Potential Habitat for Sensitive Plant Species in Noxious Weed Treatment Areas, Helena National Forest

prepared for;

U.S. Forest Service Helena National Forest Award No. RFQ-Rl- 12-0 1-079

by

Whitney Weber and

Susan Crispin

Montana Natural Heritage Program P.O. Box 201800 Helena, MT 59620-1800

August, 2001

MONTANA

Natural Heritage

This document should be cited as follows:

Weber W L and S. R. Crispin. 2001. Potential habitat for sensitive plant species in noxious weed treatment areas, Helena National Forest. Report to the U.S. Forest Service. Montana Natural Heritage Program, Helena. 9 pp. and Appendix.

Introduction

This analysis was conducted to identify areas of potential habitat for Sensitive Plant Species within weed areas targeted for treatment on Helena National Forest (HNF). The results will be used to design field surveys that are as effective and efficient as possible.

At the outset of the analysis, Bonnie Heidel (former Program Botanist), Susan Crispin (Program Director and botanist), and Lois Olsen (HNF) reviewed the Region 1 Sensitive Species list, and information on Species of Concern in the Montana Natural Heritage Program (MTNHP) databases. We identified five species with a significant likelihood of occurring in or near mapped weed polygons on the Forest: Cirsium longistylum, Grindelia howellii, Phlox kelseyi var missoulensis, and Polygonum douglasii ssp austinae. Lesquerella klausii was also selected for the analysis, as it has been associated with many of the locations of Phlox kelseyi var missoulensis, and Polygonum douglasii ssp austinae and was formerly a Species of Concern. Botrychium paradoxum and Botrychium crenulatum were subsequently added to the list after they were found in appropriate habitat on the Forest just this summer (2001) by Lois Olsen. Several other species were excluded from further consideration. All species considered are summarized in Table 1 .

We then assembled data from MTNHP and HNF files documenting the distribution and habitat characteristics of known populations of these species. Occurrence records were assembled from the Montana Natural Heritage Program databases (current as of July 2001) and 30 meter Digital Elevation Models (DEMs) were used to determine the range of aspect, elevation, and slope values for locations of those species. Soil types were determined using the “Landtype” variable within the “Landwaters” GIS coverage provided by the Helena National Forest Service. Likewise, characteristic vegetation types for each species were derived using the “Best stratum” field within individual forest unit vegetation coverages.

Based on the data layers assembled, we used five variables - aspect, elevation, slope, soil type, and vegetation type - to predict potential habitat for each species within the Helena National Forest. {Botrychium crenulatum was not included in this modeling exercise, due to lack of occurrence records as a basis for determining habitat parameters.) The potential habitat was further screened to within 50 feet of the proposed weed treatment areas, provided by the USFS. This exercise was completed using ArcView 3.2, unless otherwise noted, and is described below.

