human disturbance

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Summer of Weeds: Pineapple Weed

“The spread of the fruitily perfumed pineapple weed, which arrived in Britain from Oregon in 1871, exactly tracked the adoption of the treaded motor tyre, to which its ribbed seeds clung as if they were the soles of small climbing boots.” – Richard Mabey, Weeds: In Defense of Nature’s Most Unloved Plants

Can a plant that is native to North America be considered a weed in North America? Sure. If it is acting “weedy” according to whatever definition we decide to assign to the word, then why not? Can “weeds” from North America invade Europe the same way that so many “weeds” from there have invaded here? Of course! Pineapple weed is just one such example.

Native to western North America and northeastern Asia, this diminutive but tough annual plant in the aster family can now be found around the globe. Matricaria discoidea gets its common name from the distinctive fruity scent it gives off when its leaves and flowers are crushed. Its scent is not deceptive, as it is yet another edible weed (see Eat the Weeds). Teas made from its leaves have historically been used to treat upset stomachs, colds, fevers, and other ailments.

pineapple weed (Matricaria discoidea)

Pineapple weed reaches as few as a couple centimeters to a little over a foot tall. Its leaves are finely divided and fern-like in appearance. Its flower heads are cone or egg-shaped, yellow-green, and cupped in light-colored, papery bracts. The flower heads lack ray florets and are composed purely of tightly packed disc florets. The fruits (i.e. seeds) are tiny, ribbed achenes that lack a pappus.

Compacted soils are no match for pineapple weed. It is often seen growing in hard-packed roadways and through small cracks in pavement, and it is undeterred by regular trampling. It is a master of disturbed sites and is commonly found in home gardens and agriculture fields. It flowers throughout the summer and is often confused with mayweed (Anthemis cotula); the telltale difference is that mayweed gives off a foul odor when crushed.

Meriwether Lewis collected pineapple weed along the Clearwater River during the Lewis and Clark Expedition. In their book, Lewis and Clark’s Green World, Scott Earle and James Reveal write, “There is nothing in the expedition’s journals about the plant, but it would seem that there was little reason for Lewis to collect the two specimens that he brought back other than for its ‘agreeable sweet scent.’ It is otherwise an unremarkable, rayless member of the aster family.” The authors continue their mild ribbing with this statement: “The pineapple weed deserves its appellation, for it is a common weed – although a relatively innocuous one – that grows in disturbed places, along roadsides, and as an unwanted garden guest.”

pineapple weed (Matricaria discoidea) – photo credit: wikimedia commons

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Quote of the Week:

From Weeds and What They Tell (ed. 1970) by Ehrenfried Pfeiffer

“Weeds are WEEDS only from our human egotistical point of view, because they grow where we do not want them. In Nature, however, they play an important and interesting role. They resist conditions which cultivated plants cannot resist, such as drought, acidity of soil, lack of humus, mineral deficiencies, as well as a one-sidedness of minerals, etc. They are witness of [humanity’s] failure to master the soil, and they grow abundantly wherever [humans] have ‘missed the train’ – they only indicate our errors and Nature’s corrections. Weeds want to tell a story – they are natures way of teaching [us] – and their story is interesting. If we would only listen to it we could apprehend a great deal of the finer forces through which Nature helps and heals and balances and, sometimes, also has fun with us.”

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Summer of Weeds: Henbit and Purple Deadnettle

There are weeds for every season. Now that we are heading into the hot days of summer, spring weeds (if they haven’t already) are fading. There is a parallel between them and the spring wildflowers we love. They start early, greening up and flowering even before there are leaves on the trees. They exploit the sun made available before deciduous trees and shrubs can hog it all, and they take advantage of the moisture in the soil brought by winter snowfall and spring rain. They thrive in cool temperatures, and their flowers provide early pollen and nectar for emerging pollinators. One major difference between spring ephemeral weeds and spring ephemeral wildflowers is that, despite having similar strategies and providing similar services, the spring weeds aren’t from here; and so we look down on them.

