Is the cost of Phragmites control worth it?

In a survey of 285 land managers in the U.S., researchers found that they spent nearly $4 million dollars per year on control of non-native Phragmites australis on 89,000 ha but few were happy with the results of their control efforts.  The  goals of most managers were to restore native flora and fauna and improve ecosystem function, but less than half felt they had met those goals.  Most organizations cited a lack of personnel and monetary constraints, along with re-invasion of Phragmites and difficulty in accessing populations.  The researchers found no correlation between amount spent on control and success in achieving management goals.

So does that mean that Phragmites control is a waste of time and money?  Or just that there needs to be more long-term funding of control and monitoring or new techniques developed for control?  Research on effects of Phragmites on natural systems shows mixed results.  Some studies show changes to benthic fauna and others show few changes. Phragmites is thought to alter nutrient cycling and some hydrological processes.  Different populations under different salinity levels and hydrological regimes may vary in their ecological effects.  Many control projects receive one-time funding and re-invasion can occur before any significant changes in flora, fauna or ecosystem processes have had time to take place.  Biological control is being investigated as a potential option, but because there are native strains of Phragmites australis, it could be difficult to find a biological control agent that doesn’t damage native populations.

The article ends with a cautionary note to land managers to assess what damage they think is occurring before spending money on control and to attempt to increase post-control monitoring.

Martin, L. J. and B. Blossey. 2013. The runaway weed: costs and failures of Phragmites australis management in the USA. Estuaries and Coasts, 36(3): 626-632.

 

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Invasive Species humor

The Illinois Invasive Species Awareness Week blog has just posted a new installment on invasive species humor!  This one focuses on illustrations, http://illinoisisam.blogspot.com/2013/02/the-hunt-for-invasive-species-slogans.html.

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South American Invasive Plants

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horses in a pasture invaded by thistles

I’m in Argentina for six weeks, and it’s been interesting observing what species invasive here are well-known to me from North America.  One of the best ways of predicting species’ invasiveness is by knowing if they are invasive elsewhere after all! The following photos are from the southern part of Buenos Aires Province and from the Costanera Sur Ecological Reserve in the city of Buenos Aires.  Other plants not shown here have included white mulberry, Morus alba, tree-of-heaven, Ailanthus altissima, two other thistle species, Carduus spp., purple starthistle, Centaurea calcitrapa, Eucalyptus species, Acacia species, and castor bean plant, Ricinus communus. Monterey pine, Pinus radiata, and green ash, Fraxinus pensylvanica are two plants invasive here introduced from North America.

A good source of information on Argentine invasive plants has been Gekko, Grupo de Estudios en Conservacion y Manejo.

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Centaurea solstitialis, yellow star thistle

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Hedera helix, English ivy, under invasive tree species

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Populus alba, white poplar

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Cytisus monspessulanus, French broom

Dipsacus Costanera

Dipsacus fullonum, common teasel (in Buenos Aires Costanera Sur Reserve)

Arundo donax

Arundo donax, giant reed (Buenos Aires, Costanera Sur Reserve)

 

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Invasive Plants and Biodiversity

Finally a study specifically addresses why some invasive plant studies show a decrease in biodiversity, and some show an increase or no change in biodiversity.  Not surprisingly, scale matters.  If you walk through a forest heavily invaded by non-native shrubs, you often find no plants growing under the shrubs.  But in the context of the landscape, you can still find the native species that used to grow in that forest.  On the small scale, invasive plants decrease biodiversity, but at larger scales, biodiversity often remains unchanged.  The authors point out that some ecosystem services that occur at smaller scales such as water filtration, are still likely to be affected by plant invasions.

K. I. Powell, J. M. Chase, T. M. Knight. 2013. Invasive Plants Have Scale-Dependent Effects on Diversity by Altering Species-Area Relationships. Science: 339 (6117): 316  DOI:10.1126/science.1226817

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Maryland’s new invasive plant regulations

Maryland has posted its regulations for assessing plant invasiveness.  These regulations will be used to develop a two tier list of invasive plants.  Tier 1 plants will be banned from sale, and Tier 2 plants will be labeled as invasive.  Find out more at http://ipetrus.blogspot.com/2012/11/regulation-of-invasive-plants-in.html

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Is Perilla frutescens spreading?

In the mid-Atlantic people seem to be noticing large patches of beefsteak plant, Perilla frutescens, this year. This mint plant is used as an Asian herb and ornamental with its ruffly purplish leaves.  I’ve seen it growing in sun to part sun along field edges and woodland paths.  It grows very densely, but no studies on its potential impacts are available yet.  John Peter Thompson has compiled a great bibliography on this plant for those of you interested in investigating it further, http://ipetrus.blogspot.com/2012/10/invasive-wild-sesame-perilla-mint-beef.html.

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Plants evolve greater phenotypic plasticity in invaded range

I’ve been interested in the expression of phenotypic plasticity by invasive plants since studying Melaleuca quinquenervia population genetics for my dissertation.  Often invasive plants seem to be able to grow in a wider range of habitats and perform better in their invaded range than in their native range.  The ability to change traits depending on environmental conditions, phenotypic plasticity, could help explain this success.  A study by Sonia Sultan et al. (2012) shows that Polygonum cespitosum, Oriental lady’s thumb, has evolved to have greater phenotypic plasticity and higher reproductive output in response to the more open, sunny conditions in its invaded range in the western United States.  They tracked populations over 11 years to observe differences among populations in their evolutionary trajectories.  It’s not easy to keep a study going for so long and it looks like it has yielded some really interesting results!

Sonia E. Sultan, Tim Horgan-Kobelski, Lauren M. Nichols, Charlotte E. Riggs & Ryan K. Waples. 2012. A resurrection study reveals rapid adaptive evolution within populations of an invasive plant. Evolutionary Applications, online 09 Sept. DOI: 10.1111/j.1752-4571.2012.00287.x

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Controlling Para grass without herbicides

Para grass, Urochloa mutica, grows in the southeastern United States in fields, marshes and swamps.  It spreads by runners to form dense stands. It can be controlled with herbicides, but managers often wish to avoid using herbicides in sensitive wetland areas.  Research on non-chemical control methods in Florida show that Para grass can be controlled using a combination of flame weeding or mowing and flooding.   Particularly in areas where water levels can be manipulated, burning or cutting plants prior to flooding proved can be an effective means of killing Para grass.

Sushila Chaudhari, Brent A. Sellers, Stephen V. Rockwood, Jason A. Ferrell, Gregory E. MacDonald, Kevin E. Kenworthy. 2012. Nonchemical Methods for Paragrass (Urochloa mutica) Control. Invasive Plant Science and Management: January-March 2012, Vol. 5, No. 1, pp. 20-26.

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