TABLE 1: Selection of USES Sensitive species for Helena NF weed treatment analysis.
SPECIES i	HABITAT	KNOWN OCCURRENCE AREAS	PROBABILITY IN WEED TREATMENT AREAS
Moderate to high potential for occu Botrychium crenulatum Botrychium paradoxum \	i 1 rring in HNF weed treatment areas: wetlandsirecently reported jno occurrences in Helena NF (recently \| rom fescue grassland : reported there) j	moderate??
mesic montane meadows ;	Lincoln District i	moderate
Cirsium longistylum	montane grassland \| !	Duck Creek Pass and Avalanche Creeks are the only known occurrences in high quality natural habitat	moderate
Grindellia howellii I	along roads \|	easily surveyed by car	moderate
Phlox kelseyi var. missoulensis	exposed limestone ridges and slopes	Helena and Lincoln Districts	high, but probably not in burn areas
Polygonum douglasii ssp. austinae	shale slopes	Helena and Townsend Districts	high - potentially in burn areas
I Low potential for occurring in HNF weed treatment areas: Amerorchis rotundifolia low - wetland	Lincoln District	low
Aquilegia brevistyla	iknown from Lewis & Clark only; Little open woods, streambanks \| gelt Mountains	low
Carex livida	wetland j Lincoln District	low
Carex paupercula	wetland	no occurrences in the Helena NF	low
Cypripedium parviflorum	wetland	Lincoln District	low
Cyphpedium passerinum	moist forest	known from Lewis & Clark only; Rocky Mountain Front	low
Drosera anglica	wetland	Lincoln District	low
Drosera linearis	wetland	Lincoln District	low
Epipactis gigantea	wetlands	no occurrences in the Helena NF	low
Goodyera repens	north-facing forest slopes	no occurrences in the Helena NF	low
Juncus hallii	moist to wet meadows	Helena & Townsend Ranger Districts	low-moderate?
Oxytropis podocarpa	alpine zone	known only from the Lewis & Clark, Front Range	low
Salix wolfli var, wolfii	wetlands	not tracked by MTNHP	low
Saxifraga tempestiva	wetland, alpine	no occurrences in the Helena NF	low
Scirpus subterminalis	wetland	Lincoln District	low
Thalictrum alpinum	iwet meadows	no occurrences in the Helena NF	low
Veratrum californicum	j wetlands	no occurrences in the Helena NF	low low
Viola renifolia	swampy woods ino occurrences in the Helena Nh
Fornerly tracked species included as frequent associate and possible "indicator” of Phlox and Po 1 P’.auerella kiausii dry slopes and exposed loverlaps with Polygonum in Big Belts, STfS SanS spadas) Z.. land -h w.h Phla. ia Lincola Diatao. _	lygonum habitat: high; may indicate potential habitat for other species

2

Methods

The following outlines in greater detail the steps taken and methods used in this analysis:

a. The MTNHP database was queried for occurrences (EOPoints) of each species. Individual ArcView shapefiles (e.g., cirs_eopoints) were created containing the occurrences of each species.

b. Using the ArcView Spatial Analyst extension, the aspect and slope were calculated from the Digital Elevation Model (DEM).

c. Features of the DEM, “Landwaters” coverage and vegetation coverages, which intersected the individual shapefiles (cirs_eopoints), were selected to determine the aspect, elevation, and slope, as well as soil and vegetation types in which the species were found. Shape files were created from the selected records.

d. A map query was performed on the aspect, elevation, and slope of each species (cirs_demdata) to derive areas meeting the terrain requirements.

e. All vegetation layers were queried using the appropriate “Best_stratum” values determined in the “Select By Theme” procedure. The selected records were converted to grid files.

f. To eliminate additional steps, the individual vegetation grids were merged into a single vegetation grid (cirs_vegmerge).

g. Likewise, the “Landwaters” coverage was queried using the appropriate “landtype” values, determined in the “Select By Theme” procedure, and the selected records were converted to grid files.

h. A map query (cirs_dem&lw) was performed to determine areas that contained compatible aspect, elevation, and slope (cirs_demdata) as well as compatible soil type.

i. Another map query (cirs_compatbl) determined areas that were compatible with both the vegetation (cirs_vegmerge) and aspect, elevation, slope, and soil (cirs_dem&lw). The map query was converted to a shapefile (cirs_compatbl.shp) and the shapefile was buffered to 50 feet.

j. The weed polygon, line, and point files, provided by the USES, were clipped with the 50 foot buffer of “cirs_compatbl.shp”.

k. The area of each polygon and length of each line were calculated using the Xtools extension.

l. Centroids of the polygon and line files were created using the Xtools extension and projected to NAD 83, decimal degrees, to derive latitude and longitude.

Results

The following models were developed based on very low sample sizes. To improve the

models, any additional occurrences that are found in the course of this or future studies

could be added to the MTNHP database and incorporated into the analysis.

Botrvchium pamdoxurn

• Elevation (2083-2299 m) and slope (2.13-1 0.29°) were derived from 7 known locations of Botrychium paradoxum within the DEM range. Aspect was not considered in this analysis upon the recommendation of Lois Olsen, USFS.

• Using the Landwaters and vegetation coverages provided by the USFS, and 4 known locations of Botrychium, vegetation and soil types were derived. Botrychium was located in open parks on soil type 77 A. Upon the recommendations of Lois Olsen, USFS, soil type was eliminated from the final model.

