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Vanderhors tt James 581.529 P

Nllreas Rapid ecological 1993 assessraent of

selected state

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RAPID ECOLOGICAL ASSESSMENT wr

SELECTED STATE LANDS IN SOUTHCENTRAL MONTANA

FOR PLANT SPECIES OF SPECL\L CONCERN

ST4TF DOCUMENTS COLLECTION

JUN 22 1994

MONTANA STATE LIBRARY

1515 E. 6th AVE- HELENA. MONTANA 59620

Prepared by:

James P. Vanderhorst

Montana Natural Heritage Program

State Library Building

1515 East Sixth Avenue

Helena, Montana 59620

Prepared for:

Montana Department of Fish, Wildlife, and Parks Parks Division - Region Five 2300 Lake Elmo Drive Billings, Montana 59105

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RAPID ECOLOGICAL ASSESSMENT wr

SELECTED STATE LANDS IN SOUTHCENTRAL MONTANA

FOR PLANT SPECIES OF SPECIAL CONCERN

ST^TF nocumms collection JUN22|99^

MONTANA STATE^UBRA«V HELENA, MONTANA 59620

Prepared by:

James P. Vanderhorst

Montana Natural Heritage Program

State Library Building

1515 East Sixth Avenue

Helena, Montana 59 62 0

Prepared for:

Montana Department of Fish, Wildlife, and Parks Parks Division - Region Five 2300 Lake Elmo Drive Billings, Montana 59105

October 1993

I

© 1993 Montana Natural Heritage Progreun

This document should be cited as follows: Vanderhorst, J. P. 1993. Rapid ecological assessment of selected state lands in southcentral Montana for plant species of special concern. Montana Natural Heritage Progreim. Helena, MT. iii + 3 0 pp. plus slides

TABLE OF CONTENTS

page

TABLES AND FIGURES iii

INTRODUCTION 1

METHODS 2

RESULTS 4

CONCLUSION 24

LITERATURE CITED 27

APPENDIX 1. Element occurrence record for

Eupatorium maculatum 28

APPENDIX 2. Species list for Chief Plenty Coups State Park 29

APPENDIX 3. Species list for Deadman's Basin State Park . . 30

APPENDIX 4. Slides of Eupatorium maculatum attached

11

LIST OF TABLES

TABLE 1. Location of sites 3

TABLE 2 . MPSSC known from the area 5

TABLE 3. Working list of target species 6

TABLE 4. Summary of results and recommendations 2 5

LIST OF FIGURES

FIGURE 1. Map of Bluewater Springs Trout Hatchery 8

FIGURE 2. Map of Chief Plenty Coups State Park -. 13

FIGURE 3 . Map of Cooney State Park 14

Figure 4. Map of Natural Bridge State Park 20

Figure 5. Map of Water Birch Fishing Access Site 23

111

INTRODUCTION

This study was conducted by the Montana Natural Heritage Program for the Parks Division of Region Five in the Montana Department of Fish, Wildlife, and Parks. The purpose was to locate or assess the potential for occurrences of Montana Plant Species of Special Concern (MPSSC) on selected lands in Region Five. MPSSC are those plant taxa listed by the Montana Natural Heritage Program which are "rare, endemic, disjunct, threatened, or endangered throughout their range or in Montana, vulnerable to extirpation from Montana, or in need of further research" (Heidel and Poole 1993). The information yielded by this project will be used by the Department of Fish, Wildlife, and Parks to prepare a weed control management plan Environmental Impact Statement in keeping with the Montana Environmental Protection Act.

Lands administered by Region Five of Montana Fish, Wildlife and Parks Department consist of Fishing Access Sites, Fish Hatcheries, State Parks, and Wildlife Management Areas, spanning six southcentral Montana counties: Big Horn, Carbon, Stillwater, Sweetgrass, Wheatland, and Yellowstone. Most sites are located at relatively low elevations in bottomlands along the Big Horn, Boulder, Musselshell, Stillwater, and Yellowstone rivers and along Rock Creek.

The surface geology at most sites is generally of alluvial origin. Plants occupying alluvial substrates tend to be generalist, as Welsh et al. (1987) have noted for the Utah flora. Thus, the plant species of concern expected at these sites are those which are peripheral in Montana with broader ranges outside the state (e.g. Eupatorium maculatum and Viburnum lentago) . These low elevation settings are historically areas of settlement, extensive habitat conversion and heavy use. The successional nature of the habitat and historic patterns of use make these sites prone to weed invasion.

A few sites are located in foothills adjacent to the major drainages or otherwise include upland habitat. The Pryor Mountains and Big Horn Canyon areas are near some of these Region Five lands and harbor some of the highest known concentrations of endemic MPSSC in the state. Endemic species have distribution ranges restricted within state boundaries or within a small area that crosses state boundaries. Thus, endemic plant species of special concern may also be expected at some state sites that have intact upland habitat and proximity to the Big Horn / Pryor Mountain areas.

METHODS

State lands of Montana Department of Fish, Wildlife, and Parks, Region Five were assessed for the potential occurrence of MPSSC as listed by Heidel and Poole (1993) . A total of twenty-two sites were visited by Jim Vanderhorst (twenty sites) on August 30-September 3, 1993 and by Bonnie Heidel (two sites, Deadman Basin State Park and Selkirk Fishing Access Site) on September 8, 1993. They included thirteen Fishing Access Sites, two Trout Hatcheries, and seven State Parks (Table 1) . Region Five lands which were not included in this study include two Wildlife Management Areas and an additional twenty-five Fishing Access Sites.

Before fieldwork, the Montana Natural Heritage Program Biological Conservation Database (BCD) was queried for all occurrences of MPSSC in the six counties included in Region Five, producing almost two hundred element occurrence records for sixty-eight MPSSC in the six-county area (Table 2) . None of the records had been documented on Montana Fish, Wildlife, and Parks lands though some were based on collections in proximity to state lands, with vague locality information. Many of the sixty-eight MPSCC are alpine species, and the potential for them to occur at the low elevations covered by this project is remote, so the working target list excluded alpine species (Table 3) . Most project area target species are known only from Carbon and/or Big Horn Counties, a reflection of the high degree of endemism centered in the Pryor Mountains and Big Horn Canyon areas. Lesica and Shelley (1991) and other field guides were consulted to determine the ecological niches of these species to further narrow the list of targets.

Due to the late season dates and paucity of background information on the sites, only preliminary surveys could be conducted. The preliminary surveys, or "rapid ecological assessment", involved subjective classification of a site's habitat and dominant vegetation, and assessment of the its suitability for hosting MPSSC. In addition, systematic searches were conducted in appropriate habitats for those few MPSSC which could be easily identified in late summer. In the sole instance when a MPSSC was found at a site, a complete survey of that population was conducted and data were taken on population numbers and boundaries, dominant and associated species, and edaphic site attributes.

This report presents a synopsis for each of the sites visited which describes the dominant native and introduced vegetation, assesses the potential for occurrences of MPSSC, and makes recommendations of weed control strategies which minimize the impacts on the native flora. Both common and scientific plant names are used, in keeping with Dorn (1984) . Other floras and guides consulted include Dorn (1988) , Hitchcock and Cronquist (1973), Welsh et. al. (1987), and Whitson et. al. (1987).

TABLE 1. Location of Fishing Access Sites (FAS) , Trout

Hatcheries (TH) , and State Parks (SP) surveyed by this project.

