Sweet sorghum productivity for biofuels under increased soil salinity and reduced irrigation
Introduction
Interest in sweet sorghum in Mediterranean environments is increasing because of the use of biofuels (from juice) and raw materials (from bagasse) for energy production (Barbanti et al., 2006). Sweet sorghum is characterized by high sugar content, mainly sucrose, fructose and glucose, in the juice of the stalks, from which ethanol can be easily produced and used as biofuel. For this reason, sweet sorghum has also become a popular energy plant throughout the world (Mastrorilli et al., 1999). Additionally, sweet sorghum biomass is used for fiber, paper, syrup and animal feed (Steduto et al., 1997).
Water is the principal limiting factor of crop production in many areas of the world. Salinity also causes great losses in agriculture by lowering yields of various crops. Land salinization is acute and widespread in Greece (Koukoulakis et al., 2000). In these areas, irrigation is needed to obtain maximal yield because decreasing the water supply by irrigation causes a significant reduction in seasonal evapotranspiration, aerial sorghum dry matter and grain yield (Berenguer and Faci, 2001).
Sweet sorghum grows in marginal areas because of its high tolerance to saline and drought conditions (Berenguer and Faci, 2001, Almodares and Hadi, 2009). Sweet sorghum has higher water-use efficiency than other summer crops under both well-watered and water-stressed conditions (Steduto et al., 1997). From the agronomic point of view, sweet sorghum is more environmentally friendly than maize because of its relatively low nitrogen needs (Barbanti et al., 2006) and water requirements (Mastrorilli et al., 1999). According to Almodares and Hadi (2009), sweet sorghum used for biofuel production may be an alternative crop to maize in marginal irrigated areas where the irrigation water is limited during crop development. Sweet sorghum has also been suggested as a good source for ethanol production because of its rapid growth rate, early maturity and high total energy value (Smith and Buxton, 1993). Moreover, sweet sorghum production is encouraged by new policies regarding nonfood crops in the European Union (Rexen, 1992).
Despite that the potential of sweet sorghum as an alternative energy crop has been emphasized (Smith and Buxton, 1993, Steduto et al., 1997), the ability of various sweet sorghum cultivars to grow under soil salinity and water deficiency field conditions has not been sufficiently determined. Screening sweet sorghum cultivars with the objective of meliorating saline soils are challenges to breeders, plant physiologists and agronomists. When considering the introduction of sweet sorghum cultivars, the acceptance of farmers and their willingness to integrate ecologically appropriate crops must be guaranteed. The motivation of farmers may increase if sorghum cultivars provide direct benefits, such as acceptable biomass and biofuel production, from land where other crops are unproductive (Almodares and Hadi, 2009).
In semiarid Mediterranean areas, the principal limiting factor of crop production is water applied as irrigation to maximize yields. Therefore, to achieve a better planning of available water resources and to establish irrigation strategies that optimize crop yield, it is necessary to know the crop response to a variable irrigation supply (Berenguer and Faci, 2001), especially in saline soils where water stress is increased (Ould Ahmed et al., 2008). The objective of this research was to assess the productivity of four sweet sorghum cultivars grown in intermediate (3.2 dS m−1) or high (6.9 dS m−1) soil salinity with either low (120 mm) or intermediate (210 mm) irrigation water supply under Mediterranean conditions. Sweet sorghum productivity was also compared with the productivity of one grain cultivar and one grass sorghum cultivar.
Section snippets
Experimental site
A field experiment was conducted in 2007 (year 1) and was repeated in the same field in 2008 (year 2) at the Technological and Educational Institute Farm of Thessaloniki in Northern Greece (22°48′33″ E and 40°39′08″ N; elevation of 0 m). Experiments were carried out on a sandy loam (Typic Xeropsamment) soil with the following physicochemical characteristics; clay 56 g kg−1, silt 180 g kg−1, sand 764 g kg−1 and organic matter 9 g kg−1. The soil had a pH value of 8.1 (1:2 H2O). The mean monthly
Sorghum emergence
Sorghum emergence at 3 WAP was affected by soil salinity (P < 0.001) and depended on the type of sorghum cultivar (P < 0.001). In particular, the sorghum plant density in a soil salinity of 6.9 dS m−1 was 20% lower (59,917 plants ha−1) than the plant density in a soil salinity of 3.2 dS m−1 (75,083 plants ha−1) (Table 1). Averaged across the two soil salinity levels, the Susu grass sorghum cultivar (53,250 plants ha−1) was the most affected cultivar. The Sugar graze sweet sorghum, Urja sweet sorghum and
Discussion
According to the sorghum irrigation common practice in Greece, irrigation inputs range from approximately 520 mm to 660 mm (Sakellariou-Makrantonaki et al., 2007). Therefore, the low (90 mm + 30 mm) and intermediate (180 mm + 30 mm) irrigation water supplies applied during the current experiment further supplemented with rainfall water of 261 mm in year 1 and 142 mm in year 2 were approximately 50% and 75%, respectively, of the water amount typically applied in Greek sorghum fields.
The electrical
Conclusion
The results of this study indicated that sweet sorghum provides sufficient yields even when grown under stresses of soil salinity and reduced irrigation. Sweet sorghum plants produce sufficient juice, total sugar and ethanol yields in fields with soil salinity up to 3.2 dS m−1 even though the plants receive 50–75% of the water regimes typically applied to sorghum. Therefore, sweet sorghum may be viable as an alternative crop system for bioethanol production under increased salinity and reduced
Acknowledgement
Authors are grateful to Dr. Panteli Efthimiadi for providing the seeds of sorghum cultivars.
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