• From the planned weed treatment areas, 9 lines of the original 1 80, 1 point of 225, and 14 polygons of 790, were found to contain potentially compatible habitat for Botrychium paradoxum. Latitude and longitude for points are given in the attached tables. Polygonal areas and line lengths are listed in the tables, as well as latitude and longitude of their respective centroids.

• The maps for Botrychium paradoxum in Appendix B display areas in which potential habitat and proposed weed treatment areas intersect. These intersects are widespread distribution within the Forest but show discemable clusters. To increase visibility of the locations, all point, line and polygon locations are displayed as red points - some larger than the actual area of potential habitat. Larger scale maps could show the exact shape and size of the small areas.

• The total acreage of potential habitat, which intersects with proposed weed treatment areas, is 29.70 acres and the total linear distance is 1.06 miles. Detailed data for Botrychium paradoxum begins on Appendix A, Page 1 .

Cirsium loneistvlum

• Aspect (42.14 - 341.57°), elevation (1423 - 2357 m), and slope (0.76-25.62°) were derived from 19 known locations of Cirsium longistylum within the DEM range.

• Using the Landwaters and vegetation coverages provided by the USFS, and 10 known locations of Cirsium, vegetation and soil types were derived. Cirsium was located m closed canopy mature timber (n = 2), open parks (n = 7), and rock (n - 1). Known locations of Cirsium were located on the following soil types: 100 (n = 1), 34- (n = 1), 360 (n = 1), 44- (n = 1), 49-(n = 1), 51- (n = 1), 54- (n = 1), 77A (n = 1), 79B (n = 1),

and87-(n=l).

4

Cirsium longistylum (continued)

• From the planned weed treatment areas, 58 lines of the original 180, 7 points of 225, and 278 polygons of 790, were found to contain potentially compatible habitat for Cirsium longistylum. Latitude and longitude for points are given in the attached tables. Polygonal areas and line lengths are listed in the tables, as well as latitude and longitude of their respective centroids.

• The maps for Cirsium longistylum in Appendix B display areas in which potential habitat and proposed weed treatment areas intersect. These intersects are widespread within the Forest but form discemable clusters. To increase visibility of plant locations, all point, line and polygon locations are displayed as red points. Larger scale maps could reveal the exact shape and size of the small areas.

• The total acreage of potential habitat, which intersects with proposed weed treatment areas, is 717.13 acres and the total linear distance is 8.81 miles. Detailed data for Cirsium longistylum begins on Appendix A, Page 2.

Grindelia howellii

• Aspect (22.38 - 326.31°), elevation (1228 - 1693 m), and slope (0.955 - 27.02°) were derived from 2 1 known locations of Grindelia howellii within the DEM range. No known locations of Grindelia howellii fell within the Landwaters and vegetation coverages provided by the USFS; therefore, we were unable to further analyze potential habitat for this species. Grindelia is known to grow along roadsides, and would most effectively be surveyed in this fashion. Alternatively, if Forest Service staff could identify the vegetation and soil types corresponding to general descriptions of known occurrences outside the forest, it may be possible to construct a model that would narrow the potential habitat areas to be surveyed.

Phlox kelseyi var. missoulensis

• Aspect (30.96 - 307.57°), elevation (1286 - 2349 m), and slope (1 .07 - 7.78°) were derived from 7 known locations of Phlox kelseyi var. missoulensis within the DEM range.

• Using the Landwaters and vegetation coverages provided by the USFS, and 3 known locations of Phlox, vegetation and soil types were derived. Phlox was located in open parks (n = 2), and rock (n = 1). Known locations of Phlox were located on the following soil types: 54- (n = 1), 11 A (n = 1), and 210 (n = 1).

• From the planned weed treatment areas, 19 lines of the original 180, 1 point of 225, and 43 polygons of 790, were found to contain potentially compatible habitat for Phlox kelseyi var. missoulensis. Latitude and longitude for points are given in the attached tables. Polygonal areas and line lengths are listed in the tables, as well as latitude and longitude of their respective centroids.

