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Joint International Conference on Long-term Experiments ...

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some pathogen agents, a chemical and thermic disinfecti<strong>on</strong> is necessary, with hot vapors<br />

(150 o C), at 90 o -95 o C, for 6-7 hours, at 30cm deep.<br />

The manure doses are 80-100t/ha <strong>on</strong>ce a year in greenhouses with older cultures and<br />

twice a year (cycle I and cycle II) in new greenhouses (Davidescu D. and Velicica<br />

Davidescu, 1992; Ciofu et al, 2003).<br />

Composted birds manure can be also applied with 3 m<strong>on</strong>ths in advance in doses of 15-<br />

25t/ha and forestry composts from resins bark or beech (Rusu, 1993).<br />

In greenhouse c<strong>on</strong>diti<strong>on</strong>s, the mobility of nutritive elements from the organic manure is<br />

more intense than at the same culture in the field, thus c<strong>on</strong>sidering that for each 100t manure<br />

in a vegetati<strong>on</strong> cycle in the soil it is liberated in average: 250-300 kg N, 120-170 kg P2O5<br />

and 350-450 kg K2O (after Davidescu D., 1992, cited by Avarvarei, 1997).<br />

The technological steps for optimizing the c<strong>on</strong>tent of organic matter (MO) is a<br />

compulsory request for this technology, so that every interpretati<strong>on</strong> and practical measure<br />

takes into account this value of the organic comp<strong>on</strong>ent. An optimized agrochemical support<br />

solves the nutriti<strong>on</strong> effects and prevents or diminishes some disturbing factors (salinitysalinizati<strong>on</strong>,<br />

acidity-acidificati<strong>on</strong>, toxicity of other i<strong>on</strong>s, polluting effects) (Rusu, 1968,<br />

1988).<br />

2./ The agrochemical optimizati<strong>on</strong> of the reacti<strong>on</strong> state and of the c<strong>on</strong>tent of soluble<br />

salts in the soil from the greenhouse at tomato culture<br />

As regards the optimizati<strong>on</strong> of the c<strong>on</strong>tent of soil in nutritive elements, the c<strong>on</strong>centrati<strong>on</strong>s of<br />

the nutritive i<strong>on</strong>s have to be guided towards the levels of optimum sufficiency in soil, after<br />

fertilizati<strong>on</strong>s.<br />

The greenhouse soils are frequently pr<strong>on</strong>e to salinizati<strong>on</strong> and alkalizati<strong>on</strong>, following<br />

the accumulati<strong>on</strong> of soluble salts obtained from the fertilizati<strong>on</strong> with organic and chemical<br />

manure, irrigati<strong>on</strong> water, water from the phreatic layer and the process of chemical<br />

alterati<strong>on</strong> of the soil mineral fracti<strong>on</strong>.<br />

The soil disinfecti<strong>on</strong> using vapors in greenhouses has the effect of increasing<br />

salinizati<strong>on</strong> due to the accelerati<strong>on</strong> of the transforming process of the amm<strong>on</strong>iac azoth<br />

(NH +<br />

4 ), which inhibits the activity of nitrificati<strong>on</strong> bacteria. These two processes lead to a<br />

temporary accumulati<strong>on</strong> of NO2 (Davidescu D. and Velicica Davidescu, 1992).<br />

Heavy irrigati<strong>on</strong> water, as well as the superficial phreatic layer, c<strong>on</strong>stitutes a source of<br />

enriching the surface soil layer with mineral salts (bicarb<strong>on</strong>ate, carb<strong>on</strong>ate, chlor, sodium<br />

sulphate, magnesium).<br />

Sweet irrigati<strong>on</strong> waters (rain water) diminish the salinizati<strong>on</strong> effect with the diluti<strong>on</strong> of<br />

the soluble salts.<br />

For this reas<strong>on</strong>, shortly after being in use, the reacti<strong>on</strong> of the greenhouse soil tends to<br />

become neuter-alkaline or even alkaline, fact that has negative influences <strong>on</strong> the cultures<br />

development.<br />

The applicati<strong>on</strong> of the amendments is imposed when the value of pH exceeds 8.5.<br />

297

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