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Green Mountain National Forest Dorset-Peru Integrated Resource Area Non-Native Invasive Species Inventory Prepared for the Green Mountain National Forest Service by The LAND Stewardship Program July 2009 1 Acknowledgements We would like to thank several parties for making this report possible. First, we would like to thank the Green Mountain National Forest (GMNF) for providing financial support for crew time and for allowing us to use the Mount Tabor Work House and welcoming our team to the project. Also, thank you to Melissa Reichert, Kate Walker, and Mary Beth Deller of the GMNF for their fantastic support and training. We would also like to recognize Kim Hoffman for her help. LANDS work was also supported by a TogetherGreen (an alliance of Audubon and Toyota) grant and support from the Conservation Leadership Seed Fund of the Rubenstein School of Environment and Natural Resources at the University of Vermont (UVM). The Student Conservation Association (SCA) contributed administrative and program support, oversight, time, and financial resources. Finally, thanks to the Green House Residential Learning Community staff at UVM for lending us their great facilities. About the LANDS College Conservation Corps The field of conservation is rapidly evolving to meet the growing demands of society. New ideas and strategies are changing how we conserve and steward land. The Land Stewardship Program (LANDS) is one of these new ideas. During the great depression, the conservation corps model was pioneered as a means to promote stewardship in the nation and provide jobs for the unemployed. That idea has since been reinvented 116 times by local and state corps across the United States. However, the general theme is the same -- young people learning and growing through service. LANDS is an innovative College Conservation Corps designed to train tomorrow’s conservationist practitioners and leaders, and is a pilot partnership between the UVM and the Student Conservation Association in its third year of successful programming. LANDS crew interns work on projects that are more technical than traditional crew work for a broad range of public and private non-profit organizations. They draft management plans, map areas of interest using GPS and GIS, inventory resources, calculate carbon stocks, and even find time to build trails and remove invasive species. Municipalities, land trusts, state agencies, university researchers, National Forests and Parks, and volunteer-managed conservation organizations all benefit from LANDS’s high quality, affordable products. LANDS interns are advanced undergraduates in the natural resources field from all over the world with a range of skills and interests. LANDS is a unique service-learning model that will hopefully be replicated at universities across the nation to address an ever expanding list of conservation needs while training students as future environmental leaders. http://www.uvm.edu/~conserve/lands_website/ Cover Photo: Asiatic bittersweet (Celastrus orbiculatus) climbing a trail sign on the Dorset/Peru property. 2 Table of Contents Acknowledgements................................................................................................................... 2 About the LANDS College Conservation Corps ...................................................................... 2 Table of Contents...................................................................................................................... 3 Introduction............................................................................................................................... 4 Project Description................................................................................................................ 4 Methods................................................................................................................................. 4 Green Mountain National Forest Non-Native Invasive Species List.................................... 5 Current Conditions.................................................................................................................... 6 Data Organization ................................................................................................................. 6 Dorset Peru IRA NNIS: Overview Map ........................................................................... 7 NNIS Maps & Descriptions .................................................................................................. 