Author: Abedi, Tayebeh
Date published: August 1, 2010
Cereals are an important dietary protein source throughout the world, because they constitute the main protein and energy supply in most countries (Bos et al. 2005). Wheat is one of the major cereal crops with a unique protein, which is consumed by humans and is grown around the world in diverse environments. Wheat seed-storage proteins according to their solubility properties are traditionally classified into four classes; albumins, globulins, prolamins and glutelins. Gluten, the most abundant wheat endosperm protein, is a large complex mainly composed of polymeric and monomeric proteins known as glutenins and gliadins, respectively (MacRitchie 1994). It has already been known that gluten proteins have a premier role in wheat flour quality. It is recognized that variation in protein content and composition significantly affect wheat quality with a subsequent influence on baking properties (Borghi et al. 1995; Daniel and Triboi 2000; Johansson and Svensson 1999; Johansson et al. 2001; Wooding et al. 2000). Wheat protein content and baking quality highly depend on genetic background and environmental factors, especially influence of drought and heat stress, during the grain filling period and nitrogen availability (soil N, rate and time of N application) (Altenbach et al. 2002; Dupont and Altenbach 2003; Luo et al. 2000; Ottman et al. 2000; Rharrabti et al. 2001; Tea et al. 2004). Nitrogen rate, type of nitrogen, and timing of its application are important factors to increase wheat yield. (Garrido-Lestache et al. 2005; Grant et al. 2001; López -Bellido et al. 1998). Furthermore, N fertilization is useful to enhance the baking quality parameters such as protein content and protein quality (Grant et al. 2001). Some studies showed that N fertilization increases the total quantity of flour proteins, resulting in an increase in both gliadins and glutenins (Dupont and Altenbach 2003; Johansson et al. 2001; Johansson et al. 2004; Martre et al. 2003; Triboi et al. 2000). The use of chemical fertilizers has been increased worldwide for cereal production (Abril et al. 2007) due to availability of inexpensive fertilizers (Graham and Vance 2000). The continued use of chemical fertilizers causes health and environmental hazards such as ground and surface water pollution by nitrate leaching (Pimentel 1996). So, reducing the amount of nitrogen fertilizers applied to the field without a nitrogen deficiency will be the main challenge in field management. One of the possible options to reduce the use of chemical fertilizer could be recycling of organic wastes. Compost as the organic waste can be a valuable and inexpensive fertilizer and source of plant nutrients. Positive effects of organic waste on soil structure, aggregate stability and water-holding capacity were reported in several studies (Jedidi et al. 2004; Odlare et al. 2008; Shen and Shen 2001; Wells et al. 2000). Furthermore, compost has a high nutritional value, with high concentrations of especially nitrogen, phosphorus and potassium, while the contamination by heavy metals and other toxic substances are very low. (Asghar et al. 2006). Previous studies showed that the combination of compost with chemical fertilizer further enhanced the biomass and grain yield of crops (Sarwar et al. 2007; Sarwar et al. 2008; Cheuk et al. 2003). Furthermore, positive changes have been reported in the quality of wheat flour, because of increasing the amount of gluten after compost treatment (Gopinath et al. 2008). It is important to conduct research to determine the plant response to N fertilization and to develop rational practices for more N use efficiency in this plant, in order to improve the nitrogen application management. The objective of this study is to investigate the influence of inorganic (nitrogen) and organic (compost) fertilizers on yield, yield components, gluten content, protein concentration and its banding pattern in various growth stages of bread wheat. The main aim of this study is to improve nitrogen management practices to maximize grain yield production with no reduction in protein content and its quality and alleviate the environmental hazards by extra nitrogen leaching.
