Stop Wasting Your Time on Invasives Plan Your

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Stop Wasting Your Time on Invasives – Plan Your Way to Success! Ellen Jacquart

Stop Wasting Your Time on Invasives – Plan Your Way to Success! Ellen Jacquart The Nature Conservancy ejacquart@tnc. org

I have a confession…. . I really, really hate planning.

I have a confession…. . I really, really hate planning.

They’re everywhere!! They are not everywhere. Really. It is crucial to know how much

They’re everywhere!! They are not everywhere. Really. It is crucial to know how much there is; planning will help you select winnable battles. #1 Misconception

Diversity is more than a species count. Invasive plants can have many negative impacts

Diversity is more than a species count. Invasive plants can have many negative impacts to natural areas. It’s all ok – it’s just more diversity! Planning helps decide which invasive plants are causing the worst impacts and so should be higher priority. #2 Misconception

Local control and management only Public awareness typically begins Introduction Detection Plant absent Scattered

Local control and management only Public awareness typically begins Introduction Detection Plant absent Scattered locations Time Numerous locations At or near biological potential Control Costs Eradication unlikely, intense effort required Acres Infested Eradication simple Eradication feasible Weed Increase Over Time and Control Potential

Considerations in controlling invasive species • Prevention is the ALWAYS the best strategy! •

Considerations in controlling invasive species • Prevention is the ALWAYS the best strategy! • Early detection is the second best strategy

By the time you are in the control and management strategy, the cost is

By the time you are in the control and management strategy, the cost is huge and the failure rate is high. When I was young, I observed that nine out of every ten things I did were failures, so I did ten times the work. George Bernard Shaw

Why do so many invasive control efforts fail? • unrealistic goals • lack of

Why do so many invasive control efforts fail? • unrealistic goals • lack of follow-through • no size-up before starting • ineffective method used How do we succeed?

You can do it! Some successful invasive plant management projects: • Lanphere Dunes in

You can do it! Some successful invasive plant management projects: • Lanphere Dunes in Humboldt Bay NWR • Sandy River knotweed project • Weed it Now! Berkshire-Taconic landscape project

Lanphere Dunes, Humboldt Bay NWR Plants were manually cleared over three years Before -

Lanphere Dunes, Humboldt Bay NWR Plants were manually cleared over three years Before - 10 acres of European dune grass infestation by 1990 After – native plant cover increased dramatically

Sandy River project, northern Oregon TNC, Oregon Watershed Enhancement Board, the Bureau of Land

Sandy River project, northern Oregon TNC, Oregon Watershed Enhancement Board, the Bureau of Land Management and the United States Fish and Wildlife Service

Sandy River project, northern Oregon What has been accomplished? • Surveyed 10 miles of

Sandy River project, northern Oregon What has been accomplished? • Surveyed 10 miles of river (600 acres) representing 200 different landowners • 150 gross acres of knotweed found made up of 2, 840 different patches • All acres have been treated at least once; most treated 3 times • Stems have been reduced 80%; control expected in 2005

Weed It Now! Berkshire-Taconic Landscape Project Japanese barberry

Weed It Now! Berkshire-Taconic Landscape Project Japanese barberry

From a 120, 000 acre landscape they chose a 9, 000 core area to

From a 120, 000 acre landscape they chose a 9, 000 core area to inventory and control barberry.

Weed It Now! What has been accomplished? -goal is to reduce Japanese barberry to

Weed It Now! What has been accomplished? -goal is to reduce Japanese barberry to 5% of the area. -started treating in 2002, now treating approximately 2, 000 acres per year in a three state area

Why are these projects successful? • Working with partners across boundaries (Cooperative Weed Management

Why are these projects successful? • Working with partners across boundaries (Cooperative Weed Management Areas)

Cooperative Weed Management Areas – The term CWMA, or Cooperative Weed Management Area, refers

Cooperative Weed Management Areas – The term CWMA, or Cooperative Weed Management Area, refers to a local organization that integrates invasive plant management resources across jurisdictional boundaries in order to benefit entire communities.

