Alpine Restoration in Colorado's Rocky Mountains
These approaches to restoring closed social trails on Colorado's 14,000-foot peaks were developed by Jim Ebersole, Robin Bay, and Dave Conlin. This handout was prepared by Robin Bay for use at Colorado Fourteeners Initiative staff trainings.
Restoration
& Revegetation Methods
Restoration Training
Colorado Fourteeners Initiative
Prepared by Robin Bay
9 June 2001
Goals of ecological
RESTORAtION
Reconstructing the original drainage system
Maximizing the systems ability to retain water - to avoid water channeling
Restoring the function and structure of the vegetation
Restoring species composition
Maintaining native genetic diversity
Soil conservation and stabilization
Aesthetics
Levels of
restoration - USFS guidelines
Type I - Restoration attempting to enhance all biotic and abiotic factors of disturbed zone in order to restore the natural processes of the system. Common methods are threefold: slope stabilization, revegetation, post-closure research and monitoring. These methods include: seeding, turf transplanting, seed propagation, soil enhancement, etc.
Type II - Closing of social trails, signing, seeding, construction of check dams to mitigate erosion, and transplanting.
Type III - Closing and disguising of social trails in an attempt to keep hikers off non-system trails.
Type IV - Passive restoration - closing trails and allowing natural succession to occur.
steps to restoration
Outlined below are the
steps required for Type I restoration. If a different level of
restoration is prescribed then not all of the
steps would be
followed to the same extent.
The methods and results described here are based on what we currently know about alpine revegetation. As more restoration and revegetation projects are completed here in Colorado and at other locations, new information will be added and the methods will undoubtedly be altered and improved.
Step 1: Closing social trails
Goal: Keep hikers off
Signs
Rock barriers
Disguising the trail (willows, branches)
Rock fill
Step 2: Stabilizing social trails
Goal: Stop
erosion and attempt to recreate the original contour of the slope
Terracing - should be back filled at an angle to match original contour
Crib steps in steep trail sections
Check dams to mitigate water channeling
Drainage structures to remove water from trails
Step 3:
revegetation
Goal: Restore
the function and structure of the vegetation
Considerations
Vegetation cover that can be achieved in a short time
Cost of implementation (materials and labor)
Materials - plant materials, soil, erosion matting, etc.
Physical effort
Aesthetics
Active
revegetation
I. Seeding
Considerations
Least time and effort required
Low cost
Slow to achieve vegetation cover
Very susceptible to disturbance, climate change, etc.
Implementation
Best to use native seed collected near to the restoration site
- Important to collect from the same microhabitat where seed will be spread
Use the dominant species in the community
In general better to use a mix of species including those with different life histories and
physiological traits (mixture of graminoids and forbs)
Seed should be collected after seeds are mature, usually in late August/early September
Mature seeds (especially of graminoids) will often fall out in your hand
It is okay to collect some of the inflorescence with the seeds, but try to break it up as
much as possible before spreading
If seeds are not spread immediately they should be stored cool and dry
Spread seed at rate of 20 - 40 g/m2 (wet weight including some inflorescence material)
Rake area to loosen soil before spreading seed
Cover seed with a thin layer of soil so it is less likely to blow or wash away (you can use
the soil that was
raked off.
Table 1. Some common species that have been successful for seeding in the alpine. This is by no means a complete list of possible species. Any common species present can be used.
