CHAPTER 4 EFFECT OF NUTRIENT CONCENTRATION AND CHLOROPHYLL CONTENT OF BLACK GRAM

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CHAPTER 4 EFFECT OF NUTRIENT CONCENTRATION AND CHLOROPHYLL CONTENT OF BLACK GRAM 4.1 Black gram A large number of pulses are grown in India. The major ones being lathyrus, lentil, chickpea, blackgram and mungbean. Among the pulses blackgram (Vigna mungo L.) is one of the main edible pulse crop of India. It ranks fourth among the pulses with an area of about 70,000 hectares (BBS, 2006). Nitrogen is an essential element and important determinant of growth and development of crop plant (Tanaka 1984). The important plant parameters proposed for estimating nitrogen stress are leaf nitrogen, dry weight, leaf elongation, leaf area and carbon dioxide rate (Green, 1976). Soils of India are mostly deficient in nitrogen. As soils of N deficiency is common in tropics and subtropics (Dakora and Keya, 1997), N supply and N management will continue to be important factor in crop production in this region. Another factor of concern is the significant environmental decline already associated with the injudicious use of the fertilizer nitrogen (Vitousek 1997). It has been observed that photosynthesis rate decreases after 77

flowering. The leaf nitrogen and chlorophyll content also showed a similar decline (Rao and Ghildiyal, 1985). It was suggested that decrease in photosynthesis rate after flowering was due to the mobilization and translocation of nitrogen from leaves to seeds, owing to higher nitrogen requirement of pulse crop for seed development (Ghildiya1 and Sirohi, 1996). Mitra et al. (1988) observed that urea application retarded leaf senescence as judged by the retention of chlorophyll and leaf nitrogen. It should be possible to increase N 2 fixation by legumes through genetic improvement and management practices (Hardarson and Atkins, 2003). Since the process of nodulation and nitrogen fixation is inhibited at higher levels of fertilizer nitrogen in the soil (Lawn and Brun, 1994) there is a high demand of nitrogen by the crop at post flowering period; hence it is necessary to have clear understanding on nitrogen use efficiency of legume crops. Foliar application of N is reported to have beneficial effect on mungbean (Hamid, 1991). Anabaena azollae sp exhibit lignolysis and released phenolic compounds which induced profuse sporulation of the organism (Malliga, 2008). This study was therefore undertaken to find out the role of cyanobacterial effluent with organic manures on the leaf chlorophyll. 4.2 Analysis of nutrient content of two blackgram species A field experiment was conducted at the fields of Thanjavur District, TamilNadu (from March 2008 to June 2008). Two organic manures such as Anabaena azollae sp (ML-2) treated coir waste and cow dung were used. The seeds of two black gram ATD mash 1 and ATD mash 3 were collected from Aduthurai, Tamil Nadu. 78

Soil of the experimental field was silty clay with ph 6.5. The experimental soil contained 0.159% total N, 0.619% organic carbon, 0.312 meq exchangeable P/100g soil, 0.38 meq exchangeable K/100 g soil and CEC 22.54 meq/100 g soil. Log phase culture of Anabaena azollae ML-2 was taken and mixed with (1:5) coir waste and incubated for degradation process. The experimental site is situated in a fertile land. The experiment was laid out in a factorial RCBD with 3 replications. Treatment Combinations Two varieties of black grams like ATD mash-1 and ATD-mash-3 were treated with two different manures - Anabaena azollae+ coirwaste and cow dung. The two different organic manures used at different concentration constituted the following combinations. i) ATD mash-3 with no manure (control) ii) ATD mash-3 treated with different concentration of 20kg ha -1, 60kg ha -1, 80kg ha -1 and 100kg ha -1 level of coir waste manure. iii) iv) ATD mash-1 treated with no manure (control) ATD mash -1 treated with different levels of 20kg ha -1, 40kg ha -1, 60 kg ha -1, 80 kg ha -1 and 100kg ha -1 of coir waste nitrogen fertilizer. The above procedure is followed for cow dung manure also. 79

The well prepared soil was fertilized at the rate of 50 and 36 kg P and K per ha. Organic Nitrogen is six levels of 0, 20, 40, 60, 80, 100 kg ha -1. Half dose of N and full dose of P and K were applied as basal at the time of seed sowing. Seeds were sown on 9 th March, 2008, with 10x30 cm 2 spacing; light irrigation was given to establish the seedlings properly. Excess seedlings were removed on 20 th March 2008 to retain one seeding per square feet. The crop was top-dressed with rest half of N on April 6, 2008. 4.3 Laboratory analysis of plant samples Leaf chlorophyll content Leaf chlorophyll content of two black gram varieties were measured at pre-flowering and pod filling stage. For this reason the top most leaf was collected and leaf chlorophyll was determined in the lab by utilizing acetone method (Arnon, 1986). Oven dried plant materials (leaves + stem + petiole + grain) at final harvest were ground for the estimation of different mineral icons. Total N analysis Estimation of total nitrogen was done by colorimetric method flowing Linder (1994). Plant sample was digested in Kjeldahl digestion flask with salicylic sulfuric acid and digestion catalyst. After digestion, color of the solution was developed with four different reagents (reagent B 1ml, 7-10 drops of solution A, 5ml of solution C and 5 ml of solution D). Then 80

