The suppression of growth of one plant species by another due to the release of toxic substances (Webster 1983).
--Insert overview photo here--
Chemical ecologists have defined allelopathy
more broadly as any direct or indirect, harmful or beneficial effect of one
plant on another through the production of chemical compounds that escape in
the environment (Rice, 1984). Others
have narrowed this definition slightly by limiting the scope of allelopathic compounds to those that are secondary metabolites (Malik and Inderjit
2002).
Importance of allelopathy
Allelopathic interactions are undoubtably an important factor in determining some species distribution and abundance within plant communities. Allelopathic interactions are also thought to be an important factor in the success of many invasive plants . For a detailed
example, see Spotted Knapweed .
Mechanisms of action
There are hundreds of secondary metabolites, and many are
known to be phytotoxic (Einhellig
2002). Allelopathic
effects of these compounds are often observed early in the life cycle, i.e. via
inhibition of seedling germination and/or growth. They exhibit a wide range of mechanisms of action,
from affects on DNA (alkaloids), to photosynthetic and mitochondrial function (quinones), to phytohormone
activity, ion uptake and water balance (phenolics). Interpretations of mechanisms of action are
complicated by the fact that many individual compounds have multiple phytotoxic effects (Einhellig
2002).
Demonstrating an allelopathy in nature
In practice, the vast majority of allelopathy
research attempts to focus on direct negative plant-plant interactions via allelochemicals. One
of the greatest challenges of this approach is showing that the effect is
direct, since allelochemicals can have indirect
effects on plant species through interaction with biotic (e.g. mycorrhizae), and/or abiotic
soil factors (e.g. nutrients) respectively (Inderjit
2002). In terrestrial systems, the soil
plays an important role as the matrix through which potential allelochemicals pass.
Both abiotic and microbial decomposition will
have significant effects on the concentration of allelochemicals
reaching other plants.
It is also quite difficult to separate the effects of allelopathy from those due to resource competition
(i.e. for space, light, water, nutrients or CO2). Controlled greenhouse studies that allow for
examination of a single independently varying factor may be of little interest
since they never vary independently in nature.
Thus proving that allelopathy is
occurring is quite difficult. Willis (1985)
required that six criteria be met, and even when maximally relaxed to three, proving
its existence is rarely accomplished (if ever, see Blum 1999).
- pattern of inhibition of one species by another
- putative aggressor must produce a toxin
- known mode of release of this toxin
- toxin transport or accumulation in the environment
- afflicted plant have means of uptake of toxin
- observed pattern of inhibition cannot be solely explained by physical competition or other biotic factors
Role of plant stress
Allelopathy also interacts with
plant stress, because stressed source plants often release a greater array and
concentration of allelochemicals, and stressed target
plants may be more susceptible to allelochemicals (Reigosa et al. 2002).
Measurement of the effects of allelochemicals
along stressor gradients should help to elucidate the relationship between allelopathy and stress.
Examples of allelopathy
--Insert detailed Salvia photo here--
The most throuroughly studied studied cases of allelopathic
interaction are in desert shrubs and trees.
Salvia leucophylla
was one of the best early examples (Muller 66), but even its strong evidence
for allelopathy may be of limited importance as
suggested by caging experiments (Harper 1977).
Others argue that allelopathy plays an
important role even in the face of this evidence (ref).
Black Walnut (Jose)
Eucalyptus
(Willis)
See also
References
- Webster 1983. Websters ninth new collegiate dictionary. Merriam-Webster, Inc., Springfield, Mass.
- Rice EL 1974. Allelopathy. Academic Press, New York.
- Mallik AU, Inderjit. 2002. Problems and prospects in the study of plant allelochemicals: a brief introduction. In: Chemical Ecology of Plants: Allelopathy in aquatic and terrestrial ecosystems, Mallik, AU and Inderjit, Eds. Birkhauser Verlag, Basel, Switzerland.
- Einhellig, FA. 2002. The physiology of allelochemical action: clues and views. In: Allelopathy, from Molecules to Ecosystems, Reigosa, MJ and N. Pedrol, Eds. Science Publishers, Enfield, New Hampshire.
- Inderjit. 2002. Multifaceted approach to study allelochemicals in an ecosystem. In: Allelopathy, from Molecules to Ecosystems, Reigosa, MJ and N. Pedrol, Eds. Science Publishers, Enfield, New Hampshire.
- Willis RJ. 1985. The historical basis of the concept of allelopathy. Journal of the history of Biology, 18: 71-102.
- Blum U, Shafer SR, Lehman ME. 1999. Evidence for inhibitory allelopathic interactions involving phenolic acids in field soils: concepts vs. an experimental model. Critical Reviews in Plant Sciences, 18(5):673693.
- Reigosa MJ, Pedrol N, Sanchez-Moreiras AM, Gonzales L. 2002. Stress and allelopathy. In: Allelopathy, from Molecules to Ecosystems, Reigosa, MJ and N. Pedrol, Eds. Science Publishers, Enfield, New Hampshire.
- Muller CH. 1966. The role of chemical inhibition (allelopathy) in vegetational composition. Bulletin of the Torrey Botanical Club 93:332-351.
- Harper JL. 1977. Population biology of plants. pp. 374-81. Academic Press, London.
- Jose S. 2002. Black walnut allelopathy: current state of the science. In: Chemical Ecology of Plants: Allelopathy in aquatic and terrestrial ecosystems, Mallik, AU and Inderjit, Eds. Birkhauser Verlag, Basel, Switzerland.
- Willis RJ. 1999. Australian studies on allelopathy in Eucalyptus: a review. In: Principles and practices in plant ecology: Allelochemical interactions, Inderjit, Dakshini KMM and Foy CL, Eds. CRC Press, Boca Raton, FL.