Showing posts with label Dog-strangling vine. Show all posts
Showing posts with label Dog-strangling vine. Show all posts

3 March 2008

Dog-Strangling Vine

"We stand to lose our natural ecosystem, all our native plants, everywhere in the Great Lakes Basin and southern Ontario.” - Ontario Ministry of Natural Resources Ecologist Waysel Bakowsky, when asked about the threat of DSV.

Dog-Strangling Vine is a highly invasive perennial vine that dominates and destroys ecosystems.If you see this plant on your property, or your local park or community garden, the alley where you walk your dog, the parking lot at work, the playground at your kid's day care, your mother-in-laws' garden, or your neighbour's yard (with their permission of course) please remove it. ...before it looks like this:or worse, this:

photo by Stephen J. Darbyshire

"DSV" is some times understood to be two similar species (Pale Swallow-wort Cynanchum rossicum or Vincetoxicum rossicum which prefers sun, and Black Swallow-wort Cynanchum louiseae or Vincetoxicum nigrum) but, for most practical purposes it's generally referred to, and treated as, simply DSV.

DSV is invading, dominating and destroying natural areas, habitats and ecosystem functions in and near our area: oak savannah, forests, woodlands, tallgrass prairies, meadows, even alvars. DSV directly threatens to displace all of our native plants, in all of our natural areas, except wetlands (although it does grow along riparian river and stream edges). It spreads by prolific wind-dispersed seeds similar to our native milkweeds. Seeds are poly-embryonic (one seed can produce several viable embryos / plants). Plants can self-pollinate in a single day. Research has found decline in the populations and diversity of insects in old fields dominated by DSV. DSV displaces native Milkweed species, impacting pollinators who depend on them. Also, in experiments, when given the choice of both DSV and Milkweed, Monarch butterflies have been observed laying up to 1/4 of their eggs on DSV, resulting in death of those larvae. DSV is salt-tolerant and can handle a range of substrates with variable pH's from limestone to granite, and is found in gravel, clay and sandy soils. Currently there are no biological controls to keep DSV in check.

REMOVE:

How? Dig out the entire root of the plant (pulling is ineffective: roots will persist and form several plants). Its easier if you use the right tools (weed rockers don't get out all the brittle roots, and planting trowels are often dull and clumsy when used as weeding tools). In hard compacted soils, try using a sharper-edged trowel or spade. Also a "Weed Wrench" is recommended (Mary Gartshore, Pterophylla Nurseries). If you do dig out the roots (good for you!), avoid any unnecessary soil disturbance (it day lights existing seed bank in the soil and also provides a place for new invasive seeds to enter) and backfill the hole to prevent further invasion. At this point you can also either replant with the area with desired species (of course I'm recommending natives) and/or cover the area with mulch.

In infestations too large to dig out, control further spreading by cutting the plants. This will help to prevent seed pods from maturing. You will likely have to cut at least twice during the season (every year for the 1st few years), as plants continue to produce seeds from May to November. (Note: Fletcher Wildlife Garden has had some success with a single cut per year when timed around June 26.) Common tools used for cutting: garden shears (but they can be hard on the back), weed whippers and mowers. However, Fletcher Wildlife Garden has found scythes to be easier, efficient (requiring less volunteers and time) and more manouverable when trying to cut around desired plant species among the DSV. Scythes are available at Lee Valley for $112.

Larger patches can also be controlled by covering the area with tarps or landscape barrier fabrics (secured by landscape fabric stakes / pegs or coat hangers) or a thick layer of newspaper for several months, followed by the removing remaining persisting plants. Another control option is Glyphosate (aka Round-Up). Glyphosate is not a one-shot deal: Cara Webster (City of Toronto Urban Forestry) recommends 2 glyphosate applications each year for the 1st 2 years. Please see this earlier post for more information about glyphosate and DSV.

DISPOSE:

After removing or cutting DSV, DO NOT dispose of roots or seeds in your garden composter, or in a open air pile. Reproductive parts of DSV and other weeds can go into regular city yard waste collection.