Site Name

Big Horn FAS Bluewater Springs TH Boulder Forks FAS Bratten FAS Buffalo Jump FAS Buffalo Mirage FAS Captain Clark FAS Chief Plenty Coups SP Cooney SP

Deadman's Basin SP Fireman's Point FAS Grant Marsh FAS Grey Bear FAS

Greycliff Prairie Dog Town Lake Elmo State Park Manuel Lisa FAS Natural Bridge SP Pictograph Caves SP Selkirk FAS Water Birch FAS White Bird FAS Yellowstone River TH

County

Big Horn Carbon Sweet Grass Sweet Grass Stillwater Yellowstone Yellowstone Big Horn Carbon

Wheatland Stillwater Big Horn Sweet Grass SP Sweet Grass Yellowstone Yellowstone Sweet Grass Yellowstone Wheatland Carbon Stillwater Sweet Grass 3

Legal Description

T5S R32E S8,9

T6S R24E S8,9

T2S R13E S21

TIS R17E S28

T4S R16E S31

T2S R23E S36

T4N R19E S27

T5S R26E S5,6

T4S R20E S25,26,34,35,36

T7N RISE S34,35

T2S R20E S32

TIN R33E S

TIN R13E S35

TIS R16E S7

TIN R26E SIO, 15

T5N R34E S34

T3S R12E S26

TIS R27E S19

T8n R12E S9

T6S R20E S7,18

T3S R19E S14

TIN R14E S15

RESULTS

Six sites among the twenty-two sites surveyed were found to have significant floristic values or potential for such. These areas are characterized as having known or potential plant species of special concern, or intact plant communities of noteworthy condition or composition. One target species, Eupatorium maculatum, was found at Bluewater Springs Trout Hatchery, with potential habitat for other target species at the same site. Three other sites have potential habitat for target species (Chief Plenty Coups State Park, Cooney State Park, Natural Bridges State Park) that also warrant survey work earlier in the growing season. Two more sites have intact natural vegetation of potential state significance (Pictograph Caves State Park, Water Birch Fishing Access Site) though they have low probability of harboring target species. It is recommended that each of these six sites be revisited and surveyed in greater detail at appropriate dates before weed control treatments are applied in places where their vegetation is native.

The remainder of this section, beginning on the page 7, is devoted to synopses of each of the sites visited. These include descriptions of the dominant vegetation, assessment of the potential for occurrences of MPSSC, and recommendations for weed control. The most common vegetation at these sites are bottomland types, including woodlands, wetlands, and managed or weedy meadows. There are only a few MPSSC from Table 3 which occur in these habitats. The most obvious two are Eupatorium maculatum and Viburnum lentago, species which could be readily identified at a late season date. Habitats which are more likely to host MPSSC are the dryer uplands which are found at a few sites, especially those close to the Pryor Mountains (e.g. Chief Plenty Coups State Park and Bluewater Springs Trout Hatchery) . The plants in these habitats were mostly senescent at the late season date of these surveys, thus intensive searching for MPSSC was inappropriate.

Site specific results are summarized in Table 4, noting significant floristic values, also characterizing the habitats, degree of weediness, and overall recommendations.

Table 2. Montana Plant Species of Special Concern (MPSSC) known from Big Horn, Carbon, Stillwater, Sweet Grass, Yellowstone, and Wheatland Counties and the habitats where they are found.

Adoxa moschalellina Agoseris lackschewUzii AquUegia brevistyla Astragalus aretoides Astragalus barrii Astragalus chameleuce Astragalus geyeri Astragalus gray! Astragalus oreganus Bulbostylis capiUaris Camissonia andina Carex gravida Carex valUcola Castilleja longispica Claytonia lanceolata jlava Cleome lutea Conioselinum scopulorum Cryptanxha Jlavoculaia Cryptanlha scoparia Cypripedium calceolus Delphinium andersonii Delphinium geyeri Draba Jladnizensis Draba porsildii Epipaclus gigantea Erigeron allocalus Erigeron eaionii Erigeron Jlabellifolius Erigeron formosissimus Eriogonum lagopus Eriogonum saluginosum Eriophorum caUitrix EupaXorium maculatum Gentiana prostrata Gentianella lenella CeiUianopsis simplex Crayia spinosa Hemicarpha drummondii Juncus covillei Juncus triglumis Kobresia macrocarpa Koenigia islandica Leptodactylon caespilosum Lesquerella sp. novum Malacothrix torreyi Mentzelia pumila Mimutus suksdorfii Noma densum Papaver kluanensis Penstemon caryi Phippsia algida Poteniilla plaitensis Ranunculus cardiophyllus Ranunculus gelidus Sagina nivalis Salix barrattiana

Stillwater

Sweet Grass

Sweet Grass

Big Horn

Big Horn

Carbon

Carbon

Big Horn, Carbon

Carbon

Carbon

Carbon

Big Horn

Carbon

Carbon

Sweet Grass

Big Horn, Carbon

Big Horn, Carbon

Carbon

Carbon

Stillwater

Carbon

Carbon

Carbon

Carbon

Carbon

Big Horn, Carbon

Sweet Grass

Carbon

Carbon

Carbon

Carbon

Carbon

Big Horn, Carbon

Stillwater

Carbon, Stillwater

Carbon

Big horn, Carbon

Carbon

Sweet Grass

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon

Carbon, Stillwater

Big Horn, Carbon

Sweet Grass

Stillwater

Stillwater

Carbon

moist woods and rocks, 4,400-5,400'

subalpine wet meadows, 8,500-9,500'

open woods, streambanks, 5,000-6,000'

barrens and guUics, 6,700-7,800'

barrens and gullies, 3,100-3,800'

sandy desert shrublands, 4,400'

sandy hills and plains, 2,000'?

sagebrush grasslands, 3,700-4,200'

desert shrub and sagebrush, 5,000'

sandy benches, adventive ?

grasslands, sagebrush, 3,100-5,400"

swales and shores, 3,900-4,000'

moist-mcsic slopes, 5,760-7,080'

sagebrush, meadows, 4,000-8,000'

meadows

sandy, disturbed valleys, 4,000'

moist woods and meadows, 3,600'

dry, gravelly slopes, 4,400-5,400'

desert hills

wet areas, moist woods, 3,000-6,200'

sagebrush grasslands, limestone

open slopes, 4,500-6,500'

alpine, 11,000'

alpine, 9,000-11,800'

wet area, esp. thermal, 2,900-5,750'

stony, limey soil, 4,400-5,600'

open places, 8,825'

alpine talus, 9,200-11,000'

meadows in mountains, 4,760-8,200'

sagebrush grasslands, 4,000-4,400'

bcntonitc soil, 4,700'

alpine

wet areas, 3,700^,000"

alpine

alpine, 9,500-10,000"

wet areas in mountains, 4,400-8,400"

alkaline basins, 4,500-5,000'

wet, sandy areas

moist areas

alpine, 9,800-10,500'

alpine, 9,800"

alpine, 9,800-10,800'

dry. barren hills, 4,800"

limestone, 6,800"

dry plains and hilb, 5,140"

desert shrub and woods, 4,300-5,000'

rocky slopes, 4,800-7,100'

sandy desert

alpine, 10,800-11,600"

grasslands in mountains, 5,900-8,080'

alpine, 9,800-11,500"

grasslands, 6,000-8,000"

moist meadows, 5,000-5,900'

alpine, 7,200-11,800'

alpine

alpine, 6,800-10,500"

Table 2. (com.)

Salix cascadcnsis Saxifraga apetala Senecio amplectens Shoshonea pulvinata Solidago sparsijlora Sphaeromeria capitala Stellaria crassifotia Stipa lettermanii Sullivantia hapemanii Thlaspi parvijlorwn Townsendia spalhulata Viburnum lentago

Swectgrass

Carbon

Carbon

Carbon

Stillwater

Carbon

Carbon

Big Horn

Big Horn, Carbon

Carbon

Carbon

Big Horn

alpine, 9,000-10,000'

subalpinc and alpine, 6,000-10,100'

alpine talus, 10,000'

limestone outcrops, 6,800-7,800'

rocky or sandy hills and canyons

limestone outcrops, 4,500-5,700'

meadows, 6,600-10,000'

open slopes and woods

wet, calcareous cliffs, 3,700-4,500'

meadows, 7,500-10,000'

limestone, 4,500-6,500'

riparian forest openings

Table 3. Working list of target species for this project (Table 2 with alpine taxa removed)

Adoxa moschateUina Aquilegia brevistyta Astragalus aretoides Astragalus barrii Astragalus chameleuce Astragalus geyeri Astragalus grayi Astragalus oreganus Bulbostylis capillaris Cainissonia andina Carex gravida Carex vaUicola Castilleja longispica Claytonia lanceolata Jlava Cleome lute a Conioselinum scopulorum Cryptantha Jla voculata Cryptantha scoparia Cypripedium calceolus Delphinium andersonii Delphinium geyeri Epipaclus gigantea Erigeron allocatus Erigeron eatonii Erigeron formosissimus Eriogonum lagopus Eupatorium maculatum Centianopsis simplex Crayia spinosa Hemicarpha drummondii J uncus covillei Leptodacrylon caespilosum Malacothrix lorreyi Mentzelia pumila Mimulus suksdorfii Nama densum Penstemon caryi Polenlilla plaltensis Ranunculus cardiophyllus Shoshonea pulvinata Solidago sparsijlora Sphaeromeria capitata Stellaria crassifolia Slipa lettermanii Sullivantia hapemanii Vilaspi parvijlorum Townsendia spathulala Viburnum lentago

