Intensive rice cropping with short-duration high-yielding varieties along with increased use of mineral
fertilisers and improved irrigation facilities have resulted in spectacular increases in
crop productivity. This has, however, led to gradual replacement of organic manures
as sources of plant nutrients. There has been a sharp increase in the prices of P
and K fertilisers following withdrawal of subsidy, which has led to their decreased
consumption by the farmers. The low purchasing power of the farming community and
the issue of soil health have again renewed interest in organic recycling. Organic
sources available for use in rice production include the bulky organic manures like FYM,
quick growing leguminous shrubs grown in the cropping sequence, leguminous trees grown in
alley formations and using their loppings as mulch materials, forage or food legumes
properly inoculated with Rhizobia and grown in the sequence, blue green algae and
Azolla. Yield potential of both the crops in rice-based cropping systems can be
realized by organic manuring of Kharif rice with the available sources along with mineral
fertilization of both the crops in the acid lateritic soil conditions of eastern
India. Highest yields of Kharif and Rabi rice were obtained with application of
green manure and N application.
Long-term experiments
have shown that neither organic sources nor mineral fertilisers alone can achieve
sustainability in crop production. Continuous use of FYM is effective in stabilizing
rice productivity under low to medium cropping intensity where the nutrient demand is
relatively small. Nonetheless, integrated use of organic and mineral fertilisers has
been found to be more effective in maintaining higher productivity and stability through
correction of deficiencies of secondary and micronutrients in the course of mineralisation
on one hand and favourable physical and soil ecological conditions on the other. Organic
manuring also improves the physical and microbial conditions of soil and enhance
fertiliser use efficiency when applied in conjunction with mineral fertilisers.
Thus, all the major sources of plant nutrients such as soil, mineral, organic and
biological should be utilised in an efficient and judicious manner for sustainable crop
production in rice-rice cropping system.
Several studies have
been conducted on the complementary use of organic and mineral fertilisers in cropping
systems involving rice. Extensive field investigations in the acid lateritic soils
at Kharagpur revealed that locally available organic materials such as chopped straw, FYM,
water hyacinth compost, Azolla and green manure in situ with sunnhemp and dhaincha can
substitute N fertilizer up to 50 per cent of the total crop requirement. In a study
on fertilizer economy through organic manures in rice-rice cropping system, it was found
that total produce with application of 90 kg N + 12 t FYM/ha to Kharif rice and 60 kg N/ha
to Rabi rice was close to 120 kg N/ha +60 kg P2O5/ha to Kharif rice and 60 kg N/ha to Rabi
rice. Annual dressing of 10-15t FYM/ha along with optimal NPK fertilisers enhanced
rice yield over the optimal NPK dose by 25 and 20 percent in Kharif and Rabi season
respectively under the lateritic soils of Bhubaneshwar. It was however more
beneficial to apply the organic manure in the Kharif season because of its better
decomposition and mineralisation of nutrients in soil. Further, the effect of FYM
application was found to be comparable or even superior to lime amendment on the acidic
soils which seemed mainly due to the formation of A1-organo-chellates, resulting in the
reduction of A1 concentration in soil solution to levels beneficial to plant growth.
Similarly, in the red soils of Hyderabad, the average increase in rice yield due to NPK +
FYM was 17-21 percent in both Kharif and Rabi seasons. These and other results
suggest that substitution of 25-50 percent of the N through FYM in Kharif and application
of 75-100 percent optimum level of NPK in the Rabi produced the highest yields of
rice. The beneficial effect of organic manures in increasing nitrogen-use-efficiency
was also evident, particularly in the Rabi season. Further application of NPK
fertilisers alone did not influence the yield of succeeding rice crop but the residual
effect was observed with the incorporation of organic manure.The grain yield of Kharif
rice was increased by 21-22 percent and 10-13 percent with the application of Azolla or
wheat straw and FYM or water hyacinth compost, respectively. The residual effect of
these sources on the succeeding Rabi rice showed a yield increase of 14-18 percent and
8-10 percent compared with the control. Further, the residual effect was more
pronounced with integrated used of NPK fertilisers and organic manures. Therefore,
integrated nutrient supply is important as a soil ameliorant in alleviating the adverse
soil ecological conditions as in the case of acid lateritic soils and in improving soil
fertility and productivity.
Green manure of
legume shrubs or tree loppings has been known to be beneficial for sustaining rice
productivity. Sunnhemp and dhaincha are popular legumes for green manuring in rice
and can accumulate up to 100 kg N/ha in 50-55 days. Incorporation of these green
manures in situ before transplanting rice supplies about 45-60 kg N/ha, besides providing
a significant residual effect to the succeeding crops. Fertilizer use efficiency is
improved when a legume crop such as Sesbania cannabina or Lathyrus sativus is
introduced in rice-rice cropping system. Adding loppings of leguminous trees like
Leucaena leucocephalla and Glyricidia napus grown in alleys can also meet the crop N
requirement substantially. The productivity of rice-rice cropping system can be increased
by about 1 t/ha besides a net saving of 30 kg fertilizer N/ha by including a
short-duration legume such as cowpea or greengram and incorporating its residues into the
soil after harvesting the grains. Similarly, blue green algae culture in the rice
field can contribute about 25 kg N/ha to the rice crop. Algae multiply and cover the
field like a carpet which when incorporated into the soil, decomposes and releases N for
rice crop. Azolla can be grown in tanks or in rice fields and incorporated into the
soil after 4-6 weeks. Nitrogen contribution through Azolla dual cropping with rice has
been worked out to be about 25-30 kg N/ha. Azolla growth is generally poor without P
fertilisation but a substantial improvement in growth and yield of rice is achieved when
dual cropped Azolla is fertilized with P and incorporated into the soil at a later
stage. An application of about 30 kg P2O5 /ha is adequate for
optimum growth of Azolla. The use of Azolla appears to be promising in the Rabi
season when there is good water management and availability of other organic sources like
FYM and green manures is limited.