8 Lower FR 10: .................................................................................................................... 8 Old Job Trail Area: ......................................................................................................... 10 FR 259:............................................................................................................................ 12 Rt. 11:.............................................................................................................................. 16 Grouse Lane:................................................................................................................... 18 Kirby Hollow Road:........................................................................................................ 20 FR 221: (No Map Provided) ........................................................................................... 22 Report Summary ..................................................................................................................... 23 Appendix................................................................................................................................. 24 NNIS Form from GMNF .................................................................................................... 24 NNIS Counts....................................................................................................................... 26 Upper Row left to right: Lydia Menendez (leader), Andrea Lauritzen, Arthur Zahor, Andrea Bruno, Gavin Cotterill, James Barnes (leader & program coordinator). Lower Row: Tim Villard, Ellen Kujawa, Lisa Fredette, Charlotte Gabrielsen, Lauren Bizzari. All are holding non-native Aegopodium podagraria- “Goutweed”) 3 Introduction Project Description The 2009 Land Stewardship (LANDS) crew prepared this report in July 2009 for the Green Mountain National Forest (GMNF) in Dorset/Peru, Vermont. The Green Mountain National Forest manages federal resources for both present and future generations. Nonnative invasive plant species (NNIS) threaten the health and stability of intact forest habitat because they do not provide the same ecological functions as native species. NNIS outcompete native plant species and fail to provide wildlife with adequate food or shelter. The area surveyed by the LANDS team is part of the Dorset Peru Integrated Resource Area (IRA) and will be managed to maintain the ecological, social, and economic sustainability over the long-term. Early detection and rapid response to invasive species can increase the chances of successfully minimizing threats while populations are still localized. Once populations are widely established, it becomes more difficult to mitigate negative impacts. In addition, longterm invasive species management programs have lower costs associated with maintenance and removal shorter term efforts. Methods Working in teams of two, LANDS interns surveyed areas within the Dorset/Peru area for the non-native invasive species listed on the Green Mountain National Forest (GMNF) NNIS list (see page 5). The NNIS inventories focused on important vector areas (trails, roads, water ways, etc.) in the Dorset/Peru IRA, as well as places where no previous NNIS inventory had been recorded. A NNIS data form provided by the GMNF was filled out for areas where infestations of invasive species occurred (see Appendix). Waypoints for the geographic location of infestations were collected using Garmin GPS units. For larger infestations, interns walked around the perimeter of the infested area to create a polygon with the GPS unit. Waypoints were also taken to indicate where trail maintenance was needed, such as on blocked or water logged trails. Geographic data from GPS units was imported into ArcGIS software to create maps of the NNIS infestations and trail maintenance needs. 