Stillwater

Sweet Grass

Big Horn

Big Horn

Carbon

Carbon

Big Horn, Carbon

Carbon

Carbon

Carbon

Big Horn

Carbon

Carbon

Sweet Grass

Big Horn, Carbon

Big Horn, Carbon

Carbon

Carbon

Stillwater

Carbon

Carbon

Carbon

Big Horn, Carbon

Sweet Grass

Carbon

Carbon

Big Horn, Carbon

Carbon

Big horn. Carbon

Carbon

Sweet Grass

Carbon

Carbon

Carbon

Carbon

Caibon

Carbon

Big Horn, Carbon

Sweet Grass

Carbon

Stillwater

Carbon

Carbon

Big Horn

Big Horn, Carbon

Carbon

Carbon

Big Horn

moist woods and rocks, 4,400-5,400'

open woods, streambanks, 5,000-6,000'

barrens and gullies, 6,700-7,800'

barrens and gullies, 3,100-3,800'

sandy desert shrublands, 4,400'

sandy hills and plains, 2,000'?

sagebrush grasslands, 3,700-4,200"

desert shrub and sagebrush, 5,000'

sandy benches, adventivc ?

grasslands, sagebrush, 3,100-5,400'

swales and shores, 3,900-4,000'

moist-mesic slopes, 5,760-7,080'

sagebrush, meadows, 4,000-8,000'

meadows

sandy, disturbed valleys, 4,000'

moist woods and meadows, 3,600'

dry, gravelly slopes, 4,400-5,400'

desert hills

wet areas, moist woods, 3,000-6,200'

sagebrush grasslands, limestone

open slopes, thickets, 4,500-6,500'

wet areas, esp. thermal, 2,900-5,750'

stony, limey soil, 4,400-5,600'

open places, 8,825'

meadows in mountains, 4,760-8,200'

sagebrush grasslands, 4,000-4,400'

wet areas, 3,700-4,000'

wet areas in mountains, 4,400-8,400'

alkaline basins, 4,500-5,000'

wet, sandy areas

moist areas

dry, barren hills, 4,800"

dry plains and hills, 5,140"

desert shrub, woodlands, 4,300-5,000'

rocky slopes, 4,800-7,100'

sandy desert

grasslands in mountains, 5,900-8,080'

grasslands, 6,000-8,000'

moist meadows, 5,000-5,900'

limestone outcrops, 6,800-7,800"

rocky or sandy hills and canyons

limestone outcrops, 4,500-5,700'

meadows, 6.600-10,000"

open slopes and woods

wet, calcareous cliffs, 3,700^,500'

meadows. 7,500-10,000"

limestone, 4,500-6,500"

riparian forest openings

Big Horn Fishing Access Site

This site occupies bottomlands along the Big Horn River. Although it is in the vicinity of Big Horn Canyon and the Pryor Mountains, areas known for their many endemic and other rare plant species, the site has low potential for hosting MPSSC. The native vegetation, most notably sagebrush grasslands {Artemesia cana/Bouteloua gracilis ?) , has been mostly replaced by weedy hayfields. Cultivated species in these fields include Agropyron cristatum (crested wheat) , Bromus inermis (smooth brome) , Medicago sativa (alfalfa) , and Melilotus officinale (sweet clover) . Weedy adventive taxa include Cirsium arvense (Canada thistle) , Bromus tectorum (downy brome) , Lactuca serriola (prickly lettuce) , and Sisymbrium altissimum (tumble mustard) . The understories of the floodplain woodlands are either mowed or weedy. Floodplain thickets along the river are dominated by a mixture of woody natives (Salix spp. , Eleagnus commutatus and Rhus trilobata) and exotics (Eleagnus angustifolia and Tamarisk chinensis) . A small swampy area is dominated by Typha latifolia (cattails) . It was thought that this wetland might be potential habitat for Eupatorium maculatum or other sensitive species, but none were found.

As with many of the lowland fishing access sites, native plant taxa, especially in the open and understory habitats, have been almost entirely replaced by adventives. Precluding expensive and perhaps impossible efforts to reestablish the native communities, the best alternative at many of these sites may be to manage the open areas as mowed turf or hayfields. Weed control at these sites, provided it is aimed at introduced weedy taxa, is not likely to have adverse impact on MPSSC or the native flora in general.

Bluewater Springs Trout Hatchery

Located along Bluewater Creek in the foothills of the Pryor Mountains, this site hosts several native plant communities, along with aggressive weeds and at least one MPSSC, Eupatorium maculatum. For this reason it is strongly recommended that further sensitive plant surveys be conducted before weed control measures are taken and that weed management plans be designed which minimize impacts on species of concern and native communities.

The species of concern, commonly called Joe Pye Weed, is found in the wetland thickets around Big Bluewater Spring and along the creek (Figure 1) . Woody dominants in these thickets include Betula occidentalis (water birch) , Salix drummondiana and other Salix spp. (willows) , Ribes spp. (currants) , Cornus stolonifera (dogwood) , Eleagnus angustifolia (Russian olive) , and Tamarisk chinensis (salt cedar) . Herbaceous associates include Solidago canadensis , Scirpus acutus , and Thalictrum dasycarpum. Introduced weeds directly associated with the species of concern are Cirsium arvense (Canada thistle) ,

Figure 1. Portion of the USGS Bluewater Quadrangle (7.5 minute series) showing Bluewater Springs Trout Hatchery. The diagonal hatches indicate the location of a population of Eupatorium maculatum.

Euphorbia esula (leafy spurge) , and Conium maculatum (poison hemlock) . An Element Occurrence Record which includes additional data for this population is included as Appendix 1 of this report. In addition, slides of the plants and habitat are attached as Appendix 4. Another MPSSC previously known nearby from wetlands along the North Fork of Bluewater Creek, Epipactus gigantea (giant helleborine) , should be searched for at this site.

In addition to these wetlands, other native plant communities are found within the boundaries of the hatchery. Dryer thickets and woodlands are dominated by Populus sp.

(cottonwoods) , Prunus virginiana (chokecherry) and Juniperus scopulorum (Rocky Mountain Juniper) . Sagebrush grasslands with Artemesia tridentata and Elymus spicatus as codominants, alkaline gullies and barrens, and rock outcrops are habitats here which may potentially host other MPSSC, especially considering the proximity of the Pryor Mountains.

Other weedy species found at the hatchery include Kochia scoparia, Cyanoglossum officinale (houndstongue) , Lactuca serriola (prickly lettuce) , and Glycyrrhiza lepidota

(licorice). This last species was reported by hatchery personnel to be increasing at the site in recent years.

Boulder Forks Fishing Access Site

Habitat types at this site along the Boulder River consist of floodplain woodlands, thickets, mudflats and gravel bars, and hay meadows. The woodlands are dominated by Populus balsamifera (Balsam Poplar) with an understory of Crateagus sp. (hawthorn) and Alnus incana (alder) and many native herbaceous elements. The thickets are dominated by Salix lutea and Salix exigua (willows) , and the mudflats by Phalaris arundinacea (canary reedgrass) . Weeds in these habitats are not a great problem, however, Arctium minus (burdock) and Cirsium vulgare (bull thistle) were observed. Most of the open ground at this site was historically managed for hay. Cultivated species found in these meadows include Bromus inerwis (smooth brome) , Dactylis glomerata (orchardgrass) , Phleum pratense (timothy) , and Trifolium pratense (red clover) . Weedy species include Bromus tectorum (downy brome) , Cirsium arvense (Canada thistle) , Cyanoglossum officinale (houndstongue) , Lychnis alba (white campion) , and Tragopogon dubius (salsify) . The weed problem at this site is not great at this time; leasing the open areas for hay seems an appropriate means of retaining this status and is compatible with recreation. If weed control measures are taken in the woody habitats (although this is not recommended) care should be taken not to disturb the diverse native flora. The potential for MPSSC in these habitats is low.

