U.S. Forest Service, Manti-La Sal National Forest, Ferron-Price Ranger District. 1996 Continuing Education in Ecosystem Management Team (for the Manti-La Sal National Forest). Huntington Analysis Area Landscape Assessment. June.

RELEVANT TO:

GRASSLANDS/SHRUBLANDS

AQUATIC/RIPARIAN

FOREST

LIVESTOCK GRAZING

RECREATION

MONITORING

DESCRIPTION

This analysis of ecological conditions in the 166,823 acre Huntington Watershed of the Ferron/Price Ranger District (Manti-La Sal NF) was prepared by a group of professionals from various agencies and disciplines following a six-week intensive training in ecosystem management. The team gathered information from agency personnel, local residents, scientific literature, museums and other sources to estimate reference conditions as well as current conditions; identified key resources at risk and their ecology; and identified management options that "may be available to influence the processes" (p. 1-3).

Many of the ecological conditions and information gaps noted in this analysis of Huntington Watershed raise questions for management and monitoring throughout the Dixie, Fishlake, and Manti-La Sal National Forests, given similar human activities, ecological conditions, and/or monitoring status.

MAJOR FINDINGS AND QUESTIONS RAISED FOR THE THREE FORESTS

[Note: Questions raised for the three Forests are noted in italics)

Has this lack of information been rectified in the 8 years since this report?

Do sufficiently large reference areas of wet meadows and poorly-drained soils exist on the Forest to compare with similar areas used for motorized recreation and livestock grazing?

This requires cumulative impact analysis, as riparian areas are critical for wildlife and biodiversity on the Forest.

Five stations out of how many stations? What has been done since 1996 to address fecal coliform exceedances?

What is the time frame for these losses?

Why is only "past grazing" implicated?

Is livestock grazing allowed in the North Horn formation?

On what basis are the primary causes being attributed? Is cattle grazing still being allowed in these erosive lower canyons?

Are ORVs and other recreational roads being allowed in the North Horn formation?

This requires cumulative impact analysis with Forest activities.

Why is livestock removal of herbaceous competition to tree seedling establishment not mentioned?

What monitoring does the Forest use to determine the relative contribution of suppression of suckering versus livestock/elk browsing to lack of aspen regeneration?

Such activities would cumulatively be continuing in the riparian areas.

Have quantitative vegetation data been gathered for the main stem of Huntington Creek in the 8 years since this report?

This shows the importance of establishing reference riparian areas to make possible sustainable ecosystem management.

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Are there plans for restoration of narrow leaf cottonwood here?

What has been the nature of these plans, and the impact of their implementation?

What management actions and effects have taken place since 1996 to address this unsustainability?

This is a list of unsustainable impacts to riparian areas, which are perhaps the most critical ecosystem in the Forest.Moreover the report notes that "At present, the largest significant contiguous reverie corridor which remains intact is the Upper Scad/Staker Creek/Left Fork/Huntington habitat."(3-36). Also, there is "one small population of Bonneville cutthroat" in Spring Creek (3-36); Spring Creek is listed above as having "moderate to heavy impacts" due to sheep.

What has been changed since this 1996 report to improve conditions in this significant riparian region?

What has been changed since this 1996 report?

Moose?

Is the Forest insuring that Booths willow and beaked sedge are reproducing well? Are other native willows absent that should be here?

The reference for improvement is "personal communication." Does the Forest have quantitative or systematic data on this?

What is the cover, abundance, and distribution?

Are these native perennial grasses and forbs, or exotic species?

What management is proposed to allow actual recovery of native vegetation, wildlife, and ecosystem health?

Is reintroduction of bighorn sheep, as in Hells Canyon National Recreation Area of Oregon and Idaho a possibility?

What options exist for increased presence of beaver and reduction of dam removal?

What evidence exists that elk do not displace deer on winter range other than "personal communication" as referenced in this report?

Why is livestock removal of herbaceous cover not mentioned as a factor in the replacement of juniper by pinyon?

Has the Forest been tracking the condition and/or loss of sage communities?

Does the Forest have reference sage communities by which to judge the impact of livestock-grazed sage communities?

Are reintroductions of Colorado River cutthroat possible if habitat conditions were to improve?

How is the Forest dealing with this gap between theory and reality regarding cattle grazing?

What cumulative impacts analysis is available regarding the impacts on the vegetation, water-holding capacity, riparian areas, wildlife in Miller Flat?

What has the Forest done to address this problem since 1996?

RELEVANCE TO FOREST MANAGEMENT