CWMA Cookbook: A Recipe for Success A Step-by step Guide on How to Develop

CWMA Cookbook: A Recipe for Success A Step-by step Guide on How to Develop a Cooperative Weed Management Area in the Eastern United States

Why are these projects successful? • Working with partners across boundaries (Cooperative Weed Management

Why are these projects successful? • Working with partners across boundaries (Cooperative Weed Management Areas) • Consistent strategy over multiple years • PLANNING

Plan before you act! TNC’s Weed Management Template The template, tables, and more can

Plan before you act! TNC’s Weed Management Template The template, tables, and more can be found at: tncweeds. ucdavis. edu/products

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess impact of management actions Weed Management Template 2. Identify and prioritize species/infestations that threaten targets and goals 3. Assess control techniques 4. Develop and implement weed management plan Figure 1. Flow chart for Adaptive Management of Weeds describing management actions and decisions confronting natural area managers (from Randall (1997), based on a diagram by Oren Pollak, personal communication).

1. Establish conservation targets and goals • Remember – you are NOT managing invasive

1. Establish conservation targets and goals • Remember – you are NOT managing invasive plants • You ARE managing land for particular goals and objectives: – Rare species – High quality natural communities – Productive forest land

2. Identify and prioritize species/infestations that threaten targets and goals • The most over-looked

2. Identify and prioritize species/infestations that threaten targets and goals • The most over-looked step, and the hardest step, in the process • In short - ‘stop pulling the dandelions’

Prioritization • Site-based Prioritization – Where do I go first? • Species-based Prioritization –

Prioritization • Site-based Prioritization – Where do I go first? • Species-based Prioritization – Which do I go after first? A combination of both are necessary for success.

Site-Based Invasive Prioritization: WHERE do I go first? 1. Identify and map invaded and

Site-Based Invasive Prioritization: WHERE do I go first? 1. Identify and map invaded and un-invaded areas (NO MAP – NO CONTROL!!) 2. Focus on large blocks of un-invaded areas – keep them un-invaded 3. Control small outlier populations first 4. ‘Unfragment’ boundaries of invaded areas 5. Reverse the invasion – expand the uninvaded area outward.

Site-Based Invasive Prioritization: WHERE do I go first? 6. For long distance dispersers: -in

Site-Based Invasive Prioritization: WHERE do I go first? 6. For long distance dispersers: -in aquatic settings, control upstream to downstream -for bird-dispersed species, control large seed source populations first

Site-Based Invasive Prioritization: WHERE do I go first? 7. All roads, trails, and watercourses

Site-Based Invasive Prioritization: WHERE do I go first? 7. All roads, trails, and watercourses are invasive corridors; survey them regularly to detect new invaders quickly 8. Keep your focus on targets – restoration may be necessary.

Setting Species Priorities: WHAT do I go after first? I. Current extent of the

Setting Species Priorities: WHAT do I go after first? I. Current extent of the species on or near the site; II. Current and potential impacts of the species; III. Value of the habitats/areas that the species infests or may infest; and IV. Difficulty of control.

I. Current extent of the species. 1. Species not yet on site but present

I. Current extent of the species. 1. Species not yet on site but present nearby. 2. Species present as new populations or outliers of larger infestations, esp. if expanding rapidly. 3. Species present in large infestations that continue to expand 4. Species present in large infestations that are not expanding. Where do I get this information?

Inventory! • Spend the first dollars you get on inventory. • ‘The NAWMA standard’

Inventory! • Spend the first dollars you get on inventory. • ‘The NAWMA standard’

NAWMA standard(North American Weed Management Association) Just three things to address: - What is

NAWMA standard(North American Weed Management Association) Just three things to address: - What is it? - Where is it? - How much is there? -gross vs. infested acres

45 acres gross area 9 + 5 = 19 acres infested area 30% cover

45 acres gross area 9 + 5 = 19 acres infested area 30% cover 100 -acre wetland site 100% cover 30 acres 5 10 50% cover

Mapping Standards: • North American Weed Managers Association http: //www. nawma. org/

Mapping Standards: • North American Weed Managers Association http: //www. nawma. org/

Setting Priorities: I. Current extent of the species on or near the site; II.

Setting Priorities: I. Current extent of the species on or near the site; II. Current and potential impacts of the species; III. Value of the habitats/areas that the species infests or may infest; and IV. Difficulty of control.

II. Current and potential impacts of the species. 1. Species that alter ecosystem processes

II. Current and potential impacts of the species. 1. Species that alter ecosystem processes such as fire frequency, sedimentation, nutrient cycling, or other ecosystem processes. 2. Species that outcompete natives and dominate otherwise undisturbed communities. 3. Species that do not outcompete dominant natives, BUTa) Prevent or depress recruitment or regeneration of native species, OR b) Reduce or eliminate resources used by animals. 4. Species that overtake and exclude natives following natural disturbances such as fires, floods, or hurricanes.