Bratten Fishing Access Site

This area occupies bottomlands along the Yellowstone River. The presence of an old homestead is evidenced by

several introduced tree species including Populus alba (white poplar) and species of Ulmus (elm) and Salix (willow) which accompany the native cottonwoods (Populus deltoides and P. angustifolia) . The open areas beneath and surrounding the trees have been mowed or leased for hay. Introduced cultivated species which dominate these meadows include Bromus inermis (smooth brome) , Elymus repens (quackgrass) , Phleum pratense (timothy) , Medicago sativa (alfalfa) , Melilotus officinale (sweetclover) , and Trifolium pratense (red clover) . Weedy species in the meadows include Arctium minus (burdock) , Bromus tectorum (downy brome) Capsella bursa-pastoris (shepherd's purse), Cirsium arvense (Canada thistle), Euphorbia esula (leafy spurge), and Lychnis alba (white campion) . Native vegetation at this site is limited to the riverside bars which are dominated by Salix exigua , Equisetum laevigatum, and Phalaris arundinacea. No MFSSC are likely to be found at this site.

Buffalo Jxunp Fishing Access Site

Vegetation at this site along the Stillwater River consists of a small floodplain woodland, riverside reeds, and meadows which are mostly mowed and maintained as picnic and camp areas. The woods are dominated by Populus balsamifera (balsam poplar) , with an understory dominated by Prunus virginiana (chokecherry) , Rosa woodsii (rose) , and Clematis ligusticifolia (virgin's bower). Phalaris arundinacea (canary reedgrass) occupies moist ground adjacent to the river. Cultivated species in the meadow include Medicago sativa (alfalfa) , Melilotus officinale (sweetclover) , Phleum pratense (timothy) , and Trifolium pratense (red clover) . A diversity of weeds are found in the woods and mowed area including Arctium minus (burdock), Capsella bursa-pastoris (shepherd's purse) , Cirsium arvense (Canada thistle) , Cyanoglossum officinale ( hounds tongue ) , Glycyrrhiza lepidota (licorice), Lepidium virginicum (peppergrass) , Matricaria matricarioides (pineapple weed) , and Plantago major (plantain) . Surrounding the mowed area is a narrow (and weedy) vestige of the native plant community which presumably once occupied the site. On the flat this is represented by Elymus cinereus (wild rye) dominated grassland (rarely seen during this project) , and above by dry slopes with Artemesia campestris (common sagewort) , A. frigida (fringed sage) , Opuntia polycantha (prickly pear) and Rhus trilobata (skunkbrush) . It is unlikely that any MPSSC occur in these habitats.

Buffalo Mirage Fishing Access Site

This area along the Yellowstone River is occupied by floodplain woodlands, mudflats, and gravel bars and weedy roadsides. The woods are dominated by Populus deltoides and P. angustifolia (cottonwoods) with a unique (for this project at least) understory dominant shrub, Rhus trilobata (skunkbrush) . Eleagnus angustifolia (Russian olive) , E.

10

commutatus (silverberry) , and Rosa woodsii (rose) are additional understory shrubs. Also alarmingly dominant in the understory is Euphorbia esula (leafy spurge) , a bad, difficult to control weed; special care should be taken so that control measures do not harm the native woody vegetation. The gravel bars and flats are dominated by Salix exigua (willow) , Phalaris arundinaceae (canary reedgrass) , Rumex crispus (curly dock) , and Polygonum amphibium (water smartweed) . The weedy roadsides are dominated by introduced grasses, including Bromus inermis (smooth brome) , B. tectorum (downy brome) , Elymus repens (quackgrass) , Poa pratensis (Kentucky bluegrass) , and Setaria viridis (foxtail) . Verbascum thapsus (mullein) and Melilotus officinale (sweetclover) are two more introduced species common along the road. The possibility of MPSSC occurring at this site is remote.

Captain Clark Fishing Access Site

This is a very weedy bottomland site along the Yellowstone River. The area is divided by fences and by a slough into three sections. The area across the slough was not accessed for this project, but from a distance seems to be mostly cottonwoods and willow thickets. The two sections on the road side of the slough are mostly meadows with some cottonwoods and thickets. One section was heavily trampled and grazed by cattle (illicitly ?) with little vegetation surviving except the dominant introduced forage Elymus hispidus (intermediate wheatgrass) , which oddly was not touched by livestock (perhaps it was over-mature for palatability) , a native species of Symphoricarpos (snowberry) , and the weeds Sisymbrium loeselii (tumble mustard) and Hordeum jubatum (foxtail barley) . The heavily impacted thickets in this grazed section are dominated by Salix exigua (willow) with a vine understory of Vitis riparia (wild grape) and introduced Solanum dulcamara (blue bindweed) . The ungrazed meadows are dominated by a rank growth of weedy natives and exotics including Cirsium arvense (Canada thistle) , Iva xanthifolia (marsh elder) , Medicago sativa (alfalfa) , Melilotus alba and M . officinale (sweetclovers) , and Verbascum thapsus (mullein) . Except for the woodlands across the slough, the native flora at this site is very limited and there is little potential for occurrences of MPSSC (none have been reported in Yellowstone county) . A weed management plan is badly needed. Grazing does not seem compatible with recreation, however, leasing the meadows for hay would be acceptable, and may help reduce the weed problem.

Chief Plenty Coups State Park

The vegetation of this park includes native habitats, hay fields, and areas managed as mowed turf. The native habitat consists of wet bottomlands and dry, rocky uplands. The bottomlands are dominated by cottonwoods {Populus deltoides and P. balsamifera) , box elder {Acer negundo) , and shrubs

11

including water birch (Betula occidentalis) , currants {Ribes spp.), dogwood (Cornus stolonifera) , and chokecherry (Prunus virginiana) . These wetlands have a diverse understory of native grasses, sedges, rushes, and forbs with scattered exotic weeds including Canada thistle (Cirsium arvense) , Poison Hemlock (Conium maculatum) , houndstongue {Cyanoglossum officinale) , licorice {Glycyrrhiza lepidota) , prickly lettuce {Lactuca serriola) and sow thistle {Sonchus uliginosus) . The dry uplands consist of shrublands dominated by sagebrush (Artemesia cana) , snakeweed {Gutierrezia sarothrae) , hawthorn {Crataegus sp.)/ wild plum {Pxrunus americana) , and skunkbrush (Rhus glabra) , grasslands dominated by blue bunchgrass {Elymus spicatus) and blue grama (Bouteloua gracilis) with Spanish bayonet (yucca glauca) and prickly pear {Opuntia polycantha) , and rock pavement with common sagewort {Artemesia campestris) , fringed sage (Artemesia frigida) , and creeping juniper {Junipejrus horizontalis) growing in the cracks. Weeds are not well established in these uplands, however, some species were observed including downy brome {Bromus tectorum) and the noxious spotted knapweed (Centaurea maculosa) .

Considering the park's diverse native flora, a high potential for occurrences of MPSSC (partly due to the proximity of the Pryor Mountains) , and the presence of a spring and gravesites which Native Americans consider spiritual sites, it is recommended that weed control be carefully implemented. The park would benefit from a complete botanical survey of its natural areas both for determining the presence or absence of MPSSC and for its interpretive value; as a beginning, a list of plant taxa identified at the park by this project is provided in Appendix 2 of this report. A few small tree and brush "islands" within the area maintained as turf have severe infestations of Canada thistle and poison hemlock; these spots should be treated. However, it is recommended that the natural and spiritual areas of the park not be treated with chemicals, at least until a more detailed botanical survey can be conducted at an earlier point in the growing season and input from the Crow people is considered. Figure 2 is a map of the park which delineates the areas of concern.

Cooney State Park

Although it is one of the largest sites visited during this project, Cooney has relatively little native habitat. This is confined to the sagebrush (Artemesia cana, A. tridentata) /grassland (Bouteloua gracilis, Elymus spicatus, Oryzopsis hymenoides, Stipa comata) slopes on the unroaded north side of the reservoir, and to the narrow corridor of willow (mostly Salix exigua) thickets surrounding the inlet on the south side (see Figure 3) . No MPSSC were located or are suspected in the willow thickets, but the sagebrush grasslands were not thoroughly searched and may have some potential for hosting species of concern; a survey at an earlier date in the

12

Figure 2. Map of Chief Plenty Coups State Park. Diagonal

hatches designate the areas of concern discussed in the text warranting survey or other consideration.