4 Green Mountain National Forest Non-Native Invasive Species List 1 Scientific Name Common Name Data Entry Code National I-Rank 2 Species Listed in Federal Noxious Weed Legislation Heracleum mantegazzianum giant hogweed HEMA17 Medium/Low AEPO ALPE4 CEOR LONIC for all Low High/Medium High/Medium High/Medium for all but L. maackii, which is High LOJA LYSA2 PHAU7 POCU6 RHCA3 FRAL4 High/Medium High High High/Medium High/Medium High/Medium ACPL ANSY BETH BEVU ROMU High/Medium Not yet assessed High/Medium Medium/Low Medium/Low Class B Noxious Weeds 3 Aegopodium podagraria Alliaria petiolata Celastrus orbiculatus L. maackii, L. morrowii, L. tatarica, & L. x bella Lonicera japonica Lythrum salicaria Phragmites australis Polygonum cuspidatum Rhamnus cathartica Rhamnus frangula (=Frangula Alnus) goutweed garlic mustard Asiatic bittersweet Shrubby honeysuckles (amur, morrow, tatarian, & Bell’s honeysuckle); also referred to as “exotic bush honeysuckles” Japanese honeysuckle purple loosestrife common reed Japanese knotweed common buckthorn glossy buckthorn Watch Species Acer platanoides Anthriscus sylvestris Berberis thunbergii Berberis vulgaris Rosa multiflora Norway maple wild chervil Japanese barberry common barberry multiflora rose 1 This is an abbreviated list of NNIS species provided by the Forest Service. Species that were not of specific concern or high priority in the area of focus in this project were omitted. 2 National I-Ranks are from NatureServe (2008) and are based on an assessment of invasiveness. 3 Any noxious weed that is not native to the state, is of limited distribution statewide, and poses a serious threat to the State, or any other designated noxious weed being managed to reduce its occurrence and impact in the State. 5 Current Conditions Data Organization The following maps show key areas where NNIS were located in the Dorset/ Peru Integrated Resource Area. They are arranged North to South and by access road. The last two maps are Kirby Hollow Rd and Grouse Lane which were not in our focus area, but located to the east in the Dorset–Peru Remote Backcountry Forest Management Area. Non-native invasive honeysuckle (Lonicera sp.) 6 Dorset Peru IRA NNIS: Overview Map 7 NNIS Maps & Descriptions Lower FR 10: FR10: Forest Access Road • Invasive plants: The predominant NNIS for this road are honeysuckle and garlic mustard. Other NNIS species found were small single plants of common barberry and multiflora rose. Since garlic mustard is an easy species to remove, the crew eliminated this population. However, yearly monitoring will be necessary to curb any future growth. Most honeysuckle plants were fairly small and could be easily eliminated, although there were a few larger, well-established shrubs which might take more removal effort. • Trail Conditions: The road is in good condition. AT/LT (south to Griffith Lake): Hiking Trail • Invasive plants: Intact forest; no invasives. This trail requires no immediate invasive species management, but should be monitored for future infestations. • Trail conditions: Wet and muddy. Some trail maintenance would be helpful to hikers. FR 322: Old logging road • Invasive plants: Teams found small populations of buckthorn, honeysuckle and Phragmites. These invasive plants were newly-established and could be easily removed. In any case, this old logging road should be monitored for the spread of these invasive plants. • Trail conditions: Wet and muddy. Some trail maintenance would be helpful to hikers. Trail Maintenance need on AT/LT at Bromley Mountain 8 9 Old Job Trail Area: FR 30/30A: Old Logging Road • Invasive plants: Teams found honeysuckle, barberry and large patches of wild chervil within the middle of the trail. The honeysuckle and barberry is easy to remove, and although the wild chervil is somewhat more difficult, we recommend removing it as soon as possible. • Trail conditions: We recommend placement of a water bar and the removal of several fallen trees. Old Job: AT Trail • Invasive plants: The crew found a patch of garlic mustard at the Old Job trail trailhead. This patch was removed, but should be continually monitored. Teams also observed several small honeysuckle shrubs, which are easily removed. • Trail conditions: We recommend placing a sign at the trailhead warning hikers of the stream crossing near the Old Job Shelter. Corridor 7: Snowmobile Trail • Invasive plants: Except for the patch of garlic mustard at the trailhead parking lot of the Old Job trail, no invasives were found. The trail should be periodically monitored. • Trail conditions: The lower end of this trail was well-maintained. The upper end, however, was so muddy that at times the trail seemed more like a streambed than a trail. The trail map provided by the Forest Service also appears to be inaccurate in terms of distances, and the spur trail (to Little Mud Pond) does not seem to exist. 