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36<br />

ANA LUISA ANAYA<br />

phytochelatines, various pest-control effects, and poisoning. Complex biological-biochemical<br />

interactions among roots, rhizosphere organisms, and the rhizosphere solution<br />

determine the overall biogeochemical processes in the wetland rhizosphere and<br />

in the vegetated wetlands. In order to comprehend how wetlands really function and<br />

to understand these interactions it is necessary to implement long-term collaborative<br />

research (Neori et al., 2000). We can find promising allelochemicals and useful interactions<br />

in the rich biodiversity of these particular ecoystems, but without doubt, in all<br />

type of ecosystems.<br />

3. CHEMISTRY OF ALLELOPATHY<br />

As we know, plant and microbial compounds are continuously analyzed as potential<br />

sources of herbicides, pesticides, and pharmaceuticals because they provide a diversity<br />

of carbon skeletons and there has been success in that a number of compounds<br />

have shown biological activity. The same bioassays and techniques to reveal mechanisms<br />

of action apply to the search for herbicides as in the study of allelopathy. Certainly<br />

there is overlap in goals and compounds studied, but there also is a difference<br />

in that the starting point in the ‘herbicide search’ might be any natural product, as<br />

opposed to one identified with allelopathy. Most inhibitors of plants are secondary<br />

compounds that have their origin in either the shikimate or acetate pathways, or they<br />

are compounds having skeletal components from both of these origins (Einhellig,<br />

2002). Waller et al. (1999) listed over twenty classes of secondary metabolites that are<br />

produced, stored, and released into the rhizosphere where they have biological activity<br />

as well as undergo microbial transformation and degradation. Einhellig (2002)<br />

concluded that the 14 categories suggested by Rice (1984) are sufficiently broad to<br />

still retain validity: water-soluble organic acids, straight-chain alcohols, aliphatic<br />

aldehydes and ketones, unsatured lactones, long-chain fatty acids and polyacetylenes,<br />

naphthoquinones, anthraquinones and complex quinones, gallic acids and<br />

polyphloroglucinols, cinnamic acids, coumarins, flavonoids, tannins, terpenoids, and<br />

steroids, amino acids, and purines and nucleosides.<br />

In this chapter some of the main compounds and studies associated with allelopathy<br />

will be mentioned.<br />

Terpenoids and phenolics are the most common compounds involved in allelopathic<br />

interactions. Terpenoids are the largest group of plant chemicals (15,000-20,000)<br />

with a common biosynthethic origin. The terpenoid pathway generates great structural<br />

diversity and complexity of compounds, thus generating enormous potential for<br />

mediating ecological interactions (Duke, 1991; Langenheim, 1994). Terpenoids may<br />

produce effects on seeds and soil microbiota through volatilization, leaching from<br />

plants, or decomposition of plant debris. These interactions can significantly affect<br />

community and ecosystem properties, although studies of plant-plant chemical interactions<br />

have often been controversial because of difficulty in unambiguously demonstrating<br />

interference by chemical inhibition rather than through resource competition<br />

or other mechanisms (Harper, 1977).

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