/_ Smi— i. ^—

f rr ' ^T>

.1? JX

13

Figure 3. Map of Cooney State Park. Diagonal hatches designate areas with native vegetation.

14

growing season is recommended before herbicides are applied in these natural areas. However, weed control efforts will, undoubtedly, be concentrated in the developed areas of park. The vegetation of these areas consists of shoreline dominated by cottonwoods {Populus deltoides) , willows {Salix exigua and others) , sedges (including Carex lanuginosa) , and cattails (Typha latifolia) , meadows dominated by introduced grasses (Agropyron cristatum, Bromus inermis, Elymus hispidus) and legumes {Medicago sativa, Melilotus officinale) , and mowed picnic and camp areas. Weeds in the developed areas include downy brome {Bromus tectorum) , spotted knapweed (Centaurea maculosa) , Canada thistle {Cirsium airvense) , bull thistle (Cirsium vulgaris) , licorice (Glycyrrhiza lepidota) , erect cinquefoil (Potentilla recta) , and salsify (Tragopogon dubius) .

Deadman's Basin State Park

This developed water recreation site centered around an impoundment fed by diversion is located in an open, intermontane setting. No MPSSC are known from these settings in Wheatland County, but there have been almost no botanical studies in the county except in the Little Belt Mountains to the north. Records of MPSSC known from the Little Belts and of sand loving MPSSC with highly sporadic distributions statewide were considered, but none of these species were . found and the probability of them occurring here is low to none; the site is too low and dry for the Little Belt species and has little development of a sand loving flora. Native habitat in the park in good condition includes ungrazed mixed grass prairie dominated by Carex filifolia (thread leaved sedge) and Stipa comata (needle and thread) and sparsely vegetated sandstone outcrops. In addition, the artificial wetland habitat created below the impoundment has low plant diversity but appears to benefit wildlife. Noxious weed infestations including patches of Centaurea maculosa (spotted knapweed) and Cirsium arvense (Canada thistle) are mostly limited to developed areas (picnic areas, boat launches, and roadsides) but have potential to spread over much of the park. Control efforts for knapweed need to involve local landowners because there are very severe infestations in surrounding private tracts (e.g. west of the Highway 12 exit to the park) . A list of plant species identified at the park is included as Appendix 3 to this report.

Fireman's Point Fishing Access Site

This site along the Stillwater River near its confluence with the Yellowstone contains both bottomland and upland habitats. The dominant trees in the bottoms are Populus halsamifera (cottonwood) and Acer negundo (boxelder) . The understory is dominated by shrubs including Eleagnus commutatus (silverberry) , Prunus virginiana (chokecherry) , and species of Rosa (rose) and Symphoricarpos (snowberry) . Wet

15

areas directly adjacent to the river and ditch are inhabited by Phalarls arundinacea (canary reedgrass) and Salix exigua (willow) . The uplands are steep, dry, rocky slopes with scattered Pinus ponderosa (ponderosa pine) and shrubs including Artemesia cana (silver sagebrush) , Chrysothamnus nauseosus (rabbitbrush) , Juniperus scopulorum (Rocky Mountain juniper) , and Yucca glauca (Spanish bayonet) . Although weeds are not presently a great problem at this site the following were seen (mostly around the parking lot) : Arctium minus (burdock) , Bromus inermis (smooth brome) , Centaurea maculosa (spotted knapweed) , Cirsium arvense (Canada thistle) , Cyanoglossum officinale (houndstoungue) , Euphorbia esula (leafy spurge) , Glycyrrhiza lepidota (licorice) , Melilotus alba and M. officinale (sweetclovers) , and Sonchus uliginosus (sowthistle) . At least two of these, knapweed and spurge, are extremely aggressive; steps should be taken to control them before they get out of hand. Although this site contains a large area of relatively pristine native habitat, the likelihood of finding MPSSC is low; the only ones known from Stillwater County are found in the alpine or in moist woods.

Grant Marsh Fishing Access Site

This is another very weedy site in bottomlands along the Bighorn River. The vegetation consists of floodplain woodlands, rank weedy meadows, and wetlands around sloughs. The woodlands are dominated by cottonwoods {Populus deltoides) and have a disturbed understory dominated by ragweed {Ambrosia artemesifolia) , Canada thistle (Cirsium arvense) , licorice {Glycyrrhiza lepidota) , and white sweetclover {Melilotus alba) . The meadows are dominated by exotics and weedy natives including goosefoot {Chenopodium sp.), field bindweed (Convulvus airvensis) , intermediate wheatgrass {Elymus hispidus) , foxtail barley {Uordeum jubatum) , marsh elder {Iva xanthifolia) , kochia {Kochia scoparia) , prickly lettuce {Lactuca seriola) , alfalfa {Medicago sativa) , sweetclover {Melilotus alba) , tumble mustard {Sisymbrium loeselii) , and mullein {Verbascum thapsus) . The wetlands are somewhat less weedy (although sowthistle, Sonchus uliginosus , is well established) and are dominated by Russian olive {Eleagnus angustifolia) , rushes {Juncus spp.), curley dock {Rumex crispus) , bull rushes {Scirpus spp.), goldenrod {Solidago canadensis) , salt cedar {Tamarisk chinensis) , and cattails {Typha latifolia) . It was thought that this was potential habitat for Eupatorium maculatum and sensitive Carex species but none were found. It is unlikely that these or any other MPSSC inhabit these wetlands. This site needs a comprehensive weed control strategy and reclamation to less objectionable types of vegetation, but this will not be easily achieved.

Grey Bear Fishing Access Site

Vegetation at this site along the Yellowstone River consists of woodlands with openings, small meadows and

16

extensive wetlands. The dominant tree is Populus acuminata (lance-leaved Cottonwood). The understory of the woods is either shrubby, dominated in dryer areas by Eleagnus commutatus (silverberry) , Juniperus scopulorum (Rocky Mountain juniper) , and Symphoricarpos (snowberry) , and in wetter areas by Cornus sericea (dogwood) and Salix lutea (willow) , or open, dominated by introduced grasses and legumes. Species represented in these open understories and in the small meadows include Agropyron cristatum (crested wheatgrass) , Bromus inermis (smooth brome) , Elymus hispidus (intermediate wheatgrass) , Elymus repens (quackgrass) , Medicago sativa (alfalfa) , Melilotus alba and M. officinale (sweetclovers) . Weeds in these habitats include Centaurea maculosa (spotted knapweed) , Cirsium arvense (Canada thistle) , Cyanoglossum officinale (houndstoungue) , Glycyrrhiza lepidota (licorice), Lactuca seriola (prickly lettuce) , Sisymbrium loeselii (tumble mustard) , Sonchus uliginosus (sowthistle) , Tanacetum vulgare (tansy) , Tragopogon dubius (salsify) , and Verbascum thapsus (mullein) . The low wetlands are dominated by native plants including shrubs, Cornus stolonifera (dogwood) and Salix exigua (willow) , grasses, Phalaris arundinacea (canary reedgrass) and Phragmites australis (common reed) , rushes, Juncus balticus , and cattails, Typha latifolia. Conium maculatum (poison hemlock) is the most common weed in the wetlands. Although no MPSSC are suspected at this site, the wetlands are a high quality native habitat which should not be disturbed; however, weed control is appropriate in the disturbed woods and meadow areas.

Greycliff Prairie Dog Town State Park

The habitat of this park is inherently weedy due to constant rodent disturbance. Weed control is, therefor, probably futile except for spot treatment around picnic tables and along the road and trails. The prairie dogs themselves keep the weeds down by using them as a food source. Chemicals which might be poisonous to the wildlife (at all levels of the food chain) at this site should be avoided. The dominant native plant species around the dog diggings is Artemesia frigida (fringed sage) . Weeds observed include Arctium minus (burdock) , Bromus tectorum (downy brome) , Carduus nutans (musk thistle) , Cirsium arvense (Canada thistle) , Convulvulus arvensis (field bindweed), Glycyrrhiza lepidota (licorice), Hyoscyamos niger (henbane) , Verjbena bracteata (prostrate vervain) , and VerJbascum thapsus (mullein) . On the hills to the east of the prairie dog colony is relatively undisturbed native vegetation dominated by shrubs including Artemesia tridentata (big sagebrush) , Juniperus scopulorum (Rocky Mountain juniper) , Prunus virginiana (chokecherry) , and Rhus trilobata (skunkbrush) , and bluebunch wheatgrass, Elymus spicatus. Although the potential for MPSSC in this habitat is low, there is a high diversity of native plants and relatively

17

few weeds; thus weed control should be aimed only at carefully chosen targets.