(Pictures and descriptions of these species are attached at the end of this packet.)
|
Graminoids |
Forbs |
|
Carex spp. (sedge) |
Acomastylis rossii (alpine avens) |
|
Deschampsia cespitosa (tufted hairgrass) |
Artemisia scopulorum (alpine sagebrush) |
|
Elymus scribneri (Scribner wheatgrass) |
Bistorta
bistortoides (alpine bistort) |
|
Phleum alpinum (alpine timothy) |
Cerastium beeringianum ( alpine chickweed) |
|
Poa spp. (bluegrass) |
Potentilla spp. (cinquefoil) |
|
Trisetum
spicatum (spike trisetum) |
Sibbaldia
procumbens (sibbaldia) |
|
|
Silene acaulis (moss campion) |
|
|
Trifolium spp. (clover) |
II. Turf
Transplanting
Considerations
Very good vegetation cover in short time period
Very time intensive
High physical effort
Requires a lot of plant material, but should only be done when turf is available from trail construction
Does not work if done sloppily
Implementation
Remove turf from new trail construction in blocks attempting to excavate root systems as much as possible
Blocks should be a least 5 x 5 in. and as deep as possible within the trail construction guidelines
Turf blocks should be transplanted the same day or the next day to maximize success
If it is necessary to stock pile turf,
- put it in the shade if possible (at treeline)
- place block edges close together, heap dirt around outside so edges dont dry out
- sprinkle with water daily if not raining
- dont leave for more than a week or the vegetation underneath will die
Dig in blocks so that vegetation is flush with ground surface and all roots and edges are buried.
Rocks can be placed in between turf blocks to stabilize them
- Never remove rocks from the tundra near the trail!
Probably can be done at
any time in the growing season.
III. Plug
transplants
Considerations
Pretty good vegetation cover (we have no long term data for this method yet)
Time and labor intensive
We believe best in wet areas
Implementation
Remove small clumps of vegetation from surrounding area excavating as much of the root system as possible.
- Important to use plugs from the same microhabitat where they will be transplanted.
Plugs should be 3 - 5 in. in diameter and 5 in. deep cylinders, tapered as little as possible.
Remove plugs at least 3 ft. from the trail and fill in holes with soil or rocks.
Dig holes slightly larger than plugs and fill in around plugs with the excavated soil.
Place plugs 5 - 8 in. apart. Attempt to create clumps and not just a straight line of transplants.
We believe this method will be most effective in wet areas.
We initiated the first trial of this method in the Rocky Mountains during the summer of 2000 on Mount Harvard, thus no data is yet available evaluating the success.
Passive
restoration - Natural seedling
establishment
Considerations
Involves no time, physical effort, or materials
Slow to achieve vegetation cover
Will not hold soil in place
Will not work if the seed bank is badly damaged - the upper soil horizon gone - or where there is soil movement
Implementation
Most successful in mildly disturbed areas with little erosion, very low slope angle, and nearby seed sources (i.e. mature vegetation)
Mature vegetation can also act as a safe-site for developing seedlings providing protection
from environmental hazards.
This method may have beneficial use between turf blocks or single species transplants.
Seedlings will likely
naturally colonize gaps of up to 20 cm between turf blocks - which means that
turf materials can be placed farther apart so that they can cover more area.
Erosion Matting
Considerations
Increases success of single species transplants, seeding, and probably would improve natural seedling establishment as well.
Heavy and expensive
Not aesthetically pleasing to some hikers
Not always allowed in Wilderness Areas
Implementation
Recommend Curlexβ excelsior erosion matting made with aspen fibers held together with
cotton netting. There are also mats with straw, jute and other fibers that we have not tried.
Tack down with 6" staples every meter, place rocks on the edges, and dig in the ends (especially the uphill end)
Rolls are 4' x 180' and weigh approximately 80 lb.
Step 4: MAINTENANCE & Monitoring
Considerations
If implemented correctly none of these methods should require maintenance
It takes a little longer to implement revegetation in such a way that they can be monitored, however if done well it can serve as a resource to further our knowledge and understanding of revegetation methods
Monitoring and evaluating the success of past restoration/revegetation projects can ultimately lead to even more successful future projects
Implementation
Always record the method used, date, and exact location with photos if possible, drawings are also good
Record the estimated area revegetated
When seeding or transplanting plugs record the species used and the amount of plant material used
Photo-degradable erosion matting will not completely degrade above treeline and will often have to be removed after several years. It is also often necessary to return to the site after several years to remove any debris used to disguise the trail.