10 11 FR 259: FR 259: Residential Road • Invasive plants: This road had the highest number of non-native invasive species. Species observed include: Asiatic bittersweet, honeysuckle, common buckthorn, Japanese knotweed, wild chervil, common barberry, Japanese barberry, multiflora rose, goutweed, and garlic mustard. The garlic mustard, honeysuckle and buckthorn seem to be the greatest in abundance. All visible garlic mustard was removed, but locations should be monitored in future years. • Trail conditions: The road is well-maintained, but there are some issues of slope instability in the wooded section. The side of the slope is falling away under tree roots, which might cause issues of downed trees in the road at a later time. Lake Trail/ Baker Peak Trail: Hiking Trail • Invasive plants: Teams found and removed a large patch of garlic mustard at the trailhead. Team also found a single honeysuckle .5 miles up the trail. • Trail conditions: Trail is well-maintained. Non Native Invasive Wild Chervil (Anthriscus sylvestri) 12 13 FR 21/21A + FR 58: FR 21/21A: Forest Roads • Invasive plants: Honeysuckle was found along FR 21 at roughly the road's midpoint. There is also a patch of Japanese knotweed on the east end of FR 21A near Hapgood Pond. Honeysuckle was also found on an old beaver dam surrounded by core forest. • Trail conditions: Variable. Some sections are deeply rutted and appeared to be worsening from heavy rains, others are in great shape. FR 58: Forest Road • Invasive plants: None. • Trail conditions: The road is in good condition with no obstacles or obstructions. AT/LT (North to Griffith Lake):Hiking Trail • Invasive plants: None. • Trail conditions: Trail is well-maintained. Non-native invasive common buckthorn (Rhamnus cathartica) removal 14 15 Rt. 11: Route 11/30: Busy Highway • Invasive plants: The crew found mature seeding invasive honeysuckle, mature glossy buckthorn, mature common buckthorn, Japanese and common barberry, Japanese knotweed, and Norway maple. • Trail conditions: Road is well-maintained. AT/LT (North to 21): Hiking Trail • Invasive plants: The crew found honeysuckle and oriental bittersweet at the Rt. 11 trail head. The trail itself was clear of invasives. The honeysuckle and bittersweet could be easily removed. In any case, this trail should be periodically monitored for population growth. • Trail conditions: Some trail erosion was found about .5 miles up from trailhead on the left side. Some puncheons need to be repaired or redone. Two widow makers were found .7 miles from the summit as well as 1 mile north of Bromley Summit. Other areas are recommended to have puncheons. Ski Trail (East Side of Mt. Bromley): Hiking Trail and Ski Lift Clearing • Invasive plants: None. • Trail conditions: Trail was well-maintained. Non-native invasive common buckthorn (Rhamnus cathartica) 16 17 Grouse Lane: Grouse Lane (off Northern end of Tower Road) • Invasive plants: The trail itself was clear of invasives, but the perimeter of the parking lot and road had populations of honeysuckle, garlic mustard, multiflora rose, buckthorn and goutweed. Pachysandra (Pachysandra terminalis), a commonly planted exotic groundcover was also found. It is not a species of concern for the GMNF, but indicates the connection between horticultural plantings and this site. The garlic mustard was removed, but this area should be monitored since these invasives could easily spread up the trail and into the undisturbed forest. Neighbors and/or property managers may be dumping yard waste at this location based on the presence of so many commonly planted exotics, or it may be an old homestead site. • Trail conditions: The road leading to the trailhead was in good condition (with the exception of some muddy potholes). The trails were fine, but there were some downed trees that warrant removal. Trail issues along AT/LT at Bromley Mountain 18 19 Kirby Hollow Road: Kirby Hollow Road (Northern End): Residential Road • Invasive Plants: The crew found honeysuckle, buckthorn, Japanese barberry, common barberry, and autumn olive along the main road and longing roads. These plants could be easily removed, and the area should be monitored. • Trail Conditions: For a Class 4 road, this was in remarkably good condition. 20 21 FR 221: (No Map Provided) Little Michigan Trail (Trailhead): Hiking Trail • Invasive plants: Teams found a small population of multiflora rose, which could be easily removed. • Trail conditions: Trail is well-maintained. 