Material and Method
The field experiment was conducted on silty loam soil at the Experimental Farm of School of Agriculture, Shiraz University, Shiraz, Iran, is located at bajgah (1810 m above the sea level with longitude 52° 35' and latitude 39° 40') in the autumn of 2007. The experiment was laid out in a randomized complete-block design with four replications. The treatments included nitrogen at four levels (0, 80, 160 and 240 kg N ha ^sup ^sup -1^^) and municipal waste compost at two levels (30 and 60 Mg ha ^sup ^sup -1^^) pre planting and soil incorporated. Nitrogen was supplied from urea and was added to plots in two periods (50% at planting time and 50% at stem elongation stage) and compost was supplied from compost factory in Esfahan, Iran. After land preparation plowing, disking and ridging the plots (6 m long and 2 m wide) were done and winter wheat (CV. Shiraz) was planted at seeding rate of 180 kg ha ^sup -1^ in the rows. Spikes per plant were determined from 1 m2 area of each plot by clipping the plants at the soil surface. After over drying and weighing, grain was threshed from the straw, cleaned, and weighed. Kernel weight was determined by counting weighing four 250 kernel samples taken from the harvested grain of each plot. Kernels per ear were calculated by dividing the number of kernels per harvested area by the number of ears per harvested area. After harvesting the grain yield and yield component (spikes plant^sup -1^, seeds spike^sup -1^ and 1000 kernels weight) were determined for all plots. As our results showed no significant differences between 160 and 240 kg N ha ^sup -1^ on yield components and grain yield, we considered just three levels of all N treatments (0, 80 and 160 kg N ha ^sup -1^) to investigate protein content and its pattern. Samples from all replications in different growth stages were used to determine the gluten and protein content and electrophoresis analyses.
In different growth stages, the leaves were harvested, frozen in liquid nitrogen and then stored at -80° C. The frozen leaves were ground to a fine powder in liquid nitrogen and total protein extracted with ice-cold 0.1 M Tris - HCl buffer (pH 7.5) containing 5% (w/v) PVP (4:1 buffer volume/fresh weight). The homogenate was centrifuged at 13000 g for 15 min, at 4° C, and the supernatant was used for determining protein concentration and SDS-PAGE analysis. Furthermore, the seeds were ground to a fine powder and 100 mg of powder was used for protein extraction. 1 ml extraction buffer was added to each micro tube containing 100 mg powder and centrifuged at 13000 g for 10 min at 4° C.
The concentration of protein was measured by the Bradford method (1976). BSA was used as a standard.
Prior to electrophoresis, samples were mixed with SDS sample buffer (62.5 mM Tris-HCl, pH 6.8, 2% [w/v] SDS, 10% [w/v] glycerol, 5% [v/v] β-mercaptoethanol, 0.001% [w/v] bromophenol blue) and boiled for 5 min. Protein samples were separated on 5- 20% SDS- PAGE gradient gels based on method of Laemmli (1970). Staining and destaining of the gels were carried out by the standard Coomassie brilliant blue G-250 (CCB) staining method.
Flour was hand washed according to the standard method (AACC 1983) with 30 min of resting time. Isolated drying gluten contained was evaluated.
All data were analyzed by analysis of variance (ANOVA) procedures using MSTATC software package. Treatment means were separated by Duncan's multiple range tests at (Duncan 0.05).
Yield and Yield Components
Results showed that, with increasing levels of nitrogen from 80 to 160 and 240 kg ha^sup -1^, wheat grain yield significantly increased (52%, 115% and 95% over control in 80, 160 and 240 kg N ha^sup -1^ treatments, respectively), compared to control (Table 1). Considerable point is insignificant difference between grain yield in 160 and 240 kg N ha 1- treatments. Results revealed a significant increase in grain yield when compost was applied. However, there was no significant difference between 30 and 60 Mg compost ha ^sup -1^ application (Table 1). The use of chemical fertilizer (N) in combination with compost increased the grain yield significantly (Table 1). The maximum yield increases were observed in 160 kg N ha ^sup -1^ in combination with 30 or 60 Mg compost ha ^sup -1^ (Table 1). Result of nitrogen and compost interaction effects indicated that maximum wheat grain yield was obtained from 30 Mg ha ^sup -1^ compost application and 160 kg N ha ^sup -1^ (7546.19 kg ha ^sup -1^) and increasing nitrogen levels from 160 to 240 kg N ha ^sup -1^ had no significant effect on wheat yield. Results clearly indicate that nitrogenous fertilizer had a significant effect on yield components (spikes plant^sup -1^, seeds spike^sup -1^ and 1000 kernels weight) and grain yield (Table 2). From 0 to 80 and 160 kg N ha ^sup -1^ all of these parameters significantly enhanced with increasing nitrogen levels, but there was no significant increase from 160 to 240 kg N ha ^sup -1^ (Table 2). Data in table 3 shows that 30 and 60 Mg compost ha^sup -1^ application lead to a same significant increase in spikes plant^sup -1^ and seeds spike^sup -1^, compared to no compost application. As well as that, the maximum amount of 1000- grain weight was obtained in 60 Mg compost ha^sup -1^ application.
