gully below the trail with cross-wise log sections
to prevent undercutting.
· Pave the trail with rock slabs to prevent
water from washing it away. Rock surface must be flat,
not tilted downhill or it will be hazardous.
6. Slow the Movement of water on the trail
where keeping it off is impossible. Water bars
or weirs--log or rock-- across the direction of flow
may have to be installed in sections of trail where
no other drainage option is possible, in old road beds
with high sides, for example. Just slowing the flow
can help to control damage. Downed trees may be trimmed
and left in place to slow rain flow, and also interfere
with and slow any unauthorized uses of trail.
References
Bjorkman, Alan W., Off-Road Bicycle and Hiking
Trail User Interactions: A Report to the Wisconsin Natural
Resources Board, Wisconsin Department of Natural Resources,
Bureau of Parks and Recreation, 101 S. Webster, Madison,
Wisconsin 53707 (606/266-2181).
Boone,
Tony, Arrowhead Trails, Inc. (www.mountain-bikes.com
(303)258-7425, personal communication May 1, 2000.
This
paper is a condensation of remarks presented at the
National Association of Recreation Resource Planners
conference in Albuquerque on May 4-5, 2000.