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vital macr<strong>on</strong>utrients such as N, P, K, Ca, Mg and micr<strong>on</strong>utrients such as Fe, Zn, Cu, Mn and<br />

Mo.<br />

Das and Patra (1979) observed that vermicompost c<strong>on</strong>ta<strong>in</strong>ed 0.47 per cent N. Kale et<br />

al. (1992) op<strong>in</strong>ed that vermicompost was like any other <str<strong>on</strong>g>organic</str<strong>on</strong>g> manure depend<strong>in</strong>g <strong>on</strong> the<br />

nature <str<strong>on</strong>g>of</str<strong>on</strong>g> wastes used as feed for worms. The nitrogen c<strong>on</strong>tent varied between 0.5 to 1.2 per<br />

cent. Similar variati<strong>on</strong> <strong>in</strong> respect <str<strong>on</strong>g>of</str<strong>on</strong>g> phosphorus and potassium c<strong>on</strong>tent have also been<br />

reported. The chemical analysis <str<strong>on</strong>g>of</str<strong>on</strong>g> vermicompost prepared at University <str<strong>on</strong>g>of</str<strong>on</strong>g> Agricultural<br />

Sciences, Dharwad revealed that it c<strong>on</strong>ta<strong>in</strong>ed 0.8, 1.1 and 0.5 per cent <str<strong>on</strong>g>of</str<strong>on</strong>g> N, P2O5 and K2O,<br />

respectively (Giraddi, 1993). In comparis<strong>on</strong> to FYM, vermicompost c<strong>on</strong>ta<strong>in</strong>ed nearly two<br />

times more N, five times more phosphorus and almost equal amount <str<strong>on</strong>g>of</str<strong>on</strong>g> potassium.<br />

2.1.3 Crop residue<br />

The recycl<strong>in</strong>g <str<strong>on</strong>g>of</str<strong>on</strong>g> various forms <str<strong>on</strong>g>of</str<strong>on</strong>g> residue has the advantage <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>vert<strong>in</strong>g surplus<br />

farm waste <strong>in</strong>to useful product for meet<strong>in</strong>g the nutrient requirement <str<strong>on</strong>g>of</str<strong>on</strong>g> crops besides<br />

ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g the <strong>soil</strong> health and improv<strong>in</strong>g the overall ecological balances.<br />

Crop residue management c<strong>on</strong>siders the use <str<strong>on</strong>g>of</str<strong>on</strong>g> residue from previous crop as an<br />

<strong>in</strong>put resource and with appropriate management <str<strong>on</strong>g>practices</str<strong>on</strong>g> (Schertz and Bushnell, 1993).<br />

On an average, cereal straw and residue c<strong>on</strong>ta<strong>in</strong>ed about 0.5:0.6:1.5 per cent <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

N:P2O5:K2O, respectively. The nutrient potential <str<strong>on</strong>g>of</str<strong>on</strong>g> straw (236 milli<strong>on</strong> t<strong>on</strong>nes) from five crops<br />

viz., rice, wheat, sorghum, pearl millet and maize was 1.31, 1.41 and 3.54 milli<strong>on</strong> t<strong>on</strong>nes <str<strong>on</strong>g>of</str<strong>on</strong>g> N,<br />

P2O5 and K2O, respectively (Gaur et al., 1995). Burn<strong>in</strong>g <str<strong>on</strong>g>of</str<strong>on</strong>g> crop residues <strong>in</strong>creased the<br />

potential loss <str<strong>on</strong>g>of</str<strong>on</strong>g> N, C, S and possibly some other nutrients due to volatilizati<strong>on</strong> and resulted <strong>in</strong><br />

unfavourable <strong>soil</strong> c<strong>on</strong>diti<strong>on</strong> (Biederbeck et al., 1980). Hence, its management ensured the<br />

recycl<strong>in</strong>g <str<strong>on</strong>g>of</str<strong>on</strong>g> major porti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> nutrients and exerted c<strong>on</strong>siderable <strong>in</strong>fluence <strong>on</strong> crop<br />

performance, primarily through their <str<strong>on</strong>g>impact</str<strong>on</strong>g> <strong>on</strong> <strong>properties</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>soil</strong>.<br />