REPLANT:

Replant weeded area with local native plants (e.g. for no cost: use nearby in-season seeds such as common milkweed, cup plant, grey-headed coneflower) or transplant other ethically acquired native plants (the $5 for SER-O's 2007-2008 Native Plant Resource Guide is money well spent!). Start with common native plants that are most likely to survive and become establish (one possible strategy might be to start with the more aggressive colonizing natives.) DSV appears to be more aggressive and capable of producing more seeds in sunny areas, however, it can also invade thicket (e.g sumacs, hawthorns and even dense cedars - Patricia Mohr) and shady areas (growing up to 9 feet, covering and out-competing shrubs and tree seedlings). However, it's most often it's along the forest edges and openings than dense shade areas. DSV "doesn't do well in areas of continuous dense forest" (Forester Jim Robb from Friends of the Rouge Watershed). For existing or new shade areas, plant with all successional forest layers (ground cover ->herbaceous layer -> shrub ->vine ->trees. For trees, Jim Robb recommends including fast growing early successional poplars and aspen as well as pine, alongside broad leaf hardwoods).

Along with planting in successional layers and using common locally adapted native plants appropriate for your site's conditions, two other defensive planting strategies are: planting in high density (more plants /sq M) and, planting in seasonal guilds -- the idea being continuous coverage through the warm seasons, for example: early spring = early woodland ephemerals like ginger, bloodroot, may apple; summer = woodland sunflower; autumn = zig-zag goldenrod and big-leaved aster.

Some plants seem to withstand DSV invasion better than others, possibly as a result of their allelopathic properties, including Zig-zag goldenrod (Todmorden Mills Wildflower Preserve, Sept. 2006 Newsletter), tall goldenrod (Steve Smith, Urban Forest Associates Inc.), some juglone spp. (Jim Robb), and also flowering raspberry (Fletcher Wildlife Garden), Colorado Blue Spruce (non-native but not invasive)(Gavin Miller). After planting, add a thick layer of mulch on bare ground around desired species.

To prevent DSV and other invasions: keep your healthy areas healthy (use mulch / leaf litter, do not disturb soils unnecessarily, grow plants adapted to your site conditions and region, do not use synthetic fertilizers or salts, catch and control any invasive early on), also plant and/or mulch nearby bare ground patches and disturbed areas and understorey vacancies, before they fill with invasives.

RETURN:

Continue to cut and control nearby DSV, monitor, weed, mulch and replant the area.

DSV Fact Sheets:

Essential DSV reading:

More info on control strategies and tools:

Get involved locally:

  • volunteer on a stewardship site near you: GTA Stewardship and “Green Groups" listed by watershed
  • take care of the lands (public or private) where you live
  • take pictures of DSV and donate them to your local stewardship group, and use them yourself (on your own website, blog, newsletters, email lists, community garden agendas, meetings and workshops) alongside more information about DSV and what you can do about it.

3 September 2007

DSV control - the High Park experience

Nobody I know likes pesticides or enjoys working with them, but, they have their place.

Honestly, I see glyphosate as a treatment for DSV invasion a lot like I see chemotherapy as a treatment for cancer.

When my mother was diagnosed with cancer, the oncologist told us (and, forgive me, but what he said still reminds me of weed eradication protocols): "our methods are still crude: we can cut it (surgical oncology), burn it (radiation) and poison it (chemotherapy)." Suddenly something as previously unintuitive and horrifying, as having my mother subjected to courses of poisonous chemicals, had become a hopeful option (in a new reality
with nothing but compromised options and outcomes) that might prolong or save her life. An option and a pressing decision too.

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High Park includes globally rare Black Oak Savannah remnants. The folks who steward that site have a local and international responsibility to preserve the indigenous flora and fauna there = High Park is an excellent example of when glyphosate is an excellent choice (again, in a new reality with nothing but compromised options and outcomes) for conservation.