Lake Elmo State Park

The native flora at this park in the greater Billings area has been almost entirely replaced by introduced and weedy species, in fact it is difficult to determine what the original vegetation was like. Much of the area has been planted with pasture forbs and grasses including Agropyron cristatum (crested wheatgrass) , Bromus inermis (smooth brome) , Medicago satlva (alfalfa) , Melilotus alba (sweetclover) and Trifolium pratense (red clover) . Weeds in the park include Centaurea maculosa (spotted knapweed) , Centaurea repens (Russian knapweed) , Cirsium airvense (Canada thistle) , Convulvulus arvensis (field bindweed) , Glycyrrhiza lepidota (licorice) , Kochia scoparia (kochia) and Salsola kali (tumbleweed) . Native taxa are mostly isolated, not part of intact systems. Native Acer negundo (boxelder) and Populus deltoides (cottonwood) grow along the lakeshore along with exotic woody species like Eleagnus angustifolia (Russian olive) and Malus domestica (apple) . Wet alkaline flats are occupied by a mixture of native and exotic species including Aster falcatus (creeping white prairie aster) , Chenopodium spp. (goosefoots) , Hordeum jubatum (foxtail barley) , Scirpus spp. (bullrushes) , Tamarisk chinsnsis (salt cedar) , and Typha latifolia (cattails) . The predominance of members of the Chenopodiaceae (goosefoot family) and other salt tolerant plants are evidence of alkaline soils. No MPSSC are likely to inhabit the park.

Manuel Lisa Fishing Access Site

Vegetation at this small area along the Bighorn River at its confluence with the Yellowstone consists of floodplain woodlands and mudflats, and disturbed sagebrush grasslands. The woods are dominated by cottonwoods (Populus deltoides) and Russian olive (Eleagnus angustifolia) , and have an understory of weeds and disturbed sand. The mudflats are dominated by canary reedgrass (Phalaris arundinaceae) , bullrushes (Scirpus sp.), and blue vervain (Verbena hastata) . The sagebrush grassland, dominated by big sagebrush (Artemesia tridentata) and blue grama (Bouteloua gracilis) has a diversity of native herbs but is also very weedy. Exotic species at this site include smooth brome (Bromus inermis) , Russian knapweed Centaurea repens) , Canada thistle (Cirsium arvense) , foxtail barley (Hordeum jubatum) , kochia (Kochia scoparia) , alfalfa (Medicago sativa) , sweetclovers (Melilotus alba and M. officinale) , and salt cedar (Tamarisk chinensis) . There is little potential here for occurrences of MPSSC.

Natural Bridge State Park

Vegetation at this park is quite diverse, relatively pristine, and unlike that of any of the other sites visited

18

during this project. Habitats range from relatively dry montane grasslands on the flats above the canyon walls to wetter forests and shady canyon walls, and include ecotones between these extremes. The flora of the upper rock walls and canyon rim is characterized by limestone loving plants such as Chielanthes feei (lipfern) , Happlopappus acaulis (cushion goldenweed) , and Selaginella densa (selaginella) . The woodlands range from moist Pseudotsuga menziesii (Douglas fir) dominated forests with an understory of Physocarpus malvaceous (ninebark) and mosses, to dryer more open woods with a mixture of Pseudotsuga and Pinus flexilis with an understory of shrubs and grasses. These dry woods grade into pristine grasslands, (perhaps the most significant botanical feature of the park) , dominated by Elymus spicatus (bluebunch wheatgrass) , Festuca idahoensis (Idaho fescue) , Oryzopsis hymenoides (Indian ricegrass) , and Stipa comata (needle and thread) . These grasslands host a large number of native plant species. Wetter montane meadows in juxtaposition with the Pseudotsuga forests are dominated by forbs such as Campanula rotundifolia (harebell) , Geranium spp. (geraniums) , Monarda fistulosa (bee balm) , Helianthella quinquenervis (little sunflower) , and Perideridia gairdneri (yampah) . Weeds are not a big problem at the park except around the parking area, trails, and picnic tables where the following exotic species were seen (some of them undoubtedly planted) : Alyssum desertoirum (alyssum) , Bromus inermis (smooth brome) , Bromus secalinus (cheat) , Bromus tectorum (downy brome) , Dactylis glomerata (orchardgrass) , Glycyrrhiza lepidota (licorice), Lactuca seriola (prickly lettuce) , Melilotus officinale (sweetclover) , Phleum pratense (timothy) , Sisymbrium altissimum (tumble mustard) , Lychnis alba (white campion) , and Verbascum thapsus (mullein) . Although no MPSSC were located there may be some potential of the wetter forests hosting Cypripedium calceolus or Adoxa moschatellina , species found in these habitats elsewhere in Stillwater County. Due to the high quality native habitats in the park it is suggested that weed control be confined to the weedy developed areas (Figure 4) where a carefully implemented program (including seeding with native species) could help enhance the native flora. A complete floristic inventory of the park would be useful for determining the status of the above mentioned MPSSC and as a tool for public interpretation of this scenic area.

Pictograph Caves State Par)c

This is another example of a park with a significant (if not pristine) native plant community. Located along sandstone rimrock, the site has a spectrum of microhabitats ranging from shady and cool to open and hot. The cliffs host tree species including Acer negundo (boxelder) , Pinus ponderosa (ponderosa pine) , and Populus deltoides (cottonwood) with a somewhat troublesome understory of Clematis ligusticifolia (virgin's bower) , Hummulus lupulus (hops) , and Toxicodendron rydbergii

19

Figure 4. Map of Natural Bridge State Park showing developed

areas (map does not show the entire park) . Diagonal hatching indicates area with significant levels of exotic plants (weeds and seeded species) . Chemical weed control should be limited to carefully identified targets within this area.

20

(poison ivy) . The more open areas are sagebrush (Artemesia cana) grasslands (Bouteloua gracilis, Elymus cinereus, Oryzopsis hymenoides, Stipa comata) with a diversity of native herbs and shrubs. Weeds, besides the viney Clematis and Humulus , are concentrated around the parking and picnic areas and around the archeological digs and include Arctium minus (burdock) , Alyssum desertorum (alyssum) , Ambrosia artemesifolia (ragweed) , Bromus tectorum (downy brome) , Cirsium arvensis (Canada thistle) , Marrubium vulgare (horehound) , and Melilotus alba (sweetclover) . No MPSSC were found or are known from elsewhere in Yellowstone County.

Selkirk Fishing Access Site

Habitat at this unusually large fishing access site along the Musselshell River includes oxbow wetlands and adjoining uplands. Vegetation consists of three more or less natural types but none of these are pristine; these are 1) mixed grass prairie uplands dominated by Elymus smithii (western wheatgrass) and Stipa comata (needle and thread) and invaded by Poa pratensis (Kentucky bluegrass) which are idle and productive but recovering from overgrazing and depauperate in forbs, including a portion with a high component of Ceratoides lanata which may represent an uncommon plant association, 2) unstable, sparsely vegetated silt slopes with a diverse pioneer community which has, however, been disturbed by construction of an irrigation channel and invaded by Centaiirea maculosa (spotted knapweed), and 3) floodplains with oxbow wetlands choked by Typha latifolia (cattails) and open forests and thickets dominated by Populus angustuifolia (cottonwood) and Salix bebbiana (willow) respectively, with understories dominated by exotic species. In addition to knapweed two other noxious weeds seen were Cyanoglossum officinale (houndstongue) and Hyoscyamus niger (henbane) . No MPSSC are known from Wheatland County, none were found at the site, and none are suspected.

