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Research Detail

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M. K. Kabir
Department of Soil, Water and Environment, University of Dhaka, Dhaka- 1000, Bangladesh

A. T. M. M. Kamal
Department of Soil, Water and Environment, University of Dhaka, Dhaka- 1000, Bangladesh

S. Jahan
Department of Soil, Water and Environment, University of Dhaka, Dhaka- 1000, Bangladesh

A. M. M. Faizullah
Department of Soil, Water and Environment, University of Dhaka, Dhaka- 1000, Bangladesh

S. M. Ullah
Department of Soil, Water and Environment, University of Dhaka, Dhaka- 1000, Bangladesh

A pot experiment was carried out to examine the yield of rice and mineral contents in rice grain (Oryza sativa L. cv. BRRI dhan-36) under five levels of sewage sludge-nitrogen fertilization, viz., SS0N280, SS60N49, SS120N35, SS200N28, and SS300N21. The grain yield contributing characters such as a number of filled grains per panicle, dry weight of grains, and weight of 1000 grains were significantly high in the treatment SSI20N35 as compared to the other treatments. However, the number of filled rice grains per panicle and weight of 1000 rice grain did not differ significantly between the treatments, SS0N220 and SSININ35. The contents of N, K, Ca, Mg, Fe, Cu, Zn and Pb in rice grains increased significantly with increasing rates of sewage sludge application. Crude protein content of rice grain increased significantly in sewage sludge treated treatment grains as compared to the sewage sludge free treatment. Accumulations of P and Mn in rice grain were unfavorably affected by sewage sludge. No detectable contents of Cr, Cd and Ni were found in rice grain.

  Sewage sludge, Nitrogen fertilization, Rice grain yield, Mineral contents
  Dhaka WASA sewage treatment plant, Pagla, Bangladesh
  
  
  Crop-Soil-Water Management
  Rice, Soil fertility

To find out the yield and mineral contents in rice grain under different levels of sewage sludge and nitrogen fertilization.

The experimental soil belonging to Naraibag series was collected from a depth of 0 - 15 cm. Dried sewage sludge (SS) was collected from Dhaka WASA sewage treatment plant, Pagla, Bangladesh. The collected soil and sewage sludge samples were air dried, ground and sieved through a 2 mm sieve for physical analyses as well as to grow rice. However, for chemical and physicochemical analyses, the soil and sewage sludge samples were further sieved through a 1 mm sieve and kept in plastic container. The relevant properties of the soil and sewage sludge samples are presented (Kabir a al. 2008). Rice seedlings (BRRI dhan-36) were grown in Boro season in pots containing 6 kg soil per pot. The experiment was conducted with five treatments, viz., SSoN280, SS60N49,SS120N35, SS200N28, and SS300N21 consisting of 5 levels of SS (0, 60, 120, 200 and 300 Ulla) and 5 levels of nitrogen (280, 49, 35, 28 and 21 kg/ha) in a CRD with three replications. Five treatments together with a basal dose of TSP (200 kg P205/ha) and muriate of potassium (200 kg K20/ha) were applied at the time of transplantation of rice seedling. After 5 days of transplantation, 50% N in the treatment SSoN280 and full dose of N in the rest of the treatments were applied. The remaining 50% N was applied in halves after 55 and 100 days of transplantation in SSoNiso treatment. Eight uniform-size rice seedlings of 40 days old were transplanted (2 seedlings/hill) in each pot, but after 15 days only the best four were allowed to grow. During the growing period, pots were irrigated properly with normal tap water and intercultural operations were done whenever necessary. The dry weight of grain, the weight of 1000 grains and the number of filled and non-filled grains were determined at maturity. The total nitrogen content of rice grain was determined by Micro-Kjeldhal's method (Jackson 1973). The protein content of rice grain was calculated by multiplying the %N content by a factor of 6.25. The total contents of P, K, Ca, Mg, Fe, Zn, Cu, Mn, Pb, Cr, Cd and Ni were determined after wet digestion of rice grain in HNO3-HC1O4 acid mixture (5 : 1). The total phosphorus content was determined colorimetrically using a Chemito visible spectrophotometer, after developing the yellow color with vanadomolybdate (Jackson 1973). Total potassium content in the extract was analyzed using a Gallenkamp flame photometer. The total contents of Ca, Mg, Fe, Zn, Cu, Mn, Pb, Cd, Cr and Ni in rice grain were analyzed in the extract by using Atomic Absorption Spectrometer (Perkin Elmer 3110) (Jackson 1973). The results were statistically analyzed using DMRT (Gomez and Gomez 1976).

  Bangladesh J. Sci. Res. 24(2): 161-168, 2011 (December)
  
Funding Source:
1.   Budget:  
  

The yield contributing characters, such as the number of filled and non-filled grains per panicle, dry weight of grains and weight of 1000 grains were taken into consideration to see the influence of sewage sludge-nitrogen fertilization on the yield of rice and are presented. The highest number of filled grains per panicle (85.67) was recorded in the treatment SS0N280 but decreased significantly with increasing sewage sludge applications, except in the treatment SS120N35. Significantly the lowest number of non-filled grains per panicle (40.00) was observed in the treatment SSoN280 and the highest in the treatment SS300N21 (49.33). However, no significant difference was found among most of the treatments. The significantly highest dry weight of grain (41.47 g/pot) was recorded from the treatment SS120N35 while statistically similar values were found in the rest of the treatments. Weight of 1000 rice grains was found the highest in the treatment SS0N280 (23.06 g) whereas decreased with increasing sewage sludge applications, but no significant difference was found between SS0N780 and SS120N35, and SS200N28 and SS300N21 treatments. The yield contributing characteristics were always significantly best in the treatment SS1x,N35 compared to all other treatments. It might be due to the fulfillment of nutrient requirements provided by the treatment SS120N35. The best yield response of rice grain was obtained with the treatment, SSI20N35 where 120 tons of sewage sludge per hectare plus 35 kg of nitrogen per hectare were added. This might be attributed due to the 'optimum release of essential macro-and micronutrient elements from the applied sewage sludge.

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