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34<br />

ANA LUISA ANAYA<br />

and accessibility to external inputs -seeds, crop cultivars, machinery, etc.) and socioeconomic<br />

constraints (market, tenure status, attitude towards entrepreneurial risk,<br />

etc.). The use of cover crops and organic amendments, via the promotion of diversity<br />

in insect, fungal, bacterial or mychorrhyzal communities, may alter antagonist or<br />

competitive effects to the benefit of crops and to the detriment of weeds. Once factors<br />

driving these effects are better understood, it might be possible to use this knowledge<br />

to improve organic weed management systems locally. It would also be helpful to find<br />

indicators of “functional biodiversity”, where weed species abundance is assessed on<br />

the role that they have in the agroecosystem (e.g. strong /weak competitors, promoters<br />

of the presence of beneficial arthropods, etc.). Management of allelopathy is another<br />

potential tool in the arsenal of the organic farmer (Barberi, 2002). In the United<br />

States, the rate of increase of organic growers was estimated at 12% in 2000. However,<br />

many producers are reluctant to undertake the organic transition because of<br />

uncertainty of how organic production will affect weed population dynamics and<br />

management. The organic transition has a profound impact on the agroecosystem.<br />

Changes in soil physical and chemical properties during the transition often impact<br />

indirectly insect, disease, and weed dynamics. Greater weed species richness is usually<br />

found in organic farms but total weed density and biomass are often smaller<br />

under the organic system compared with the conventional system. The improved weed<br />

suppression of organic agriculture is probably the result of combined effects of several<br />

factors including weed seed predation by soil microorganisms, seedling predation by<br />

phytophagus insects, and the physical and allelopathic effects of cover crops (Ngouajio<br />

and McGiffen, 2002).<br />

2. ALLELOPATHY<br />

Increasing attention has been given to the role and potential of allelopathy as a management<br />

strategy for crop protection against weeds and other pests. Incorporating<br />

allelopathy into natural and agricultural management systems may reduce the use of<br />

herbicides, fungicides, nematicides, and insecticides, cause less pollution and diminish<br />

autotoxicity hazards. There is a great demand for compounds with selective toxicity<br />

that can be readily degraded by either the plant or by the soil microorganisms.<br />

Plant, microorganisms, other soil organisms and insects can produce allelochemicals<br />

which provide new strategies for maintaining and increasing agricultural production<br />

in the future. Compounds with allelopathic activity may provide novel chemistry for<br />

the synthesis of herbicides, insecticides, nematicides, and fungicides that are not based<br />

on the persistent petroleum derived compounds which are such a public health concern<br />

(Waller and Chou, 1989; Waller, 1999).<br />

Several crops (some of which can be used as cover crops) have been proved to<br />

release allelopathic compounds in the soil (Jimenez-Osornio and Gliessman, 1987;<br />

Blum et al., 1997; Inderjit and Keating, 1999; Anaya, 1999), many of which have<br />

been chemically characterized (Pereda-Miranda et al., 1996; Inderjit, 1996; Seigler,<br />

1996; Waller et al., 1999). The idea of exploiting these compounds as natural herbicides<br />

is therefore very attractive (Putnam, 1988; Weston, 1996; Duke et al., 2000).

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