Protein and Gluten Content
Figure 1 shows no significant effects of nitrogen fertilizer on seed protein content. However, compost had a significant effect on seed protein and the maximum amount of seed protein was observed in 60 Mg compost ha ^sup -1^ treatment. Results indicated that there were no significant differences in seed gluten content between different nitrogen and compost treatments (data not shown).
SDS-PAGE Protein Analysis
Figure 2 demonstrates the SDS PAGE protein profile of wheat leaves in different growth stages and wheat seed under different fertilization treatments. The results clearly indicated that there is no polymorphism between different treatments in tillering and stem elongation stages and seed. However, in ear emergence stage, intensity of a 50 kDa molecular weight band was increased in 160 kg N ha^sup -1^ and all compost levels especially in 60 Mg compost ha^sup -1^ (Fig. 2).
The rapid increase in the world population demands parallel increases in food production, particularly of wheat. In order to preserve the environment and the present natural resources, further increases in global wheat production must be along with a proper management of fertilization. Integrated use of organic wastes and chemical fertilizers is beneficial in improving crop yield, soil pH, organic carbon and available N, P and K in soil (Rautaray et al. 2003). The results of present experiments indicated that wheat grain yield and yield components increased significantly with the application of N fertilizer and compost (Table1, 2 and 3). However, there were no significant enhancements in these parameters under last two levels of N and compost applications (160 and 240 kg N ha ^sup -1^) or (30 and 60 Mg ha^sup -1^ compost). Additionally, results showed that the use of chemical fertilizer, N, in combination with organic materials, compost, further enhanced the grains yield. Similar results were obtained by other scientists (Cheuk et al. 2003; Parmer and Sharma 2002; Sarwar et al. 2007; Sarwar et al. 2008). Besides the positive effect of organic fertilizer on soil structure that lead to better root development that result in more nutrient uptake, compost not only slowly releases nutrients but also prevents the losses of chemical fertilizers through denitrification, volatilization and leaching by binding to nutrients and releasing with the passage of time (Arshad et al. 2004). Thus, it is very likely that when we apply enriched compost along with chemical fertilizers, compost prevents nutrient losses. Consequently, integrated use of chemical fertilizers and recycled organic waste may improve the efficiency of chemical fertilizers and thus reduce their use in order to improve crop productivity as well as sustain soil health and fertility. Increasing yield potential without negative effect on the quality of the grain is difficult, mainly because increases in grain yield are generally accompanied by a decrease in the seed protein content, which is strongly associated with bread-making quality. Therefore, the protein and gluten content were determined under different fertilization treatments. The results indicated that seed water-soluble protein (figure 1) and gluten contents were unaffected by N strategy. These results are in accordance with the conclusions of other researchers who found that the quantity of albuminsglobulins is scarcely influenced by N nutrition (Dupont and Altenbach 2003; Johansson et al. 2001; Pedersen and Jorgensen 2007; Wieser and Seilmeier 1998). As noted previously, protein composition of the wheat grain is influenced by genotype, as well as by cultivation system and environmental conditions. In other words, although increased nitrogen supply correlated significantly to an increase in all protein components, its effect on grain protein also depends on the cultivar sown, due to different uses of available soil N, especially during stem elongation. One important point in our finding was significant increase in content of grain protein when we used organic material in combination with N fertilization (Fig. 1). It seems that organic matter can improve the physical properties of the soil and would have caused increased root development that acted positively in more uptakes of water and nutrients (Brady and Weil 2005). In a word, the effect of combination of compost and chemical fertilizers on seed protein was positive, because of more nutrients availability. In order to find out the effect of organic and inorganic fertilizer on protein pattern of leaf and seed, we carried out SDS electrophoresis in various growth stages and seed.As regards Figure 2, we observed no polymorphism in leaf protein pattern in all growth stages exception in ear emergence stage that density of a 50 kDa molecular weight band was increased in some treatments. Furthermore, seed water soluble proteins such as Albumin and Globulin showed no polymorphism, which confirmed insensitivity of these proteins to nitrogenous fertilization.To sum up, results described here confirm application of 160 kg N ha^sup -1^ in composition with compost as an organic fertilizer result in the maximum amount of wheat yield component which lead to the highest grain yield. Moreover, we found negligible influence of N supply on grain protein and gluten content, while compost application lead to grain protein content enhancement due to its effect on soil structure and consequently increase in plant nutrients uptake with no negative effect on seed protein pattern. In conclusion, it's strongly suggested to use combination of organic and inorganic fertilizer to achieve highest yield without negative effect on seed quality. It is clear from the results of the present study that 30% of the required nitrogen fertilizer could be replaced by compost, because compost improved the use efficiency of recommended nitrogen fertilizer and reduced its cost. In this way, by carefully managing N fertilization, less N may be needed while grain wheat yields and protein may be maintained or increased. In addition, less use of N fertilization will lead to environmental conversation.
