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64<br />

ANA LUISA ANAYA<br />

of two fungal antagonists of soil-borne diseases was evaluated after their inoculation<br />

in potting soil and in compost produced from different types of organic waste and at<br />

different maturation stages. The fungal antagonists Verticillium biguttatum, a<br />

mycoparasite of Rhizoctonia solani, and a non-pathogenic isolate of Fusarium<br />

oxysporum antagonistic to Fusarium wilt, survived at high levels (10 3 -10 5 CFU g -1 )<br />

after 3 months incubation at room temperature in green waste compost and in potting<br />

soil. Their populations faded-out in the organic household waste compost, especially<br />

in the matured product. In bioassays with R. solani on sugar beet and potato, the<br />

disease suppressiveness of compost increased or was similar after enrichment with V.<br />

biguttatum. The largest effects, however, were present in potting soil, which was very<br />

conducive for the disease as well as the antagonist. Similar results were found in the<br />

bioassay with F. oxysporum in carnation where enrichment with the antagonistic F.<br />

oxysporum had a positive or neutral effect. Postma et al. (2003) foresee great potential<br />

for the application of antagonists in agriculture and horticulture through enrichment<br />

of compost or potting soil with antagonists or other beneficial micro-organisms.<br />

All soils are suppressive to phytonematodes to some degree. The degree of<br />

suppressiveness to them or other soilborne pathogens in a soil can be enhanced not<br />

only by infesting soil with selected microorganisms, but by the use of appropriate<br />

cropping systems and the application to soil of specific organic amendments or chemical<br />

compounds. Conducive cropping systems such as monoculture can reduce soil<br />

suppressiveness to the point where the soil is not resistant to plant parasitic nematodes<br />

(Wang et al., 2002).<br />

Inorganic fertilizers containing ammoniacal nitrogen or formulations releasing<br />

this form of N in the soil are most effective for suppressing nematode populations.<br />

Anhydrous ammonia has been shown to reduce soil populations of Tylenchorhynchus<br />

claytoni, Helicotylenchus dihystera, and Heterodera glycines. The rates required to<br />

obtain significant suppression of nematode populations are generally in excess of 150<br />

kg N/ha. Urea also suppresses several nematode species, including Meloidogyne spp.,<br />

when applied at rates above 300 kg N/ha. Additional available carbon must be provided<br />

with urea to permit soil microorganisms to metabolize excess N and avoid phytotoxic<br />

effects. There is a direct relation between the amount of “protein” N in organic<br />

amendments and their effectiveness as nematode population suppressants. Most<br />

nematicidal amendments are oil cakes, or animal excrements containing 2-7% (w/w)<br />

N; these materials are effective at rates of 4-10 t/ha. Organic soil amendments<br />

containing mucopolysaccharides (e.g., mycelial wastes, chitinous matter) are also<br />

effective nematode suppressants (Rodriguez-Kábana, 1986).<br />

Vargas-Ayala and Rodriguez-Kábana (2001) established a field microplot trial to<br />

evaluate nematode population dynamics in a rotation program utilizing nematodesuppressive<br />

and non-suppressive legumes, and nematode-host and nonhost grass<br />

species. The rotation treatments consisted of velvetbean (Mucuna deeringiana) or<br />

cowpea (Vigna unguiculata) during the first year, followed in winter by oat (Avena<br />

sativa), wheat (Triticum aestivum), rye (Secale cereale), rye grass (Lolium sp.), clover<br />

(Trifolium sp.), hairy vetch (Vicia villosa), lupine (Lupinus sp.) or fallow. Rotation in

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