Two common, annual, spring weeds that are easily recognizable – but often mistaken for one another – are henbit and purple deadnettle. Both are in the genus Lamium and the family Lamiaceae (the mint family) and both arrived from Europe. Looking closely at the leaves is the best way to tell these two apart. The upper leaves of henbit (Lamium amplexicaule) lack petioles and are round or oval with rounded teeth. The upper leaves of purple deadnettle (Lamium purpureum) are crowded around the stem, have short petioles, sharper teeth, and are more spade-shaped, coming to a point at the tip. The uppermost leaves of purple deadnettle are a distinct reddish-purple. Identify That Plant offers a great tutorial to help tell these and groundy ivy (another spring-occurring, annual weed in the mint family) apart.

henbit (Lamium amplexicaule)

Henbit prefers full sun and moist, rich soils. It can have either a prostrate or an erect growth habit. In urban environments it is commonly found in lawns, garden beds, and drainage ditches. It is common in agricultural crops and fallow fields as well. According to Weeds of North America, “henbit is poisonous to livestock, especially sheep, causing the animal to stagger;” it is also a host for aster yellows, tobacco etch, and tobacco mosaic viruses. Purple deadnettle inhabits similar sites, often forming a dense groundcover. While henbit and purple deadnettle are highly attractive to bees, they do not always require insect pollination and can self-pollinate instead. Each plant can produce dozens of seeds, and seeds remain viable in the soil for as long as 25 years.

Plants in the genus Lamium are commonly referred to as dead-nettles because they resemble stinging nettle (Urtica dioica) and other plants in the genus Urtica. Lamiums do not posses the stinging quality, and so they are “dead.”  The young leaves, shoots, and flowers of henbit and purple deadnettle are edible and can be eaten raw or cooked. Check out Eat the Weeds for more details.

Illustration of henbit (Lamium amplexicaule) from Selected Weeds of the United States (Agriculture Handbook No. 366) circa 1970

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purple deadnettle (Lamium purpureum)

Quote of the Week:

From Wild Urban Plants of the Northeast by Peter Del Tredici

From a utilitarian perspective, a weed is any plant that grows by itself in a place where people do not want it to grow. The term is a value judgment that humans apply to plants we do not like, not a biological characteristic. Calling a plant a weed gives us license to eradicate it. In a similar vein, calling a plant invasive allows us to blame it for ruining the environment when really it is humans who are actually to blame. From the biological perspective, weeds are plants that are adapted to disturbance in all its myriad forms, from bulldozers to acid rain. Their pervasiveness in the urban environment is simply a reflection of the continual disruption that characterizes this habitat. Weeds are the symptoms of environmental degradation, not its cause, and as such they are poised to become increasingly abundant within our lifetimes.

A patch of dead-nettle (Lamium sp.) – photo credit: Amy Trampush (Thank you, Amy!)

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When Alien Plants Invade – The Four Stages of Invasion, part two

In a review published in New Phytologist (2007), Kathleen Theoharides and Jeffrey Dukes examine four stages of invasion as they relate to alien (i.e. introduced or non-indigenous) plant species. In part one we discussed transport and colonization, in which species must survive being transported long distances and then take root and reach maturity in an unfamiliar location. Alien plant species don’t become invasive until they have reached the last two stages: establishment and landscape spread. Removal of the species upon reaching these stages is no easy task. Luckily, introduced species have a few barriers to overcome before this point.

An established population is one that is self-sustaining and expanding. Environmental conditions may be a limiting factor, as they were during colonization, but the main constraints at this stage are “biotic filters.” Theoharides and Dukes define these as “barriers to invasion created by the actions or presence of living organisms.” Through competition for various resources, as well as herbivory and disease, neighboring organisms affect the survival, growth, and reproduction of introduced plant species. Thus, “traits that enhance competitive performance, reduce niche overlap between [introduced species] and natives, or increase enemy resistance may be most important during establishment… Other advantageous traits include secondary chemical compounds that deter herbivores, ‘novel weapons’ such as root exudates that negatively impact other plants, fast growth, and high fecundity.”

Plants compete for light, moisture, and soil nutrients, as well as for pollinators and seed dispersers. Competition inhibits the establishment of invaders when neighboring plants consume available resources more efficiently. Introduced plants risk being outcompeted by plants that are of the same functional type (plants that are “morphologically, phenologically, and physiologically similar”). They also risk competition by a single dominant species (or group of similar species) or by “an assemblage of species with different traits.” As a general rule, plant communities with greater diversity are more resistant to invasion.