2.1.4 Green manures<br />

Use <str<strong>on</strong>g>of</str<strong>on</strong>g> legumes as green manures c<strong>on</strong>tribute to the fertility <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>soil</strong> by way <str<strong>on</strong>g>of</str<strong>on</strong>g> additi<strong>on</strong><br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> roots, nodules, leaves, tops etc. Green manur<strong>in</strong>g is a possibility and a practice <strong>in</strong> subtropical<br />

regi<strong>on</strong>s, where w<strong>in</strong>ter fallow is comm<strong>on</strong>, which found to substitute nearly 50 to 56 kg<br />

N per ha (Millhott<strong>on</strong> and Melville, 1991 and Beaver et al., 1993) apart from <strong>in</strong>creas<strong>in</strong>g <strong>soil</strong><br />

<str<strong>on</strong>g>organic</str<strong>on</strong>g> matter. It is felt that legumes as w<strong>in</strong>ter cover are envir<strong>on</strong>mentally desirable which<br />

supply adequate N for cott<strong>on</strong> producti<strong>on</strong>. In situ green manur<strong>in</strong>g, as legume <strong>in</strong>tercrops is<br />

possible under all c<strong>on</strong>diti<strong>on</strong>s and results are also encourag<strong>in</strong>g. Intercropp<strong>in</strong>g <str<strong>on</strong>g>of</str<strong>on</strong>g> legumes viz.,<br />

sunnhemp, horsegram, cowpea for <strong>in</strong>corporati<strong>on</strong> as green manure at Coimbatore helped to<br />

reduce N requirement <str<strong>on</strong>g>of</str<strong>on</strong>g> cott<strong>on</strong> to an extent <str<strong>on</strong>g>of</str<strong>on</strong>g> 35 to 50 per cent (An<strong>on</strong>., 1991).<br />

Cowpea as a green manure provided about 800 to 850 kg dry matter with 2.3 to 2.5<br />

per cent N and 0.24 to 0.26 per cent P at 40 DAS. This material was easily decomposable<br />

and c<strong>on</strong>tributed 10 to 12 kg N per ha (Tarhalkar et al., 1996).<br />

Dha<strong>in</strong>cha gave 3500 to 4000 kg <str<strong>on</strong>g>of</str<strong>on</strong>g> dry matter per ha with 2.5 to 2.6 per cent <str<strong>on</strong>g>of</str<strong>on</strong>g> N,<br />

0.20 to 0.22 per cent P2O5 and 1.9 to 2.0 per cent K2O. Its fast decompos<strong>in</strong>g leaves provide N<br />

dur<strong>in</strong>g the crucial boll development period <str<strong>on</strong>g>of</str<strong>on</strong>g> cott<strong>on</strong>, while the stalk acts as temporary <str<strong>on</strong>g>organic</str<strong>on</strong>g><br />

mulch (Tarhalkar et al., 1996).<br />

The sunnhemp used by Badanur et al. (1990) for a field trial c<strong>on</strong>ta<strong>in</strong>ed 2.30, 0.51 and<br />

0.79 per cent <str<strong>on</strong>g>of</str<strong>on</strong>g> N, P2O5 and K2O, respectively.<br />

2.2 EFFECT OF ORGANIC MANURES ON SOIL PHYSICAL<br />

PROPERTIES<br />

2.2.1 Bulk density<br />

Srikanth et al. (2000) found a significant decrease <strong>in</strong> bulk density (1.27 – 1.18 g/cc) <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<strong>soil</strong> after harvest <str<strong>on</strong>g>of</str<strong>on</strong>g> sec<strong>on</strong>d crop <strong>in</strong> the <strong>soil</strong> amended with compost compared to the <strong>in</strong><str<strong>on</strong>g>organic</str<strong>on</strong>g><br />

fertilizers applied <strong>soil</strong>.

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