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86<br />

Ramesh Chander Kuhad et al.<br />

cellular lignocellulolytic enzyme activity in the assessment of soil quality is<br />

established by the essential role of soil microbes in nutrient cycling within<br />

agricultural ecosystems (Christensen and Johnston 1997). During the microbial<br />

degradation and humification of <strong>plant</strong> residues, about 80 % of the residual<br />

carbon is released to the atmosphere as CO 2 (Omar 1994). The amendment<br />

of infertile or saline soils with <strong>plant</strong> residues and their subsequent<br />

degradation by cellulolytic soil microflora with a concomitant increase in CO 2<br />

could increase soil aeration, improve its structure and also increase soil fertility.<br />

The activities of cellulolytic microbes affect the availability of energy and<br />

specific nutrients to a group of organisms deficient in hydrolytic enzyme<br />

activities (Jensen and Nybroe 1999).<br />

Soils managed with organic inputs generally have larger and more active<br />

microbial populations than those managed with mineral fertilizers (Badr El-<br />

Din et al. 2000). Reincorporation of organic matter into the soil improves soil<br />

fertility, enhances microbial growth and buffers the soil environment from<br />

sudden changes. There are many types of agroindustrial organic refuse which<br />

can be transformed and applied to soil as crop amendments, such as compost,<br />

thus reducing the need for chemical fertilizers. During the composting<br />

process, the organic substrate present in the agricultural wastes is mainly<br />

transformed oxidatively into a stabilized organic matter. The slow transformation<br />

of lignocellulosic material results in the formation of humic substances.<br />

Several researchers have established a positive correlation between<br />

the amount of humic substances and promotion of <strong>plant</strong> growth. Application<br />

of different combinations of coir with peat and vermiculate significantly<br />

increased the growth of tomato trans<strong>plant</strong>s with respect to root dry weight,<br />

stem diameter and leaf area (Arenas et al. 2002).<br />

Straw incorporation could also be beneficial in enhancing symbiotic nitrogen<br />

fixation and crop growth (Abd-Alla and Omar 1998). In nonsymbiotic<br />

nitrogen fixation studies in the laboratory and in the field, a significant<br />

increase in nitrogenase activity associated with the breakdown of straw after<br />

inoculation with various combinations of cellulolytic fungi and bacteria has<br />

been reported (Halsall and Gibson 1991; Chapman et al. 1992). Application of<br />

wheat straw with cellulolytic fungi, Trichoderma harzianum significantly<br />

enhanced growth, nodulation, nodule efficiency and increased the concentration<br />

of Ca, Mg and K in the shoots and roots of fenugreek <strong>plant</strong>s grown in<br />

saline soil (Abd-Alla and Omar 1998). The increase in dry matter production<br />

and nitrogen content was due to improved N 2 fixation reflected by enhanced<br />

formation and growth of nodules as well as nitrogenase activity.<br />

Inoculation of straw with lignocellulolytic organisms offers potential for<br />

manipulating and improving the composting of cellulosic waste (Verstraete<br />

and Top 1999; Hart et al. 2002). Composts produced using this method provide<br />

a more sustainable approach to agriculture, enabling subsistence farmers<br />

to utilize their agricultural waste products as a means to improve soil quality.<br />

Saprophytic lignin-decomposing basidiomycetes isolated from <strong>plant</strong> litter

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