Water Birch Fishing Access Site

The floodplain woodlands which occupy most of this area along Rock Creek are among the most extensive and most pristine visited during this project. However, no MPSSC are known from this kind of habitat, at least in Carbon County. The woodlands are dominated by Populus balsamifera (cottonwood) with a few Populus tremuloides (quaking aspen) and have a brushy understory with Alnus incana (alder) , Cornus stolonifera (dogwood) , Prunus virginiana (chokecherry) , and species of Crataegus (hawthorn) , Rosa (rose) and Symphoricarpos (snowberry) . Oddly, no water birch {Betula occidentalis) was seen. A few exotic species are scattered in the woods but are nowhere aggressively weedy; these include Centaurea maculosa (spotted knapweed) , Chrysanthemum leucanthemum (ox-eye daisy) , Cirsium arvense (Canada thistle) , Dactylis glomerata (orchardgrass) , Glycyrrhiza lepidota

21

(licorice) , Melilotus spp. (sweetclovers) , Sonchus uliginosus (sowthistle) , and Trifolium pratense (red clover) . Additional floodplain habitat includes gravel bars characterized by Ranunculus gmelinii (buttercup) and the exotic Myosotis scirpoides (forget-me-not) and mudflats dominated by Carex urtriculata (sedge) and species of Juncus (rushes) and Scirpus (bullrushes) . Weeds are a problem in the open camping, picnic and parking areas adjacent to the highway and railroad tracks where heavy infestations of Berteroa incana (berteroa) , Bromus tectorum (downy brome) , and Centaurea maculosa (spotted knapweed) are found along with lesser weeds such as Lactuca serriola (prickly lettuce) , Tragopogon dubius (salsify) , and Verbascum thapsus (mullein) . It is recommended that broad treatment of weeds be confined to these developed areas (Figure 5) .

White Bird Fishing Access Site

Vegetation at this site along the Stillwater River consists of relatively pristine floodplain woodlands and wetlands and meadows in small openings managed for camping and picnicking. The woods are dominated by Acer negundo (box elder) and Populus balsamifera (cottonwood) , with an understory of shrubs including Cornus stolonifera (dogwood) , Eleagnus commutatus (silverberry) , Juniperus scopulorum (Rocky Mountain juniper) , and Symphoricarpos sp. (snowberry) , Swampy areas are dominated by Phalaris arundinacea (canary reedgrass) and Salix exigua (willow) . The meadows are dominated by introduced pasture species including Bromus inermis (smooth brome) , Dactylis glomerata (orchardgrass) , Medicago spp. (alfalfas) , Melilotus spp. (sweetclovers) , Phleum pratense (timothy) , and Trifolium pratense (red clover) . Weeds include Berteroa incana (berteroa) , Centaurea maculosa (spotted knapweed) , Cirsium arvense (Canada thistle) , Euphorbia esula (leafy spurge), Glycyrrhiza lepidota (licorice), and Verbascum thapsus (mullein) . No MPS8C were found or are expected at this site.

Yellowstone River Trout Hatchery

This site in Big Timber is almost entirely a managed landscape. Most of the area is mowed turf, however, there is a small plantation of Picea (spruce) , and a small swampy area with aquatic plants such as Epilobium ciliatum (willow-herb) , Lemna minor (duckweed) , and Typha latifolia (cattail) . Weeds at the site include Arctium minus (burdock) , Cirsium arvense (Canada thistle), Malva neglecta (mallow) and Solanum dulcamara (nightshade) . The potential for MPSSC is low. Precautions should be taken so that the wetlands are not polluted with toxic herbicides.

22

Figure 5, Map of Water Birch Fishing Access Site. Diagonal Hatching indicates area with heavy infestations of weeds. Broad weed control measures should be confined to this area.

23

CONCLUSION

Although an attempt was made by this project to assess Region Five lands for MPSSC, the results should not be considered definitive or complete. Even when intense plant searches are conducted at appropriate times of the year, some targets are probably inevitably overlooked. In this case the searches were neither intense nor, in most cases, conducted at an appropriate time. Because of this, some precautions should be taken.

Certain areas should be revisited for more intense surveys earlier in the growing season before weed control measures are taken. The areas where this has been recommended were chosen based on the presence of significant native plant communities and geographical proximity to known occurrences of MPSSC. At most sites, however, the areas with severe weed problems (where control should be focused first) are not native communities. Bluewater Springs Trout Hatchery is an exception which will require development of a special weed control strategy.

Weed control should be aimed at carefully chosen targets and based on positive weed identification. Too often weed crews have sprayed populations of sensitive species. This has not been limited to small or inconspicuous species; during the summer of 1993 populations of Penstemon lemhiensis and Veratrum calif ornicum , two large, showy, sensitive species which cannot be mistaken for any weeds, were sprayed on public lands in Montana. Besides MPSSC, the general native flora should also be spared from weed control measures; if native plants are killed openings are left for weeds. Members of weed crews need to be familiar with their targets.

Despite these potential dangers, it is acknowledged that weed infestations are generally more detrimental to native plant species and communities than appropriate weed control measures. Many, if not most, of the sites visited during this project host severe infestations of weeds which warrant immediate control actions. A summary of the results and recommendations of this report is presented in Table 4 which follows.

24

Table 4. Summary of site specific results and recommendations .

SITE

DEGREE OF WEEDINESS

NATIVE COMMUNITIES

CONFLICTS, INCLUDING MPSSC

RECOMMENDATION

S

Big Horn

high

wetlands and thickets

none, low probability for species of concern

proceed with weed control

Blucwatcr Springs

high

sagebrush grassland,

desert shrub, alkaline

barrens, rock outcrops,

and wetlands

weeds in association with

Eupalorium maculalum,

potential for other

species of concern

delay weed control until

conflicts are resolved,

return for detailed

survey

Boulder Forks

low-moderate

floodplaln woodlands

none, low probability for species of concern

continue haying, weed

control OK in developed

areas

B ratten

moderate

(loodplain woodlands, thickets and bars

none, low probability for species of concern

continue haying, weed

control OK in developed

areas

Buffalo Jump

moderate

small woodlot, remnant

grasslands and

shrublands

none, low probability for species of concern

continue mowing or

hay, weed control OK

in developed area

Buffalo Mirage

high Ocafy spurge)

floodplain woodlands, thickets, and bars

none, low probability for species of concern

develop weed control

strategy for spurge

which minimizes impact

on woody natives

Captiin Clark

high, overgrazing

by trespassing

cattle?

floodplain woodlands and bars

none, low probability for species of concern

remove cattle from site,

lease for hay, proceed

with weed control.

Chief Plenty Coups

high in spots

within developed

areas

floodplain woodlands

and thickets, sagebrush,

desert shrub, grasslands,

rock outcrop

spiritual spring and

grave sites, native plant

communities, potential

for species of concern

weed control OK in

developed area, needs

further survey work in

native areas

Cooncy

high

sagebrush grasslands,

strcamsidc willow

thickets

none in developed areas

(most of the site),

potential for species of

concern in native

sagebrush grasslands

proceed with weed

control in developed

areas, further survey

needed in native areas

Dcadman's Basin

high in developed areas

mixed grass prairie, sandstone outcrops

none, probability low for species of concern

proceed with weed

control, coordinate with

adjacent landowners

Fireman's Point

low

floodplain woodlands, Ponderosa pine slopes

none in developed area,

native communities on

slopes

weed control OK in parking area

Grant Marsh

high

floodplain woodlands, wedands

chemical effects on wetlands, f)otcntial low for species of concern

mow or lease for hay,

proceed with weed

control except in

wetlands

25

SITE

DEGREE OF WEEDINESS

NATIVE COMMUNITIES

CONFLICTS, INCLUDING MPSSC

RECOMMENDATION

S

Grey Bear

moderate

floodplain woodlands

and thickets, extensive

wetlands

chemical effects on

wetland wildlife and

flora

weed control OK in

developed areas, stay

out of wetlands

Greycliff Prairie Dog Town

high

naturally disturbed area, sagebrush grasslands

chemical effects on wildlife

weed control probably

futile except along road

and around picnic tables

due to constant rodent

activity

Lake Elmo

high

minimal, alkaline thickets and meadows

none, probability low for species of concern

proceed with weed control

Manuel Lisa

high

floodplain woodlands,

mudflats, sagebrush

grasslands

none, probability low for species of concern

proceed with weed control

Natural Bridge

low-inoderate

conifer forest,

grasslands, meadows,

limestone outcrops

pristine native plant communities, potential for species of concern

weed control OK in developed area, further survey for species of concern and of plant communities may be warranted

Pictograph Caves

moderate,

confined to

developed area

and archcological

digs

grasslands, sagebrush

grasslands, woodland,

sandstone outcrops

native plant communities

weed control OK in developed area

Selkirk

high

mixed grass prairie,

unstable slopes,

wetlands, thickets,

woodlands

none, probability low for species of concern

proceed with weed control

Water Birch

moderate

(-high in

developed area)

extensive floodplain woodlands

high quality native

vegetation but low

probability for species

of concern

proceed with weed

control in developed

area

White Bird

moderate

floodplain woodlands, wetlands

none, probability low for species of concern

proceed with weed

control in developed

area, mow?