221 (Northern Tip on Forest Land): Paved Becoming Dirt Road • Invasive plants: Teams found a small population of honeysuckle, which could be easily removed to prevent further spread. Another small occurrence was found near the intersection with 21A. • Trail conditions: Trail is well-maintained. Non-native invasive garlic mustard (Alliaria petiolata) removal 22 Report Summary Overall, the Dorest Peru Integrated Resource Area of the Green Mountain National Forest is not heavily infested with NNIS. Many trails, especially inner trails were entirely clear of invasives, and most were only sparsely infested. The areas of largest concern were trailheads and residential roads where the public land use impact is greatest. Openings in the forest (e.g. landings and beaver dams) were also infested disproportionally. The Forest Service could manage invasive species by removing existing populations with early detection and rapid response, checking and removing reoccurring species growth annually, and by educating the public on the dangers of planting non-native plants. The existing populations could be fairly easily removed by a crew of volunteers or workers. The Vermont Youth Conservation Corps, for example, contracts out crews for trailbuilding and invasive species removal projects. The Nature Conservancy provides support and educational resources to organization hoping to combat invasive populations. A large part of this effort is community and business education – homeowners need to be aware of the ecological implications of planting nonnative invasive species on their properties and business owners need to be aware of the ecological ramifications of selling or planting NNIS. People may not even know that the species they plant in their gardens can be transported to otherwise undisturbed areas (e.g. Goutweed), and that these colonizations can result in the eradication of native species. The continued monitoring of invasive populations (and areas that are currently not populated by invasives) is necessary. For example, though the LANDS crew removed several infestations of garlic mustard, this invasive species maintains a seed bank that can survive for up to seven years. Even though it is easy to focus on areas that have been overrun with NNIS, areas with small populations of invasives should also be closely monitored – “early detection, rapid response” is the most efficient way of dealing with invasive species. Many of the areas we surveyed had only small populations of NNIS, which could be eradicated relatively easily. 23 Appendix NNIS Form from GMNF Invasive Plant Data Form for Green Mountain & Finger Lakes NF, 2009 v.2 General Site Data: Site ID_0920__________________________________________________________ Instructions: • 1st 2 #s are region 09, 2nd 2 are Forest 20 • 3rd 2 are district (01 = Middlebury, 02 = Manchester, 03 = Hector, 05 = Rochester) • 4th part is the name of the site, e.g., Smith Rd. or Mt. Horrid • 5th part is the first 2 letters of the genus & species names of the invasive plants found at the site, e.g., for multiflora rose (Rosa multiflora), you’d record ROMU (skip if none found) • 6th part: if you record >1 infestation for a single species at a site, the 1st one would have 01 at the end of it, the 2nd would have 02, and so on (skip if none found) Date (MMDDYYYY) _______________ Project Name__________________________ (This will be provided for you.) Examiner Last name ________________First name____________ Middle initial______ Ownership (indicate whether USDA FS, private, or other) __________________________ If USDA FS, list Forest (GMNF or FLNF) __________ & District __________________ State ________County______________________ Topographic quad________________ Waypoint Name_ _ _ _ _ _ Provide location (UTM) UTM Datum ________Zone ____ Easting _______________Northing ______________ Dominant Life Form _ _ (AL = algae; FN = forb/herb; FU = fungus; GR = graminoid; LC = lichen; LI = liana; NP = nonvascular plant; SH = shrub; SS = sub-shrub; TR = tree; UN = unknown; VI = vine) Natural Community Description: please describe the natural community you have surveyed, including list a few of the more common plants (associated species). Associated Species (not required, but helpful) Common Name ___________________OR Genus ________________& species____________________ Common Name ___________________OR Genus ________________& species____________________ Common Name ___________________OR Genus ________________& species____________________ Did you find any non-native invasive plants? __yes __no If yes, fill out the Invasive Species Data. If no, stop there. Invasive Species Data: Plant Code _ _ _ _ _ _ (see list provided; usually 4-6 letters) Common Name ___________________OR