muledeerregions

wafwalogo

Home

WAFWA Mule Deer Working Group

What's in a Name?

Of Shipwrecks and Captives

The West that Was . . . No Longer Is

Losing Ground

The Mounting Pressure of Development

A Place for Predators

Precipitation - A Driving Force

Wilderness Breakup

Elk and Mule Deer Interactions

Mule Deer Regions - No Two are Alike

Plant Communities in Trouble . .

Mule Deer Diseases

Supplemental Feeding - Just Say No

Learning By Doing

Managing Deer Herds with Harvest

Our Summary

WAFWA

Plant Communities in Trouble . . .

Maintaining plant communities and wildlife habitat to meet the expectations of the public and the life requirements of healthy mule deer populations requires more than individual efforts by states and provinces. Policies that cross political boundaries and address factors that contribute to mule deer habitat loss and degradation, and greater emphasis on working with landowners to enhance habitat on private land may be critical to the future of many mule deer herds. The following are a few plant communities in trouble, and one plant community that is thriving to the detriment of healthy mule deer habitats.

Shrub-Steppe

Of all the habitats in the West, the shrub-steppe community has probably fared the worst. Shrubsteppe is the largest natural grassland in North America. It once covered more than 200,000 square miles, and extends from southeastern Washington and eastern Oregon, through Idaho, Nevada, and Utah, and into western Wyoming and Colorado. Shrub refers to the most common type of plant that grows in this habitat, while "steppe" is a Russian word that means a vast treeless plain. Grasses such as wheatgrass and bluegrass, and shrubs such as sagebrush, bitterbrush, rabbitbrush and greasewood are common types of plants found in shrubsteppe communities.

Removal of juniper and reestablishment of sage-steppe habitat on slope in southern Oregon. By George Buckner.The shrub-steppe region is home to more than 200 kinds of birds, and 30 mammal species, including the mule deer. Mule deer eat sagebrush, particularly during the winter months.

The greatest threats to sagebrush communities are conversion of habitat for agricultural purposes, development, grazing by livestock and fire suppression.

Biologists recommend sagebrush habitats be disturbed using fire or mechanical methods to provide a mosaic of habitats, managing livestock grazing to help vegetation recover, and managing elk and mule deer populations based on the ability of the habitat to support a certain number of ungulates.

And they encourage creativity when reclaiming sites by planting native species that benefit mule deer.

Forests

Forests offer three benefits to mule deer - places to hide, places to lessen the effects of severe weather and places to eat. Quantity, quality and diversity of plants limit the number of mule deer that can exist in a forest.

Forests naturally go through six stages before they become old growth - grass-forb, shrub, shrubsapling, open sapling-pole, closed sapling-pole-sawtimber, large sawtimber and old growth. Mule deer respond favorably to forests in the first four stages because of the quantity, quality and diversity of plants present soon after logging. The amount of time today's commercial forests offer habitat quality to mule deer is far shorter than in historical times because of how quickly foresters are able to regenerate a forest using herbicides, site preparation and seedling plantings.

The following are some recommendations to improve habitat for mule deer in forests:

- Maintain portions of forests in early successional stages.

- Create markets for pulpwood timber to improve mule deer habitat in forests by thinning pole timber.

- Promote the use of fires and reseed with native plants mule deer prefer.

- Limit the negative effects of roads. Reseeding roads no longer in use, limiting traffic on roads, closing roads during high stress periods, and estimating the impacts of new roads over a landscape can help mule deer.

- Protect hardwood species such as oak to provide mast and cover for mule deer, and protect riparian areas from overuse by deer and other ungulates.

- Responsible timber harvest based on adaptive management practices can greatly enhance mule deer populations that use forests.

Aspen

Aspen is a component of many forest types and covers up to 6.9 million acres in the western United States. It is considered the most widely distributed native tree in North Aspen stand with healthy regeneration and understory vegetation in western Wyoming. By Dan Stroud.America. Mule deer rely on aspen communities for food, cover, hiding, fawning, fawn rearing, and protection from severe weather, making it a popular habitat type for them three seasons of the year.

Aspen are short-lived, and rarely survive more than 100 years. Fire is important to set back succession in aspen stands to retain grass and forb communities, to set back conifers that outcompete aspen and to create forest openings for aspen. Many aspen stands have not been subjected to fire in over 50 years, creating older aspen stands with few grasses and forbs. A sAspen stand in very poor condition due to overgrazing. Note: no young or suckering aspen trees and no understory vegetation. This stand will eventually become too old to replace itself. By Dan Stroud.tudy done in 1981 confirmed the average age of aspen stands in Colorado is 80 years old, and stands younger than 50 years of age were difficult to find.

The distribution of aspen is similar to its historical distribution, but the stands areolder, fewer and mixed with conifers.

Biologists recommend stimulating the growth of younger stands of aspen using fire, harvest, mechanical treatments and proper livestock grazing to provide several age classes of aspen stands throughout a muledeer population's range. Fire will also help control coniferous invasion of aspen stands.

and One Troubling Plant Community . . .

Pinyon-juniper

Pinyon-juniper plant communities have expanded to over 74 million acres of the Intermountain West. Pinyon-juniper plant communities began expanding when livestock were introduced in the late 1800s, fire was reduced across the landscape and climatic changes occurred.

Juniper invasion into mule deer habitat. Note background with large junipers and understory devoid of shrubs important for mule deer forage. Note sagebrush with shrubs in foreground. By George Buckner.

When pinyon-juniper initially encroaches into shrub steppe communities, habitat for mule deer improves with additional diversity of plants and cover. The improvement is short-lived. Because it is drought tolerant, pinyon-juniper woodlands eventually outcompete forbs, grasses and shrubs, especially in places where woodlands are adjacent to grasslands. Biologists have documented a loss of 80 percent of mountain big sagebrush when juniper covers 50 percent of the canopy of an area. Other plants and plant communities such as antelope bitterbrush, mountain mahogany and aspen are also lost when pinyon-juniper invades an area.

To manage pinyon-juniper woodlands for mule deer habitat, biologists recommend harvesting fuel wood and using fire in grasslands next to pinyon-juniper woodlands to reduce further encroachment and improve quantity and diversity of grasses, forbs and shrubs.


Mule Deer, Changing Landscapes, Changing Perspectives, is a series of non-technical articles based on technical papers from the book, “Mule Deer Conservation: Issues and Management Strategies” Published by The Berryman Institute, Utah State University.

The contents of this web page may be photocopied or reprinted for noncommercial purposes using the citation listed below:

Mule Deer Working Group. 2003. Mule Deer: Changing landscapes, changing perspectives. Mule Deer Working Group, Western Association of Fish and Wildlife Agencies.