Restoration Challenges: The Ongoing Battle with Dog-strangling Vine Control at High Park

By Cara Webster

The City of Toronto established a restoration crew dedicated to the restoration of the Black Oak savannah and woodland habitats in High Park in 2000. The project is now in its fourth field season and has made many successes to date with the control of invasive plants, the reintroduction of fire and the reintroduction of native plants. One very persistent invasive species, Dog-strangling Vine (Vincetoxicum rossicum and V. nigrum) has presented many challenges to the restoration of High Park. Dog-strangling Vine is a perennial herbaceous vine that easily invades the open habitat of the savannah and it also tolerates some shade in the woodland areas. Once Dog-strangling Vine is established it produces an extensive root system and abundant seed that is easily spread into adjacent areas. Volunteers in High Park attempted to control Dog-strangling Vine with manual methods such as cutting and pulling but had little success. The reintroduction of fire has also been unsuccessful at controlling this species and it may in fact be giving it an advantage early in the season. Test plots were set-up before the spring burn this year to observe differences in emergence, density and other factors between burned and unburned plots. We will continue to monitor these plots to observe long-term effects. Due to the lack of control using other methods the restoration crew has been using intensive treatments of herbicide over the past three years.

Chemical Control Methods of Dog-strangling Vine
Several different methods of herbicide application, herbicide types and dilutions have been tested to develop an effective control for this species. Roundup-Transorb, a glyphosate based herbicide, is being used since its formulation allows quick absorption and is very practical in the field since it can be applied up to an hour before rainfall. A 33% dilution of Roundup-Transorb is applied to plants using a car wash mitt to wick the plants and avoid harm to the surrounding native vegetation. Large monocultural stands are sprayed using a backpack sprayer or hand sprayer. We have found that the label recommended 2% dilution to be used in a sprayer is not very effective at controlling this species but we are continuing to track these results. Treatments have been initiated each year at the beginning of June and continue until early September to cover approximately 20 hectares in High Park. Each area is treated twice over the field season, spaced at least one month apart, to re-treat persistent plants and to catch the next plants coming into flower. Many large colonies in the park have been reduced, however, longterm maintenance is required to prevent re-establishment by individual stems. In 2002 and 2003 an additional crew has also been contracted to cover a larger area of the park and to prevent seed in untreated areas from spreading into treated areas. Priority is given to areas with rare species and areas that will be burned the following spring to prevent further encouragement of Dogstrangling Vine. Although it has been a labour-intensive process the Dog-strangling Vine population at High Park is being reduced. Three former Dog-strangling Vine colonies have been re-planted with native species to recapture the bare sites. Some colonies in the woodland areas have been able to naturally regenerate with plants from the surrounding area and from the seed bank. The restoration crew will continue to monitor the results of these efforts and develop new strategies to protect the rare Black Oak savannah.

For further information, or if you have any other experiences to share, please contact cwebster@toronto.ca.
Cara Webster is Restoration Specialist with Urban Forestry Services for the City of Toronto.

From: http://www.serontario.org/pdfs/jul2003.pdf

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30 August 2007

Monarch Butterflies laid 1/4 of eggs on Dog-Strangling Vine (Vincetoxicum nigrum), larvae die


photo: Kitty Kohout
Dog-strangling Vine (Black swallow-wort) Vincetoxicum nigrum (L.) Moench
Vincetoxicum: from vincere for "to conquer" and toxicum for "poison"

“Haribal and Renwick (1998) found that female monarch butterflies (Danaus plexippus L.) oviposit on black swallow-wort (V. nigrum) in choice tests in the laboratory; however, resulting larvae were not able to complete development on this plant. Dacey and Casagrande (pers. obs.) found that monarchs readily oviposit on V. nigrum in the laboratory and in large cages in the field. In both cases, when monarchs were given a choice of ovipositing on common milkweed (A. syriaca) or black swallow-wort, they laid approximately 25% of their eggs on the swallow-wort, and all of the resulting larvae died. Dacey and Casagrande (pers. obs.) found eggshells as evidence of monarch oviposition on black swallow-wort in uncaged field populations of swallow-wort and milkweed.” Invasive Plants of the Eastern United States - Swallow-worts.
In Toronto we have two species of Dog-Strangling Vine /"DSV" - Pale Swallow-wort V. rossicum syn. Cynanchum rossicum and Black Swallow-wort V. nigrum . Both have been recorded since the 1800's. - Kaufman & Kaufman

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