AACC (1983) Approved Methods of the AACC, 8th ed. S Paul, MN: American Association of Cereal Chemistry (Method 38^sup -1^0, approved April 1961).
Abril A, Baleani D, Casado-Murillo N, Noe L (2007) Effect of wheat crop fertilization on nitrogen dynamics and balance in the Humid Pampas, Argentina. Agric Ecosyst Environ 119: 171^sup -1^76.
Altenbach SB, Kothari KM, Lieu D (2002) Environmental conditions during wheat grain development alters temporal regulation of major gluten protein genes. Cereal Chem 79: 279- 285.
Arshad M, Khalid A, Mahmood MH, Zahir ZA (2004) Potential of nitrogen and L-tryptophan enriched compost for improving growth and yield of hybrid maize. Pak J Agric Sci 41: 16-24.
Asghar HN, Ishaq M, Zahir ZA, Khalid M, Arshad M (2006) Response of radish to integrated use of nitrogen fertilizer and recycled organic waste. Pak J Bot 38: 691-700.
Borghi B, Giordani G, Corbellini M (1995) Influence of crop rotation, manure and fertilizers on bread making quality of wheat (Triticum aestivum L.). Eur J Agron 4: 37-45.
Bos C, Juillet B, Fouillet H, Turlan L, Dare S, Luengo C, N`tounda R, Benamouzig R, Gausseres N, Tome D, Gaudichon C (2005) Postprandial metabolic utilization of wheat protein in humans. Am J Clin Nutr 81: 87-94.
Bradford M (1976) A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal Biochem 72: 248- 254.
Brady NC, Weil RR (2005) The nature and properties of soil, 13rd edn. Macmillan Publishing Co, New York.
Cheuk W, Lo KV, Branion RMR, Fraser B (2003) Benefits of sustainable waste management in the vegetable greenhouse industry. J Environ Sci Health 38: 855-863.
Daniel C, Triboi E (2000) Effects of temperature and nitrogen nutrition on the grain composition of winter wheat: effects on gliadin content and composition. J Cereal Sci 32: 45-56.
Dupont FM, Altenbach SB (2003) Molecular and biochemical impacts of environmental factors on wheat grain development and protein synthesis. J Cereal Sci 38: 133-146.
Garrido-Lestache EL, L opez-Bellido RJ, L opez-Bellido L (2005) Durum wheat quality under Mediterranean conditions as affected by N rate, timing and splitting, N form and S fertilization. Europ J Agron 23: 265-278.
Gopinath KA, Saha S, Mina BL, Pande H, Kundu S, Gupta HS (2008) Influence of organic amendments on growth, yield and quality of wheat and on soil properties during transition to organic production. Nutr Cycl Agroecosys 82: 51-60.
Graham PH, Vance CP (2000) Nitrogen fixation in perspective: an overview of research and extension needs. Field Crops Res 65: 93- 106.
Grant CA, Brown KR, Racz GJ, Bailey LD (2001) Influence of source, timing and placement of nitrogen on grain yield and nitrogen removal of durum wheat under reduced and conventional tillage management. Can. J. Plant Sci 81: 17- 27.
Jedidi N, Hassen A, Van Cleemput O, M'Hiri A (2004) Microbial biomass in a soil amended with different types of organic wastes. Waste Manag Res 22: 93-99.
Johansson E, Prieto-Linde ML, Jonsson JO (2001) Effects of wheat cultivar and nitrogen application on storage protein composition and breadmaking quality. Cereal Chem 78: 19-25.
Johansson E, Prieto-Linde ML, Svensson G (2004) Influence of nitrogen application rate and timing on grain protein composition and gluten strength in Swedish wheat cultivars. J Plant Nutr Soil Sci 167: 345-350.
Johansson E, Svensson G (1999) Influences of yearly weather variation and fertilizer rate on bread-making quality in Swedish grown wheats containing HMW glutenin subunits 2+12 or 5+10 cultivated during the period 1990-1996. J Sci Food Agric 132: 13-22.
