Decomposition
and Invasive Species
Terrestial ecosystems are changed by
an invasive species's litter decomposition rate.
Studies have shown than on the
average, invasive species have 117% higher decomposition rate in comparison to
native plants (Ehrenfeld 2010).
Generally, more litter mass is associated with higher input of elements
to the soil.
Invasive plant litter decomposes more
quickly because their litter is generally of higher quality with lower carbon:nitrogen
and lignin:nitrogen ratios. Whether due
to increased litter mass or increased decomposition rate, the invasive plants
frequently have higher net flux of carbon to the soil (Ehrenfeld 2010).
There have been several studies that
have shown that invasive plants have somewhat faster decomposing litter and
nitrogen loss; studies have repeatedly shown faster decomposition and nitrogen
cycling for both native and invasive species when they are grown together at a
site growing invasive species. The
implication is that in addition to the nature of the litter, there are soil
changes caused by the invasive plants that are not well-understood, but seem to
favor recycling of all species. For
example, one study in Hawaii compared the invasive nitrogen-fixing tree, Falcataria molucanna, to the native tree
that did not fix N₂, Metrosideros
polymorpha, and found that following invasion by a Falcataria stand, the litter decomposition rates of both trees
increased six times over what it had been in native soil (Hughes 2006).
F. molucanna M. polymorpha
Garlic mustard (Alliaria
petiolata) is an invasive plant that is able to
suppress competition by secretion of numerous secondary compounds, such as
glucosinolates, that suppress spore formation by arbuscular mycorrhizal fungi,
a common symbiotic fungus of native plants (Wolf, Klironomos 2005). Surprisingly, despite the secondary
antimicrobial compounds, garlic mustard green rosette leaves consistently
accelerated the decomposition of native tree litter and nitrogen immobilization,
while it increased soil N and P availability, soil pH, and base cation
availability. Plant tissue volatiles and
root exudates had little impact on soil properties or fungi other than AMF’s
(Rodgers et al 2007).
Alliaria petiolata
While you
might think the larger biomass would lead to higher litterfall mass, this
situation does not always occur because of other factors, such as relative
carbon allocation to leaves and decomposition rate. Florida’s invasive tree, Melaleuca, has monoterpene-rich leaves that decompose slowly. These plant chemicals probably served a
protective role against herbivores or disease in their native countries. The oil content of trees growing in Florida
is less than that found in tree of Australia (Ehrenfeld 2003).
Melaleuca quinquenervia
The preceding examples show that invasive species' litter decomposition rates change terrestrial ecosystems.
References
1. Ehrenfeld, Joan G. (2010).
Ecosystem Consequences of Biological Invasions. Annual Review of Ecology, Evolution, and Systematics. 41:59-80.
2. Ehrenfeld, Joan G. (2003). Effects
of Exotic Plant Invasions on Soil Nutrient Cycling Processes. Ecosystems. 6:503-523.
3. Hughes, R. Flint, Uowolo, Amanda.
Impacts of Falcataria molucanna
Invasion on Decomposition in Hawaiian Lowland Wet Forests: The Importance of
Stand-level Controls. Ecosystems.
Vol. 9:977-991.
4. Rodgers, Vikki L., et al. (2008).
The Invasive species Alliaria petiolata
(garlic mustard) increases soil nutrient availability in northern
hardwood-conifer forests.
Oecologia. 157:459-471.
5. Wolfe, Benjamin E. and John N.
Klironomos. (2005). Breaking New Ground: Soil Communities and Exotic Plant
Invasion. BioScience. Vol. 53 No.
6:477-487.
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