absorbance of the solution was measured at 625 nm wavelength with Double Beam Spectrophotometer (Model 200-20 Hitachi) Total P analysis Total P was determined by nitric-perchloric acid digestion method as described by Yamakawa (1992). The absorbance was measured at 440nm with Double Beam Spectrophotometer (Model 200-20 Hitachi). K analysis K was determined following Hitachi Ltd. (1996). During K analysis dry plant sample was digested with nitric-perchloric acid solution. After digestion the sample was diluted with distilled water. Then the absorbance of that respective ion was measured with atomic absorption spectrophotometer (Model 41170-30 Hitachi). Statistical Analysis The data recorded on different plant characters were statistically analyzed with the help of MSTAT program. The differences between the treatment means were compared by Least significant Difference (LSD) test (Gomez and Gomez, 1983). 81

4.4 Results and Discussion Chlorophyll and Leaf Nitrogen Content Chlorophyll and leaf Nitrogen content of two blackgram varieties were measured at pre-flowering and pod titling stage. There is a positive best fit linear functional relationship existed between leaf chlorophyll and leaf nitrogen content with different manures. Chlorophyll (mg/g) 2 1.8 1.6 1.4 1.2 1 0.8 0.6 0.4 0.2 0 Cow dung Coir waste 0 20 40 60 80 100 Nitrogen level (kg/ha) Figure 4.1 Relationship between different N levels supplied by organic manures and chlorophyll content of blackgram (ATD mash 3) 82

Chlorophyll (mg/g) 2 1.8 1.6 1.4 1.2 1 0.8 0.6 0.4 0.2 0 Cow dung Coir waste 0 20 40 60 80 100 Nitrogen level (kg/ha) Figure 4.2 Relationship between N levels supplied by organic manures and chlorophyll content of blackgram (ATD mash 1) Fig.4.1 and Fig.4.2 shows the functional relationship between different N levels and chlorophyll content of two black gram varieties at harvesting stage. 83

Leaf N content (%) 2 1.8 1.6 1.4 Cow dung Coir waste 1.2 0 20 40 60 80 100 Nitrogen level (kg/ha) Figure 4.3 Relationship between different N levels supplied by organic manures and leaf N content of black gram (ATD mash 3) Leaf N content (%) 2 1.5 1 0.5 Cow dung Coir waste 0 0 20 40 60 80 100 Nitrogen level (kg/ha) Figure 4.4 Relationship between different N levels supplied by organic manures and leaf N content of black gram (ATD mash 1) 84

Figure 4.3 and 4.4 shows the functional relationship between different N levels and leaf N content of two black gram varieties. The functional relationship indicated that with the increasing levels leaf chlorophyll and nitrogen content increased linearly. Irrespective of varieties and N levels both leaf chlorophyll and nitrogen content showed higher values at mature stage (Fig 4.1 and 4.2). This finding is consistent with the findings of Mitra et al. (1998).The chlorophyll and leaf nitrogen content were found to be slightly higher in coir waste manuring plants than cow dung manuring plants (Fig 4.3 and 4.4). It was concluded that organic manure as an exogenous source of nitrogen was used to test the model that increased nitrogen supply during flowering and pod filling stage would retard leaf senescence and improve photosynthesis and nitrogen availability for seed biomass and drought stress tolerance. Table 4.1 Effect of N,P, K content of two black gram varieties supplied with Anabaena azollae (ML-2) treated coir waste at harvest Variety Organic N Nutrient concentration (%) in (kg ha -1 ) total plant at harvest stage N P K 0 1.43 0.14 1.01 20 1.47 0.15 1.01 40 1.48 0.16 1.02 ATD mash3 60 1.58 0.18 1.24 80 1.52 0.17 1.20 100 1.49 0.16 1.16 0 1.35 0.12 0.93 20 1.37 0.14 0.95 40 1.38 0.15 0.97 ATD mash1 60 1.57 0.16 1.10 80 1.47 0.15 1.01 100 1.38 0.14 0.98 LSD(0.05) NS NS NS CV (%) 8.94 15.85 12.78 85