“In forests of the northeastern USA, Alliaria petiolata, an herbaceous mustard species, contains a type of phytotoxic glucosinolate that appears to disrupt the mutualism between arbuscular mycorrhizal fungi and hardwood canopy trees.” – – Theoharides and Dukes (2007) [photo credit: eol.org]

Two hypotheses postulate the success of some plant invaders in establishing themselves: the enemy release hypothesis and the evolution of increased competitive ability hypothesis. In the first hypothesis, plant species – having been removed from their native habitat – are freed from their natural enemies and are thus able to allocate more resources to growth and reproduction. The second hypothesis states that, in light of “reduced enemy pressure,” introduced species quickly evolve to allocate resources “from enemy defense to faster growth.” Escape from herbivory and diseases, however, is likely not the only factor in the success of invaders, and much still depends on the competitiveness of the plant and the availability of key resources.

After introduced plants become established, a lag phase generally occurs before landscape spread. This can be a result of a lack of genetic variation, a dearth of suitable habitat, unfavorable environmental conditions, or some combination of the three. New introductions may occur, and the population may continue to adapt and expand. Suitable habitat may be made available, and environmental conditions may shift. In time, landscape spread becomes a possibility.

Landscape spread occurs when multiple populations of a species are connected via long-distance dispersal. At this “metacommunity scale,” populations of an introduced plant species interact across a large area, with each population in a different stage of colonization and establishment. This means that transport, colonization, and establishment are all at play during the landscape spread stage.

“Abutilon theophrasti (velvetleaf) was originally introduced before 1700 in the USA. This species has only recently become an aggressive invader as a result of the evolution of different life-history strategies based on the nature of competition in its new environment.” — Theoharides and Dukes (2007) [photo credit: wikimedia commons]

Dispersal ability and habitat connectivity are key factors in determining the success of an introduced plant species during landscape spread. Long-distance dispersal can occur via wind, water, or animals. Species that depend on animals to spread their seeds rely on specific animals to be present. The seeds of Prunus serotina (black cherry), for example, are dispersed by birds. So, landscape spread is reliant on birds and “roosting trees” where the birds can perch and defacate the seeds. In many cases, “humans also play a large role in intraregional dispersal.”

Habitats vary across the landscape due to a combination of numerous geological and biological processes. The disturbance regime – “the frequency, spatial extent, severity, and intensity of killing events over time” – also helps determine landscape patterns. Natural disturbances, such as fire, weather, and natural disasters, are differentiated from disturbances caused by human activity. Large scale development and disturbance of natural areas by humans disrupts the natural disturbance regime and alters historical landscape patterns. As the authors write, “alterations of the disturbance regime that increase resource availability or change landscape patterns can promote non-indigenous plant species spread by creating favorable patches for colonization and establishment.”

Fragmented landscapes consisting of small patches of natural areas dispersed among large areas of human development are particularly prone to invasion by introduced plant species for many reasons, including increased influx of propagules and a high degree of edge effects (habitat edges have environmental conditions that are generally more prone to invasion than habitat interiors).

Habitat patches can be connected via corridors. It is through these corridors that dispersal can occur between populations in a metacommunity. Corridors connect populations of both introduced and native plant species. However, “native plants often require wide undisturbed corridors of intact habitat, while [introduced plant species] may disperse best through strips of human-disturbed habitat or ‘disturbance corridors.'” The environmental conditions in disturbance corridors and the presence of dispersal agents (including humans and domesticated animals) help facilitate the connectivity of populations of introduced plant species and promote the colonization and establishment of new populations.

In their abstract, Theoharides and Dukes write, “both research and management programs may benefit from employing multiscale and stage approaches to studying and controlling invasion.” With their conclusion they provide a list of potential management strategies for each stage, and they advise employing “natural filters in order to prevent invasion succees.” Examples include reducing habitat fragmentation and edge effects, promoting intact native communities, reducing human disturbances, promoting natural disturbance regimes, and minimizing disturbance corridors.

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