Genus ______________ species __________ Phenology _ _ 24 (For forbs/shrubs use: F1 = pre-flowering; F2 = flowering; F3 = fruiting; F4 = senescent/dormant.) (For graminoids use: G1 = leaves partially developed/no heads; G2 = inflorescence inside the sheath; G3 = flower partially or fully exerted from the sheath; G4 = seeds maturing or mature; G5 = senescent/dormant.) Life Form of the invasive plant _ _ (Use same codes as above for Dominant Life Form) Infested Area: Infested Area is defined as the area of land, in acres, containing a single invasive species delineated by the actual perimeter of the infestation or population as defined by the outer edge of the canopy cover of the plants or the visible population of other taxa, excluding adjacent areas not infested and outside the perimeter of the population. Canopy cover is used only to delineate the perimeter of the infestation. Infested Area _____x_____ Square feet (provide if small) ________ Acres (enter to the nearest 0.0001; if square feet given, convert to acres here by dividing the by 43,560 square feet per acre.) It is okay to estimate! Percent Infested: The estimate of “% Infested” is influenced by the perimeter of the infestation, the distribution of plants within the perimeter, species growth characteristics, site characteristics and the degree to which the created feature represents the actual infestation. If an infestation of starthistle, for example, has 1-5% canopy cover with plants and patches scattered evenly across a grassland site and the 2–acre created polygon captures the spatial extent of the infestation, the “% Infested” is 100% or equal to the area of the created polygon. If, however, Canada thistle is found growing in a series of stringer draws or narrow swales with 35% canopy cover but due to the complexity of the site and the distribution of Canada thistle along the draws a single large polygon is created that does not follow the perimeter of stringer draws. Even though the polygon is 20 acres the “% Infested” would typically be a much lower value such as 10%, or in other words, 2 acres of Canada thistle within a 20 acre mapping area (NFS Invasive Species Management Business Rules & Standards Updated 01/29/2009). Percent Infested: (You may choose between the two sets of cover codes; the Daubenmire is preferred, since it is the most consistent from person to person.) Daubenmire Codes __ T (0.1-1%) __ 1 (1.1-5%) __ 2 (5.1-25%) __ 3 (25.1-50%) __ 4 (50.1-75%) __ 5 (75.1-95%) __ 6 (95.1-100%) Cover Ten Codes __ T (0.1-1%) __ 0 (1.1-5%) __ 1 (5.1-15%) __ 2 (15.1-25%) __ 3 (25.2-35%) __ 4 (35.1-45%) __ 5 (45.1-55%) __ 6 (55.1-65%) __ 7 (65.1-75%) __ 8 (75.1-85%) __ 9 (85.1-95%) __ A (95.1-99%) __ X (100%) Distribution _ _ (CL = plants in clumps; LI – linear distribution, e.g., along roads; SE = scattered evenly; SP = scattered patchy.) Within the infestation, how much of the vegetation canopy cover does this species represent? __ T (0-1%) __L (1.1-5%) __M (5.1-25%) __H (25.1-100%) Comments (not required, but very helpful) ________________________________________________________________________ ________________________________________________________________________ ________________________________________________________________________ Map of site (include N/S arrow) – draw a polygon that indicates the infestation at the site. 25 NNIS Counts Road Name Forest Road 10 AT/LT South to Griffith Lake Forest Road 322 Forest Road 30/30A Old Job Trail Corridor 7 Forest Road 221 Little Michigan Area Route 11 Forest Road 30 AT/LT North to 21 Ski Trail Grouse Lane (printed data forms read Tower Road) Kirby Hollow Road Forest Road 259 (continued) Non-Native Invasives 17 Honeysuckle 6 Garlic Mustard 2 Multiflora Rose 1 Common Barberry None 2 Honeysuckle 2 Common Buckthorn 1 Phragmites 6 Honeysuckle 3 Wild Chervil 1 Japanese Barberry 1 Honeysuckle 1 Garlic Mustard None 1 Honeysuckle 1 Multiflora Rose 41 Honeysuckle 3 Common Buckthorn 2 Japanese Knotweed 1 Phragmites 1 Common Barberry 1 Japanese Barberry 1 Norway Maple 1 Glossy Buckthorn 6 Honeysuckle 3 Wild Chervil 1 Japanese Barberry 4 Honeysuckle 1 Oriental Bittersweet None 7 Honeysuckle 2 Garlic Mustard 2 Multiflora Rose 1 Goutweed 1 Buckthorn 9 Honeysuckle 6 Buckthorn 2 Japanese Barberry 1 Autumn Olive 1 Common Barberry 18 Garlic Mustard 16 Honeysuckle 26 Forest Road 259 (continued) 13 Common Buckthorn 8 Goutweed 4 Multiflora Rose 3 Japanese Barberry 2 Common Barberry 2 Japanese Knotweed 2 Wild Chervil 1 Asiatic Bittersweet 27