5

Phlox kelseyi var. missoulensis (continued)

• The maps for Phlox kelseyi var. missoulensis in Appendix B display areas in which potential habitat and proposed weed treatment areas intersect. These intersects show clusters of potential habitat to the east of Canyon Ferry Reservoir and to the west in the Austin — Marysville vicinity. Please note that in order to make all of the locations visible, all point, line and polygon locations are displayed as red points. Larger scale maps could reveal the exact shape and size of the small areas.

• The total acreage of potential habitat, which intersects with proposed weed treatment areas, is 1 18.27 acres and the total linear distance is 3.58 miles. The detailed data begins on Appendix A, Page 24.

Polygonum douslasii ssp. austinae

• Aspect (67.52 - 241.82°), elevation (1329- 1810 m), and slope (1 1.63 -27.90°) were derived from 5 known locations of Polygonum douglasii ssp. austinae within the DEM range.

• Using the Landwaters and vegetation coverages provided by the USFS, and 3 known locations of Polygonum, vegetation and soil types were derived. Polygonum was located in open grown mature timber (n = 1), open parks (n = 1), and unstocked timber stands (n = 1), Known locations of Polygonum were located on the following soil types: 29- (n = 1), 39-(n = 2), 390 (n = 1), and 39B (n = 1).

• From the planned weed treatment areas, 6 lines of the original 1 80, 7 points of 225, and 203 polygons of 790, were found to contain potentially compatible habitat for Polygonum douglasii ssp. austinae. Latitude and longitude for points are given in the attached tables. Polygonal areas and line lengths are listed in the tables, as well as latitude and longitude of their respective centroids.

• The maps for Polygonum douglasii ssp. austinae in Appendix B display areas in which potential habitat and proposed weed treatment areas intersect. These intersects are clustered to the east of Canyon Ferry Reservoir, including the area of the Cave Gulch Fire, to the south east of Canyon Ferry in the Deep Creek area, and are scattered throughout the continental divide area to the west. Please note that in order to make all of the locations visible, all point, line and polygon locations are displayed as red points. Larger scale maps could reveal the exact shape and size of the small areas.

• The total acreage of potential habitat, which intersects with proposed weed treatment areas, is 986.02 acres and the total linear distance is 0.52 miles. The detailed data begins on Appendix A, Page 26.

6

Lesguerella klausii

• Aspect (75.47 - 307.48°), elevation (1203-2356 m), and slope (5.876 - 35.08°) were derived from 33 known locations of Lesquerella klausii within the DEM range. Using the Landwaters and vegetation coverages provided by the USES, and 26 known locations of Lesquerella, vegetation and soil types were derived. Lesquerella was located in pole timber (n = 2), open grown mature timber (n = 8), open parks (n = 11), and rock (n = 5). Known locations of Lesquerella were located on the following soil types: 100 (n = 2), 29- (n = 2), 32A (n = 1), 32B (n = 2), 39-(n = 5), 392 (n = 1), 39A (n = 1), 39B (n = 1), 49- (n = 2), 51- (n = 1), 54 (n - 2), 91- (n = 1), 94- (n = 3), and 95- (n -!)■

• From the planned weed treatment areas, 63 lines of the original 1 80, 30 points of 225, and 448 polygons of 790, were found to contain potentially compatible habitat for Lesquerella klausii. Latitude and longitude for points are given in the attached tables. Polygonal areas and line lengths are listed in the tables, as well as latitude and longitude of their respective centroids.

• Correlating these locations with predicted habitat for Polygonum and Phlox might be used as an indicator of increased potential for those species to occur, to be tested through field surveys. However, because the potential habitat predicted is so extensive, this information may not be especially helpful in focusing surveys for those other species.

• The detailed acreage and mileage data for Lesquerella klausii begins on Appendix A, Page 1 1 .

SUMMARY AND RECOMMENDATIONS

By using data from known locations to model potential habitat for sensitive species judged likely to occur in weed treatment areas, this approach can focus survey work on a small portion of the weed treatment areas. The table below shows the areas identified for sensitive species survey as a percentage of the total mapped weed points (225 total), linear miles (198 total) and polygons (18,318 acres).