Yellowstone River Hatchery

low

small swamp, area mostly developed

chemical effects on wetland

continue management as developed landscape

26

LITERATURE CITED

Dorn, R. D. 1984. Vascular plants of Montana. Mountain West Publishing, Cheyenne, WY. 276 pp.

. 1988. Vascular plants of Wyoming. Mountain West

Publishing, Cheyenne, WY. 340 pp.

Heidel, B. L. and J. M. Poole. 1993. Montana plant species of special concern. Unpublished list. Montana Natural Heritage Program, Helena, MT.

Hitchcock, C. L. and A. Cronquist. 1973. Flora of the Pacific Northwest. University of Washington Press, Seattle, WA. 730 pp.

Lesica, P. and J. S. Shelly. 1991. Sensitive, threatened, and endangered vascular plants of Montana. Montana Natural Heritage Program, Occasional Publication no. 1. Helena, MT. 88 pp.

Welsh, S. L. , N. D. Atwood, L. C. Higgins, and S. Goodrich.

1987. A Utah Flora. Great Basin Naturalist Memoirs no. 9. Brigham Young University, Provo, UT. 894 pp.

Whitson, T. D. , R. Reichenbach, M. A. Ferrell, S. D. Miller, S. A. Dewey, J. O. Evans, and R. J. Shaw. 1987. Weeds and poisonous plants of Wyoming and Utah. Cooperative Extension Service, College of Agriculture, University of Wyoming, Laramie, WY. 281 pp.

27

APPENDIX 1

October 20, 1993

MONTANA NATURAL HERITAGE PROGRAM Element Occurrence Record

)

Scientific Name: EUPATORIUM MACULATUM VAR BRUNERI Common Name: JOE-PYE WEED

Global rank: G5TU Forest Service status: State rank: SI Federal Status:

Element occurrence code: PDAST3P141 . 003 Element occurrence type:

Survey site name: BLUEWATER HATCHERY

EO rank: B EO rank comments: WEEDS PLENTIFUL BUT POPULATION SEEMS COMPETITIVE.

County: CARBON

USGS quadrangle: BLUEWATER

Township: Range: Section: TRS comments: 006S 024E 09 W2

Precision: S

Survey date: 1993-08-31 Elevation: 3980 - 4000

First observation: 1993-08-31 Slope/aspect: LEVEL

Last observation: 1993-08-31 Size (acres) : 10

)

Location:

FROM FROMBERG ON US HWY 310, TRAVEL 9 MILES SOUTHEAST ON COUNTY ROAD FOLLOWING SIGNS TO BLUEWATER HATCHERY AND FISHING ACESS. POPULATION IS AROUND BIG BLUEWATER SPRING AND ALONG CREEK.

Element occurrence data:

1000+ AERIAL STEMS, 100% LATE FLOWERING AND EARLY FRUIT. HIGH-DENSITY POPULATION; LARGE PLANTS.

General site description:

SATURATED BOTTOM, PARTIAL SHADE, CLAY SOILS. WETLAND THICKET, WITH BETULA OCCIDENTALIS, SALIX DRUMMONDIANA, SALIX SPP., CORNUS STOLONIFERA, SCIRPUS SP., EUPHORBIA ESULA, THALICTRUM DASYCARPUM, SOLIDAGO SP., CIRSIUM ARVENSE, CONIUM MACULATUM, TAMARISK CHINENSIS, TYPHA LATIFOLIA, ELEAGNUS ANGUSTIFOLIA.

Land owner/manager:

BLUEWATER SPRINGS TROUT HATCHERY

PRIVATELY OWNED LAND (INDIVIDUAL OR CORPORATE)

Comments :

EIS FOR WEED CONTROL ON MT DEPT. OF FISH, WILDLIFE AND PARKS LANDS IS BEING PREPARED (FALL, 1993). POPULATION SHOULD BE CONSIDERED WHEN PLANNING WEED CONTROL IN VICINITY.

^ Information source: VANDERHORST, J. 1993. [MTNHP SENSITIVE SPECIES

SURVEY OF REGION 5, CONDUCTED FOR MONTANA DEPARTMENT OF FISH, WILDLIFE AND PARKS.]

Specimens: VANDERHORST, J. (5155). 1993.

APPENDIX 2

List of vascular plant species identified at Chief Plenty Coups State Park on August 31, 1993, their common names, and habitats where thev occur.

Acer negundo Artemesia campestris Art ernes ia cana Artemesia frigida Astragalus adsurgens Astragalus drummundii Beckniannia syzigacbne Betula occidentalis Bouteloua gracilis Bromus tectorum Centaurea maculosa Cirsium arvense Corpus stolonifera Conium maculatum Cyanoglossum officinale Elymus spicatus Epilobium paniculatum Glycyrrbiza lepidota Gutierrezia sarothrae He] ianthus rigidus Juniperus horizontal is Lactuca serriola Liatris punctata Mel i lotus officinale Phleum pra tense Populus balsam if era Popu lus del toides Prunus americana Prunus virginiana Psora lea tenuiflorum Rlnis trilobata Selaginella densa Solidago nemoralis Soli da go rigida Sonchus ul iginosus Yucca glauca

hoxelder

common sagewort

siver sagebrush

fringed sage

locoweed

locoweed

sloughgrass

water birch

blue grama

downy brome

spotted knapweed

Canada thistle

dogwood

poison hemlock

houndstongue

hluebunch wheat grass

willow herb

licorice

snakeweed

sunf lov;er

creeping juniper

prickly lettuce

blazing star

sweetclover

timothy

balsam poplar

plains Cottonwood

wild plum

chokecherry

scurf-pea

skunkbrush

spike moss

goldenrod

goldenrod

sow thistle

Spanish bayonet

riparian woodlands rocks

sagebrush grasslands rocks and sagebrush sagebrush grasslands sagebrush grasslands riparian grasslands riparian thickets dry grasslands disturbed grasslands disturbed areas disturbed areas riparian thickets wet, disturbed areas disturbed areas sagebrush grasslands dry hills disturbed areas, sagebrush grassland rocks and sagebrush rocks

disturbed areas sagebrush grasslands disturbed areas hayf ields

riparian woodlands riparian woodlands dry shrublands thickets

sagebrush grasslands dry shrublands rocks and sagebrush rocks rocks

wet, disturbed areas dry grasslands

APPENDIX 3

List of vascular plant species identified at Deadnians Basin State Park on September 8, 19^1

Agropyron crista turn

Artemisia cana

Artemisia frigida

Artemis ia t ridentata

Aster er icoides

Astragalus gilvi floras

Astragalus missouriensis

Astragalus spathulatus

Bidens cernua

B ramus inermis

Bromus tec tor urn

Cares filifolia

Centaurea macula t a

Ceratoides lanata

Chaenact is douglasi i

Ch ryso tha mn us nauseas us

Cirsium arvense

Elymus hispidus (Agropyron intermedium )

Elymus sp i ca t us ( Agropyron sp i ca t um )

Gr indel ia squarrosa

Gut i erre.y ia sarothrae

He ] i an thus annua

Hymenopappus a ca ul is

Koeleria crista ta I.iatris punctata

Lygode sm i a j un caea Mel ilotus officinalis .^luhlenbergia cuspidata Oryzops i s hymena ides Pet lostemum purpureum Phlox hoodii Psoralea lanceolata S i syrh inch i um mon tan um Si tan ion hystrix Stipa coma t a Stipa viridula

30

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