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Book of Extended summaries ISDA

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International Conference on Reimagining Rainfed Agro-ecosystems: Challenges & Opportunities<br />

during 22-24, December 2022 at ICAR-CRIDA, Hyderabad<br />

Methodology<br />

The field experiment on rRabi sorghum (cultivar M 35-1) under dryland conditions was laid out<br />

conducted at AICRP for Dryland Agriculture Research Station, Mulegaon Farm, Solapur during<br />

2005-06 to 2016-17 for twelve years. The experiment was laid out in split plot design containing<br />

nine treatment combinations replicated three times includes three main plot treatments viz: 1)<br />

Low tillage (LT) - sowing with seed drill and light harrowing after sowing – (SSLH) 2)<br />

Medium tillage (MT) - one harrowing + SSLH+ one hoeing 3) Conventional tillage (CT) -<br />

plough once in 3 year + one harrowing + ridges and furrows + one harrowing + SSDH + three<br />

hoeings and three sub-treatments viz: 1) Organics - 50 kg Nha -1 (50 % CR+50 % LL) CR–Crop<br />

residue, LL–Leucaena loppings - N1 2) Organics + chemical fertilizers - 25 kg N ha -1 through<br />

urea + 25 kg N ha -1 through organics (50 % CR + 50 % LL) - N2 3) Fertilizers (RDF) : 50 kg<br />

N + 25 Kg P2O5 ha -1 - N3.<br />

The average nitrogen content <strong>of</strong> crop residue and leucaena during 12 years are 0.48 % and 3.04<br />

% respectively. The N, P and K were applied through urea, single super phosphate and muriate<br />

<strong>of</strong> potash respectively. The data on crop yield, total N uptake, economics, moisture use<br />

efficiency (MUE) <strong>of</strong> grain were recorded at harvest <strong>of</strong> sorghum. After harvest <strong>of</strong> crop, soil<br />

samples were collected (0-15 cm) and analyzed for organic carbon (wet oxidation method),<br />

available N (0.32 % alkaline KMnO4oxidizable), available P (0.5 M NaHCO3 extractable, pH<br />

8.5,) and K (Neutral normal ammonium acetate extractable) following the procedures described<br />

by Page et al. (1982).<br />

The input energy (MJ ha −1 ) and output energy was/ were computed for each treatment and<br />

expressed in terms <strong>of</strong> MJ ha −1 as suggested by Mittal et al. (1985). The energy use efficiency<br />

(EUE) derived as a ratio <strong>of</strong> output and input energy for each treatment (Sankar et al., 2013).<br />

Results<br />

In the tillage and nutrient management practices, the maximum input energy was observed in<br />

CTN1 (63924 MJ ha -1 ) whereas the minimum input energy was observed in treatment LTN3<br />

(4391MJ ha -1 ) followed by treatment MTN3 (4945 MJ ha -1 ). The maximum output energy was<br />

observed in MTN2 (70389 MJ ha -1 ) followed by CTN2 (68308 MJ ha -1 ). The maximum energy<br />

use efficiency was observed in LTN3 (13.865) followed by MTN3 (13.323).<br />

In case <strong>of</strong> nutrient management, the maximum energy use efficiency was observed in N 3 (11.919)<br />

followed by N 2 (1.966). Also, it is observed that, minimum energy <strong>of</strong> 48.22 MJ was required for<br />

production <strong>of</strong> one kg grain where nutrition <strong>of</strong> 50% organic and 50% inorganic N recorded highest<br />

625 | Page Resource conservation and rainfed agriculture

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