III. Value of the habitats/areas the species infests or could infest 1. Infestations that

III. Value of the habitats/areas the species infests or could infest 1. Infestations that occur in the most highly valued habitats or areas of the site – especially areas that contain rare or highly valued species or communities and areas that provide vital resources. 2. Infestations that occur in less highly valued portions of the site. Areas already badly infested by other weeds may be given lower priority unless the species in question will make the situation significantly worse.

IV. Difficulty of control and establishing replacement species. 1. 2. 3. 4. Species likely

IV. Difficulty of control and establishing replacement species. 1. 2. 3. 4. Species likely to be controlled or eliminated with available technology and resources and which desirable native species will replace with little further input. Species likely to be controlled but will not be replaced by desirable natives without an active restoration program requiring substantial resources. Species difficult to control with available technology and resources and/or whose control will likely result in substantial damage to other, desirable species. Species unlikely to be controlled with available technology and resources.

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess impact of management actions Weed Management Template 4. Develop and implement weed management plan 2. Identify and prioritize species/infestations that threaten targets and goals 3. Assess control techniques

Prairie Acres Preserve – 100 acres of mixed wet, mesic and dry prairie Congratulations!

Prairie Acres Preserve – 100 acres of mixed wet, mesic and dry prairie Congratulations! You are the new steward for this site.

Prairie Acres Preserve targets: • Wet prairie • Prairie White Fringed Orchid • Massasauga

Prairie Acres Preserve targets: • Wet prairie • Prairie White Fringed Orchid • Massasauga Rattlesnake

Prairie Acres Preserve – Massasauga habitat – wetland open upland Wet prairie, orchid habitat

Prairie Acres Preserve – Massasauga habitat – wetland open upland Wet prairie, orchid habitat Road Targets Po R we O W rlin e House Dry prairie habitat Wet/Mesic prairie habitat

Prairie Acres Preserve – (18 ac. ) Road Inventory of invasives, summer 2003 Tree

Prairie Acres Preserve – (18 ac. ) Road Inventory of invasives, summer 2003 Tree of heaven (10 acres) Reed canary grass (2 ac. ) Asian bush honeysuckle Po R we O W rlin e House

Prairie Acres Preserve – (18 ac. ) Road Targets and Invasives Tree of heaven

Prairie Acres Preserve – (18 ac. ) Road Targets and Invasives Tree of heaven (10 acres) Reed canary grass (2 ac. ) Asian bush honeysuckle Po R we O W rlin e House Which invasives are threats to your targets?

Table 1. Assign priority 1 to 4 in each cell. Common Name Tree of

Table 1. Assign priority 1 to 4 in each cell. Common Name Tree of Heaven Reed Canary Grass Asian Bush Honeysuckle Current Extent Current/ Potential Impacts Value of Habitat Infested Difficulty of Control

I. Current extent of the species. 1. Species not yet on site but present

I. Current extent of the species. 1. Species not yet on site but present nearby. 2. Species present as new populations or outliers of larger infestations, esp. if expanding rapidly. 3. Species present in large infestations that continue to expand 4. Species present in large infestations that are not expanding.

Prairie Acres Preserve – (18 ac. ) Road Inventory of invasives, summer 2003 Tree

Prairie Acres Preserve – (18 ac. ) Road Inventory of invasives, summer 2003 Tree of heaven (10 acres) Reed canary grass (2 ac. ) Asian bush honeysuckle Po R we O W rlin e House

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Tree of Heaven 3 Reed Canary Grass 2 Asian Bush Honeysuckle 3 Current/ Potential Impacts Value of Habitat Infested Difficulty of Control

Setting Priorities: I. Current extent of the species on or near the site; II.

Setting Priorities: I. Current extent of the species on or near the site; II. Current and potential impacts of the species; III. Value of the habitats/areas that the species infests or may infest; and IV. Difficulty of control.

II. Current and potential impacts of the species. 1. 2. 3. Species that alter

II. Current and potential impacts of the species. 1. 2. 3. Species that alter ecosystem processes such as fire frequency, sedimentation, nutrient cycling, or other ecosystem processes. Species that outcompete natives and dominate otherwise undisturbed communities. Species that do not outcompete dominant natives, BUT 1. 2. 4. Prevent or depress recruitment or regeneration of native species, OR Reduce or eliminate resources used by animals. Species that overtake and exclude natives following natural disturbances such as fires, floods, or hurricanes.

