Use of sewage sludge in bioenergy production—A case study on the effects on sorghum biomass production
Graphical abstract
Introduction
Energy Policy of Poland (2009) and Council Directive (2009) on the promotion and use of energy from renewable sources report that the overall share of energy from renewable sources should be 15% in 2020 and 20% in 2030. In addition, these documents contain provisions for conservation of forest resources and the promotion of energy crops, biomass of which may be used for direct combustion or biofuel production. The latter provision requires the destination for the purpose of energy crops 10% of the Polish national acreage of arable land (i.e., about 1.7 million ha).
Sweet sorghum (Sorghum bicolor (L.) Moench ssp. bicolor) from the Poaceae family is one of the promising bioenergy plant, having relatively low input requirements, drought tolerance and ability to maintain high yields under a wide range of environmental conditions (Wight et al., 2012, Ceotto et al., 2014). What is more, this crop contains a significant quantity of fermentable carbohydrates and does not directly compete with food crops (Han et al., 2011). Sweet sorghum is an annual C4 crop with tall stalks that that can be utilized for forage, silage (Ceotto et al., 2014, Kozłowski et al., 2006, O’Hara et al., 2013) or can be subjected to direct combustion, conversion to bioethanol or as a substrate for biogas production (Monteiro et al., 2012). Its biomass after juice extraction can be burnt in boilers to generate heat and steam for the operation of processing equipment and to generate electricity for both the process and export to the electricity network or may be converted into lignocellulosic ethanol (Rennie and Tubeileh, 2011, Zhao et al., 2012, Gill et al., 2014). It has been reported to have sulphur and ash contents that are 50 and 8 times lower, respectively, than that of lignite and its higher heating value has been measured to be 16.8 MJ kg−1 (Rennie and Tubeileh, 2011). Sorghum is widely distributed across Africa, Asia and North America and plays an important role among cereal crops, taking the 5th place in terms of acreage (after wheat, rice, maize and barley). Its total global area is above 38 million hectares, while the size of its production is estimated at 57 million metric tons per year (Dweikat, 2012, O’Hara et al., 2013, Gill et al., 2014). In the temperate climate of central Europe sweet sorghum is cultivated mainly as a forage or bioenergy crop, often competitive with maize.
Although sorghum has many traits that make it ideal for biofuel production, environmental and management conditions can affect its productivity (Wight et al., 2012). As shown by many authors (Al-Jaloud, 1999, Akdeniz et al., 2006, Keskin et al., 2009) the species can produce much higher biomass yield after applying a fertilizer, e.g., municipal sewage sludge, which is a source of many valuable nutrients and has a value close to manure, but contains a number of potentially harmful constituents such as heavy metals (Keskin et al., 2009). In addition, the agricultural use of biosolids has been found safe and effective, especially when the total amount of sewage sludge production in Poland is estimated to reach 706.7 thousand tons in 2018 (Werle and Wilk, 2010). The use of sewage sludge could not only increase yields but also positively affects biological and physico-chemical properties of the soil profile (Akdeniz et al., 2006, Singh and Agrawal, 2008, Bielińska et al., 2009, Epelde et al., 2009, Usman et al., 2012). Hence the interest in the use of biosolids in the cultivation of energy crops such as sweet sorghum has been studied by many authors (Al-Jaloud, 1999, Akdeniz et al., 2006, Keskin et al., 2009, Usman et al., 2012).
The primary focus of this study was to determine the impact of different municipal sewage sludge doses on biomass yields and structure. The research hypothesis assumes that municipal sewage sludge used for sorghum fertilization can be a valuable source of minerals for plants not intended for consumption, preferably promoting their growth and development. In addition, the possibility of applying sewage sludge in growing crops for energy purposes could become an alternative to the use of conventional fertilizers and contribute to redevelopment of the main current management method, i.e., storage, which poses a threat to the environment. For this purpose, a field experiment with four levels of municipal sewage sludge doses (10, 20, 40 and 60 Mg DM ha−1), and an untreated control object was established. Efforts were made to assess the impact of sewage sludge on the chemical composition and structure of the experimental plant yield and selected physico-chemical properties as well as enzymatic activity of the soil. The study also attempted to determine the most productive variety of sorghum in the conditions of south-eastern Poland.
Section snippets
Site description
Three-year (2008–2011) field experiments were established in a landfill belonging to the Janów Lubelski Department of Public Utilities in south-eastern Poland (50°43′17.7″N 22°22′08.0″E). The soil was a clay loam, characterized by slightly acidic pH, average humus content, low phosphorus, potassium and magnesium content, and heavy metal content remaining at the natural level (Kabata-Pendias, 2011) (Table 1). The WRB (2007) classification of the soil is Cambisols.
Experiment design and sample preparation
The experiment was established
Plant characteristics
Table 3, Table 4 provide descriptive statistics for each variable calculated using all the available data. The growing cycle seemed to be the principal factor influencing plant height, stem diameter, number of leaves, as well as the weight of single sweet sorghum plant. Generally, the highest plants were noted after the higher doses of the biosolids applied especially on plots with Sucrosorgo 506 (Table 3). Plants on the plots with Sucrosorgo 506 variety were significantly taller than in the
Discussion
In the present study, we aimed to evaluate the effect of municipal sewage sludge on the sweet sorghum yield and to determine the optimum application dose in three varieties cultivated under our experimental conditions. Concerning the effect of biosolid sludge on the sorghum yield, it should be mentioned that, whilst the application of sewage sludge generally improves sorghum yield traits (plant architecture, biomass production, energy yield), the main effects is considered to be related with
Conclusions
The study has highlighted the potential use of sewage sludge as a source of organic matter for improvement of clay loam soil and a reasonable production of bioenergy crop like sweet sorghum without the use of inorganic fertilizers. Biomass sorghum dry yields exceeded 30 Mg ha−1 y−1 in an optimized system within this study. The use of increasing doses of sewage sludge stimulated production of significantly increased numbers of leaves per plant, stem diameter, and dry mass of stems and leaf blades
Acknowledgment
This study was performed partially with the financial support of the Ministry of Science and Higher Education, Poland (grant No. N N310080336).
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