Nutrient content and uptake Nutrient concentration (N, P and K) in plants Nitrogen is one of the important key factors in regulating the growth and yield of crops. N concentration in plant components often been used as an index of crops N requirement. Plants N content was determined at maturity stage. The levels of applied organic fertilizer influenced the tissue N content. N content in plant parts increased in N levels up to 60kg ha -1 and it helped to sustain high concentration of N. An increase in N levels increased N content significantly at all the growth stages, highest N content was observed at active tiltering stage with higher N level (100kg ha -1) and lower at harvest without using manure (Quayum, 2004). Plants grown without manure had tissue N concentration of 1.43% at harvest whereas plants treated with coirwaste of 60kg ha -1 had 1.58%. N content in plant tissue irrespective of varieties was highest at the same level of N treatment. Similar trend in pea was obtained by Verma (1998). N supply through manure application also influenced P and K content in the plant tissue, but differences was not as conspicuous as was observed in case of N content (Table 4.1). P and K content in all plant organs increased up to 60kg ha -1 and then further increases in nitrogen caused reduction in P and K content. From the table it is clear that total N, P and K content (%) in both the black gram varieties increased up to 60 kg N ha -1 then decreased. But these nutrients are always higher in ATD mash 3 than ATD mash 1 at all levels of N. After 60 kg ha -1, further increase in nitrogen caused reduction of P content also observed in pea (Verma and Bhandari, 1998). 86

Irrespective of N levels ATD mash 3 always contain higher tissue N concentration that ATD mash1 (Table 4.1). The increase in N content in blackgram at this level may be due to the accelerated metabolic activity of the fertilized plants resulting increased absorbing power of root system. Nutrient Concentration (N.P. and K) in grains N concentration in the grains increased progressively with the increasing levels in both the black gram varieties (Table 4.2). Irrespective of varieties and N levels, seed N content increased with the increases of N levels up to 60 kg ha -1. Further increased in N levels, N content in seed decreased gradually. Among the varieties ATD mash 3 showed that N uptake in grain increased with increase in N levels of coirwaste manuring plants than cowdung manuring plants. Nitrogen up take in rice straw also followed a similar trend as that in grain. Sing et al. (1992) reported, response of N of field pea up to 30kg ha -1 whereas Negi (1992) up to 20kg ha -1 only. 87

Table 4.2 Effect on N, P and K contents in seeds of two black grams varieties supplied with coir waste manure treated with Anabaena azollae extract at harvest Variety ATD mash3 ATD mash1 Organic N (kg ha -1 ) Nutrient concentration (%) in total plant at harvest stage N P K 0 2.19 0.18 0.84 20 2.24 0.18 0.85 40 2.25 0.19 0.86 60 2.35 0.22 0.92 80 2.29 0.19 0.89 100 2.25 0.19 0.87 0 2.00 0.13 0.78 20 2.08 0.14 0.80 40 2.14 0.16 0.82 60 2.33 0.18 0.90 80 2.22 0.17 0.87 100 2.20 0.15 0.86 LSD(0.05) NS NS NS CV (%) 8.03 6.15 2.12 P and K content in seed also increased with the increased of N levels (Table 4.2) but the effect were not so conspicuous like as N content. Maximum P and K content in seed were observed in plant treated with 60 kg ha -1. Further increase of N levels decreased, P and K content in seed. From this table it clear that N levels influence seed N, P and K content up to 60 kg ha -1. But the effect was more pronounced on N content than P and K content in seed. Among the varieties, ATD mash 3 always contained higher percent of N, P and K compared to ATD mash 1 using coir waste manuring. N, P and K content in seed always lower in 0 kg N ha -1 treated plants. 88

Nutrient uptake (N, P and K) Uptake of nutrient elements (N, P and K) by the plant was estimated as the dry matter multiplied by their respective concentration (%).The total uptake of N, P and K by the black gram varieties as influenced by applied N organic fertilizer is presented in (Fig 4.5). As the total dry matter increased over time, N, P and K uptake also increased. Response of N,P and K uptake to the applied N fertilizer paralleled the response of plant nutrient concentration (%). Total uptake of N, P and K varied due to nitrogen treatment variations. Plants treated with 60kg N ha -1 had the highest N, P and K uptake irrespective of both the varieties. Up to 60kg N ha -1 all the nutrient uptake increased, but further increase of organic fertilizer decreased the N, P and K uptake gradually. 89

(a) Total N uptake (g) 1500 1000 500 ATD mash 3 ATD mash 1 0 0 20 40 60 80 100 Nitrogen level (kg/ha) (b) Total P uptake (g) 150 100 50 ATD mash 3 ATD mash 1 0 0 20 40 60 80 100 Nitrogen level (kg/ha) (c) Total K uptake (g) 1000 800 600 400 200 ATD mash 3 ATD mash 1 0 0 20 40 60 80 100 Nitrogen level (kg/ha) Figure 4.5 The effect of different N levels supplied by coir waste on (a) N uptake (b) P uptake and (c) K uptake in two black gram varieties 90

Among the varieties ATD mash 3 always showed better uptake of these nutrients compared to ATD mash 1. This might be due to greater dry matter production by this variety. Nutrient uptake at 0 kg N ha -1 was lowest in both the varieties. Similar results also were obtained by Bahl et al. (2001) in pea and Ferdous (2003) in edible podded pea. Irrespective of Nitrogen levels and varieties, N uptake was always higher than P and K uptake (Fig.4.5). 91