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Current/ Potential Impacts Tree of Heaven 3 2 Reed Canary Grass 2 4 Asian Bush Honeysuckle 3 2 Value of Habitat Infested Difficulty of Control

III. Value of the habitats/areas the species infests or could infest 1. Infestations that

III. Value of the habitats/areas the species infests or could infest 1. Infestations that occur in the most highly valued habitats or areas of the site – especially areas that contain rare or highly valued species or communities and areas that provide vital resources. 2. Infestations that occur in less highly valued portions of the site. Areas already badly infested by other weeds may be given lower priority unless the species in question will make the situation significantly worse.

Prairie Acres Preserve – (18 ac. ) Road Targets and Invasives Tree of heaven

Prairie Acres Preserve – (18 ac. ) Road Targets and Invasives Tree of heaven (10 acres) Reed canary grass (2 ac. ) Asian bush honeysuckle Po R we O W rlin e House

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Current/ Potential Impacts Value of Habitat Infested Tree of Heaven 3 2 2 Reed Canary Grass 2 4 1 Asian Bush Honeysuckle 3 2 1 Difficulty of Control

IV. Difficulty of control and establishing replacement species. 1. 2. 3. 4. Species likely

IV. Difficulty of control and establishing replacement species. 1. 2. 3. 4. Species likely to be controlled or eliminated with available technology and resources and which desirable native species will replace with little further input. Species likely to be controlled but will not be replaced by desirable natives without an active restoration program requiring substantial resources. Species difficult to control with available technology and resources and/or whose control will likely result in substantial damage to other, desirable species. Species unlikely to be controlled with available technology and resources.

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Current/ Potential Impacts Value of Habitat Infested Difficulty of Control Tree of Heaven 3 2 2 3 Reed Canary Grass 2 4 1 2 Asian Bush Honeysuckle 3 2 1 1

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Current/ Potential Impacts Value of Difficulty Habitat of Infested Control Sum Tree of Heaven 3 2 2 3 10 Reed Canary Grass 2 4 1 2 9 Asian Bush Honeysuckle 3 2 1 1 7 But what if….

II. Current and potential impacts of the species. 1. 2. 3. 4. Species that

II. Current and potential impacts of the species. 1. 2. 3. 4. Species that alter ecosystem processes such as fire frequency, sedimentation, nutrient cycling, or other ecosystem processes. Species that outcompete natives and dominate otherwise undisturbed communities. Species that do not outcompete dominant natives, BUT 1. Prevent or depress recruitment or regeneration of native species, OR 2. Reduce or eliminate resources used by animals, OR 3. Promote populations of invasive non-native animals by providing them with resources otherwise unavailable in the area. Species that overtake and exclude natives following natural disturbances such as fires, floods, or hurricanes. What if Reed Canary Grass is really a 2, not a 4?

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Current/ Potential Impacts Value of Difficulty Habitat of Infested Control Sum Tree of Heaven 3 2 2 3 10 Reed Canary Grass 2 4 X 2 1 2 9 X 7 Asian Bush Honeysuckle 3 2 1 1 7 What if you have a tie?

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent

Table 1. Assign priority 1 to 4 in each cell. Common Name Current Extent Current/ Potential Impacts Value of Difficulty Habitat of Infested Control Sum Tree of Heaven 3 6 X 2 2 3 10 X 13 Reed Canary Grass 2 4 X 2 1 2 7 9 X Asian Bush Honeysuckle 3 6 X 2 1 1 7 10 X Single most important factor is current extent – double it and add again.

Prairie Acres Preserve – (18 ac. ) Road Site-based prioritization Tree of heaven (10

Prairie Acres Preserve – (18 ac. ) Road Site-based prioritization Tree of heaven (10 acres) Reed canary grass (2 ac. ) Asian bush honeysuckle Po R we O W rlin e House For RCG, control upstream to downstream

Prairie Acres Preserve – (18 ac. ) Road Site-based prioritization Tree of heaven (10

Prairie Acres Preserve – (18 ac. ) Road Site-based prioritization Tree of heaven (10 acres) Reed canary grass (2 ac. ) Asian bush honeysuckle Po R we O W rlin e House For ABH, control seed source first, then outliers

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess impact of management actions Weed Management Template 2. Identify and prioritize species/infestations that threaten targets and goals 3. Assess control techniques 4. Develop and implement weed management plan Figure 1. Flow chart for Adaptive Management of Weeds describing management actions and decisions confronting natural area managers (from Randall (1997), based on a diagram by Oren Pollak, personal communication).