Species Percent of maoved weed:	Points	Linear Miles	Polygon Acreage
Bolrychium paradoxum	0.4%	0.6%	0.16%
Cirsium longistylum	3.1%	5.2%	3.9%
Grindelia howellii	na	na	na
Phlox kelseyi var. missouriensis	0.4%	2.1%	0.6%
Polygonum douglassii var. austinae	3.1%	0.3%	5.4%

' The mileage totals do not include linear weed features in the Belt area, as we did not receive line data from the Forest for that area. Points and polygons for the Belt area were received and included.

7

Habitat models are only as good as the data used to create them. Most of our models were based on relatively few occurrences — ranging from 19 for Cirsium longistylum to only 3 each for the Phlox and Polygonum. Models based on only three records are unlikely to represent the full range of elevation, slope, etc. over which a species occurs. The fact both the Phlox and Polygonum are inconspicuous and/or may easily be mistaken for more common species also suggests that they could easily be more widely distributed in the Forest than current records reflect. Since survey work for such small, inconspicuous species is fairly labor-intensive, it will be productive to first search areas that fit the existing - if limited - habitat model. If a number of new occurrences are found, it may then be worth expanding searches to include, e.g., a broader range of elevation or slope. However, if few or no new populations are found in the modeled habitats, then expanding the parameters of the search is less likely to be productive.

For Cirsium and Polygonum, our model identified many areas of potential habitat in the Divide and Lincoln Districts, where no populations are currently known to exist. We chose to apply the model to the entire Forest, rather than restricting it to areas of known locations. That said, however, we would expect the likelihood of occurrence to be much greater in the eastern units where the species have been documented. The lack of known locations in the western units may indicate habitat unsuitability due to parameters not captured by our measures (especially for Cirsium longistylum which is large and easily recognized). Often, plants, by their distribution, are “telling us something” about habitat requirements that we may not be able to discern, much less quantify. Given this, we would suggest a sampling approach to surveying for these species in districts where they have not been documented to date. For greater efficiency, this sampling could focus on weed treatment areas where our models show predicted habitat for more than one sensitive species. If any new populations are found in those areas, the searches could be expanded to address all identified intersects of weed treatment areas with potential habitat in that unit. If the sampling results were negative, a complete survey of those predicted habitat areas may not be necessary or very productive.

We would also suggest that where surveys identify new populations of sensitive species, the search be extended beyond the mapped weed area to determine the extent of the population. This will help determine the extent to which the entire population may be affected by current or future weed treatments, and will generate valuable information on the species’ abundance and habitat. In some areas, it may even be worthwhile for botanists, at their discretion, to survey high quality potential habitat in the vicinity of mapped weed treatment areas where sensitive plants are not found.

Finally, the GIS layers assembled and created can be reproduced in various combinations, scales and formats to help botanists conduct survey work more easily and efficiently. For example, maps could be generated that show the full extent of identified potential habitat (beyond simply the intersects with mapped weed areas) to assist in conducting more extensive opportunistic searches.

8

DATA SOURCES & ANALYSIS TOOLS

Montana Natural Heritage Program, Biological and Conservation Database, July 2001 U.S. Geological Survey, 7 'A’ Digital Elevation Model data

U.S. Forest Service, Helena National Forest, Weed Treatment Areas (points, lines & polygons) for Clancy, Belts, Blackfoot, Divide, Elkhom, Magpie (point and polygon only)

U.S. Forest Service, Helena National Forest, “Landwaters” database

ESRFs ArcView 3.2a with Spatial Analyst extension, version 1.0a

X-Tools ArcView extension, version 6-2001

9

APPENDIX A.

Detailed data on Intersections of Potential Habitat for Sensitive Species and Mapped Weed Areas

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cq	CO	cq	cq	cq	CO	CO	cq	CO	cq
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0.01 -111.2211 46.2401

986.02 Total Acres

APPENDIX B.

Maps of

Potential Habitat for Sensitive Species in Mapped Weed Areas