Laemmli UK (1970) Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature 227: 680-685.
López -Bellido L, López-Bellido RJ, Castillo JE, Fuentes M, L opez Garrido FJ (1998) Effects of tillage, crop rotation and nitrogen fertilization on wheat-grain quality grown under rainfed Mediterranean conditions. Agrono J 92: 1054^sup -1^063.
Luo C, Branlard G, Griffin WB, McNeil DL (2000) The effect of nitrogen and sulphur fertilization and their interaction with genotype on wheat glutenins and quality parameters. J Cereal Sci 31: 185-194.
MacRitchie F (1994) Physicochemical properties of wheat proteins in relation to functionality. Adv Food Nutr Res 36: 1-87.
Martre P, Porter JR, Jamieson PD, Triboi E (2003) Modeling grain nitrogen accumulation and protein composition to understand the sink/source regulations of nitrogen remobilization for wheat. Plant Physiol 133: 1959-1967.
Odlare M, Pell M, Svensson K (2008) Changes in soil chemical and microbiological properties during 4 years of application of various organic residues. Waste Manag. 28: 1246^sup -1^253.
Ottman MJ, Doerge TA, Martin E (2000) Durum grain quality as affected by nitrogen fertilization near anthesis and irrigation during grain fill. Agron J 92: 1035-1041.
Parmer DK, Sharma V (2002) Studies on long-term application of fertilizers and manure on yield of maizewheat rotation and soil properties under rainfed conditions in Western- Himalayas. J Indian Soc Soil Sci, 50: 311-312.
Pedersen L, Jorgensen JR (2007) Variation in rheological properties of gluten from three biscuit wheat cultivars in relation to nitrogen fertilization. J Cereal Sci 46: 132-138.
Pimentel D (1996) Green Revolution and chemical hazards. Sci Total Environ 188: 86-98.
Rautaray SK, Ghosh BC, Mittra BN (2003) Effect of fly ash, organic wastes and chemical fertilizers on yield, nutrient uptake, heavy metal content and residual fertility in a ricemustard cropping sequence under acid lateritic soils. Biores Tech 90: 275-283.
Rharrabti Y, Villegas D, Garcia Del Moral LF, Aparicio N, Elhani S, Royo C (2001) Environmental and genetic determination of protein content and grain yield in durum wheat under Mediterranean conditions. Plant Breed 120: 381-388.
Sarwar G, Hussain N, Schmeisky H, Muhammad S (2007) Use of compost an environment friendly technology for enhancing rice-wheat production in Pakistan. Pak J Bot 39 (5): 1553^sup -1^558.
Sarwar G, Hussain N, Schmeisky H, Muhammad S, Ibrahim M, Safdar E (2008) Improvement of soil physical and chemical properties with compost application in rice-wheat cropping system. Pak J Bot 40: 275-282.
Shen QR, Shen ZG (2001) Effects of pig manure and wheat straw on growth of mung bean seedlings grown in aluminium toxicity soil. Biores Tech 76: 235-240.
Tea I, Genter T, Naulet N, Boyer V, Lummerzheim M, Kleiber D (2004) Effect of foliar sulfur and nitrogen fertilization on wheat storage protein composition and dough mixing properties. Cereal Chem 81: 759-766.
Triboi E, Abad A, Michelena A, Lloveras J, Ollier JL, Daniel C (2000) Environmental effects on the quality of two wheat genotypes: 1. Quantitative and qualitative variation of storage proteins. Eur J Agron 13: 47-64.
Wells A, Chan K, Cornish P (2000) Comparison of conventional and alternative vegetable farming systems on the properties of a yellow earth in New South Wales. Agric Ecosyst Environ 80: 47-60.
Wieser H, Seilmeier W (1998) The influence of nitrogen fertilization on quantities and proportions of different protein types in wheat flour. J Sci Food Agric 76: 49-55.
Wooding AR, Kavale S, MacRitchie F, Stoddard FL, Wallace A (2000) Effects of nitrogen and sulfur fertilizer on protein composition, mixing requirements, and dough strength of four wheat cultivars. Cereal Chem 77: 798-807.
Tayebeh Abedi, Abass Alemzadeh* and Seyed Abdolreza Kazemeini
Department of Crop Production and Plant Breeding, School of Agriculture, Shiraz University, Shiraz, Iran
*Corresponding author: email@example.com