3. Assess control techniques • For only those species that pose a threat •

3. Assess control techniques • For only those species that pose a threat • The ‘right’ technique may be different for a 1/10 acre of scattered garlic mustard plants vs. a 5 acre area dominated by garlic mustard – consider all the possible tools

How to Pull Garlic Mustard 1. Pull plants in late March/early April as they

How to Pull Garlic Mustard 1. Pull plants in late March/early April as they start to bolt – do not need to bag and remove 2. Pull plants again in mid-April as they start to flower – bag and remove 3. Pull plants again in late April/mid-May as they fruit – bag and remove 4. Repeat every year for 10 years

4. Develop and implement weed management plan 1. INTRODUCTION A. Description of the Site,

4. Develop and implement weed management plan 1. INTRODUCTION A. Description of the Site, Conservation Targets, and Management Goals B. How Weeds Threaten Targets and Interfere with Management Goals C. Inventory of Weeds on the Site 2. OVERVIEW OF WEED MANAGEMENT PLAN A. Management Philosophy & Setting Priorities (Using Adaptive Strategies) B. Summary of Specific Actions Planned C. Tables Table 1: Prioritized List of Weed Species Table 2: Weed Management Plan Implementation Schedule Table 3: Projected Resource Costs Table 4: Itemized Actual Annual Cost and Labor Worksheets Table 5: Projected and Actual Resource Uses 3. SPECIFIC WEED CONTROL PLANS Bad Weed #1 (Weedicus vulgare) Nasty Weed #2 (Commonus horridus) Evil Weed #3 (Diabolicus invasivii)

Weed Control Plan for Centaurea solstitialis (Yellow Starthistle) Priority: High (trails & Visitor Center),

Weed Control Plan for Centaurea solstitialis (Yellow Starthistle) Priority: High (trails & Visitor Center), low (grassland areas)—High priority has been assigned to removing unsightly infestations around the Visitor Center and along trails, which it can use to invade new areas. It interferes with primary management goals in grasslands by diminishing waterfowl nesting habitat, but the infestation is too large to eradicate with available technology and resources. Description: Annual taprooted herbaceous plant in the sunflower/thistle family (Asteraceae). It can grow up to 1 m tall with distinctive gray-green leaves and stems and yellow flowerheads surrounded by spiny bracts. It produces abundant seed each year. Current Distribution on the Preserve: Extensive populations throughout the preserve’s Savanna areas, along the trails, and near the visitor center. Other units containing populations of yellow starthistle are shown in the Appendix sample maps.

Measurable Objectives and Goal: The yellow starthistle infestation is extensive in and around the

Measurable Objectives and Goal: The yellow starthistle infestation is extensive in and around the preserve, and cannot be eradicated with available technology. Instead, our objectives are: *Eradicate the pest along all roads and trails that lead to uninfested areas. *Reduce infestations along the Willow Slough trail, especially at the trailhead and near the visitor center. *Determine the extent of the infestation on the preserve and the value of controlling it in grasslands and savannas, especially in areas where waterfowl nest. Control Options *Hand pull plants where infestations are small. *Spot treat infestations with clopyralid with an added dye early in the growing period. *Clean vehicles before entering uninfested areas. Note - the yellow starthistle infestation is extensive. Lesser-priority areas will have to be neglected. Highest priority will be given to reducing new outbreaks and to removing the plant from currently infested roads and trails that lead to uninfested areas.

5. Monitor and assess impact of management actions • Necessary to show whether treatments

5. Monitor and assess impact of management actions • Necessary to show whether treatments are effective • Can be done at different levels of intensity – ‘ocular estimate’ vs. research plots

6. Review and modify • Change what isn’t working. • Change priorities as new

6. Review and modify • Change what isn’t working. • Change priorities as new species emerge

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess

1. Establish conservation targets and goals 6. Review and modify 5. Monitor and assess impact of management actions Weed Management Template 2. Identify and prioritize species/infestations that threaten targets and goals 3. Assess control techniques 4. Develop and implement weed management plan Figure 1. Flow chart for Adaptive Management of Weeds describing management actions and decisions confronting natural area managers (from Randall (1997), based on a diagram by Oren Pollak, personal communication).

Thanks for your attention!

Thanks for your attention!