Sustainable biodiesel production from microalgae Graesiella emersonii through valorization of garden wastes-based vermicompost
Graphical abstract
Introduction
The global consumption of diesel by the transportation sector alone is about 1460 trillion liters and invariably the demand is likely to be increased by 40% in the coming decade (Leite et al., 2013). But this ever-growing demand for diesel can be seldom fulfilled by the petroleum resources due to its finite and non-renewable nature. Moreover, usage of fossil fuels is also reported to produce several environmental consequences such as greenhouse gas (GHG) emission and other climatic extremities. To tackle the issue and cater the future energy demands, globally there has been a lot of interest in developing alternative sustainable strategies. Researchers find renewable and clean energy resources as the alternative means to overcome the fuel shortage and climate change-related issues (Li et al., 2019). Biodiesel research has gained significant commendation since it has been proved as the viable alternative energy source due to its carbon neutrality, non-toxicity and biodegradability (Bennion et al., 2015). In addition, biodiesel is also found to enhance the engine performance and simultaneously curtail GHG emissions from vehicles (Manigandan et al., 2020). Though land-based oil crops are used for biodiesel production, the usage of cultivable land, water, and production costs hamper the technology to achieve sustainability (Li et al., 2020a).
Biodiesel produced from microalgae received greater attention due to its high lipid content (15–50%), rapid doubling time (3.5 h), year-round production irrespective of the season, non-usage of cultivable land, and atmospheric CO2 fixation potential (Chisti, 2007; Li et al., 2020a; Zhu et al., 2017). At the same time, the selection of microalgal strain is pivotal for successful biodiesel production in addition to culture conditions such as temperature, light intensity, and nutrients (Islam et al., 2013a). High lipid productivity, growth rate, scale-up potential and valued by-products are the important characters that would be considered during strain selection (Leu and Boussiba, 2014). The Chlorophyceae class of green algae, with a doubling time of <24 h and about 50% lipid content, has been found suitable for biodiesel production (Murthy and Kumar, 2019). Graesiella spp. is a native freshwater microalga that belongs to the class Chlorophyceae has some desirable traits which make them more advantageous than other algal strains. First, the size of the cell is large (8–12 μm) which makes them easily harvestable by sedimentation. Second, the ability to grow in high pH and extreme conditions. Third, the presence of high-quality lipid (33.4% d. wt.; ~ 90% as storage triglycerides (TAGs) and a reasonable amount of protein content (Duong et al., 2015). Fourth, it is not easily predated by zooplankton and protozoan due to its large size. Finally, it is found promising for outdoor raceway and pond cultivation when compared to other microalgal strains (Wen et al., 2016). Therefore, G. emersonii was isolated and utilized for the present study.
The mass cultivation of microalgae requires a large amount of fertilizers, which could disturb ecosystem health and questions the sustainability of commercial microalgal biofuel industry (Lam and Lee, 2012). During algal cultivation, the fertilizer production also seeks >50% of energy consumption (Clarens et al., 2010). Hence, it requires a cheap and organic form of nutrients to achieve sustainability in microalgae biodiesel production. The utilization of waste resources as a culture medium could be the suitable strategy. Various waste resources have been used for microalgae growth, such as animal excreta (Kim et al., 2016; Zhu et al., 2017), raw chicken manure, municipal wastewaters (Calixto et al., 2016), domestic sewage (Kligerman and Bouwer, 2015), etc. However, the major uncertainties include more diverse quality of waste resources, selection of suitable species, the presence of pathogens and predators, adaptability of microalgae, and reduced lipid productivity (Calixto et al., 2016; Zhu et al., 2017).
On the other hand, solid waste management (SWM) is a major challenge in developing countries because of the rapid urbanization and industrialization, societal modernization, and changing food consumption pattern (Alshehrei and Ameen, 2021). Globally, about 44% of the total wastes generated include garden, agriculture residues, and food-based wastes (Luttenberger, 2020). Among these, garden wastes (i.e., grass clippings, leaves, other plant debris etc.) contributes significantly and left unutilized either dumped as landfills or incinerated which may cause serious environmental problems (Li et al., 2020b). Therefore, proper management of these garden wastes is of prime concern since it forms the highest budget item (about 20% of the municipal budget) in low-income countries (Luttenberger, 2020). Microbial composting is a suitable approach to manage the solid organic waste globally; excluding the garden wastes which are difficult to decompose by microbes due to high C/N ratio and lignocellulose content (Li et al., 2020b). Vermicomposting is an effective technique for composting solid garden wastes rich in lignin and cellulose content (Gong et al., 2019) and convert them into stable organic fertilizers. It contains more amount of carbon, nitrogen, and phosphorus (Shinde et al., 1992) which are beneficial for microalgae (Kings et al., 2017). However, the nutrient rich compost could not be directly used for microalgal growth due to its complex nature and difficulty in assimilation by the algae (de Medeiros et al., 2020). Thus, production of extracts from the vermicompost is necessary to transfer the soluble or particulate organic matter, nutrients, and other chemical components from the solid media into a liquid phase that enables the microalgae to absorb nutrient more efficiently (Hanc et al., 2017; de Medeiros et al., 2020). In earlier studies, agro-industrial residues, fruits, and vegetable waste-based microbial compost have been found as lucrative nutrient source for microalgal cultivation (de Medeiros et al., 2020). It is noteworthy to mention that the quality of raw materials used for vermicompost, and the process of extract (aerobic or anaerobic) production decides the nutrient quality of the compost and the extract produced thereof (Hanc et al., 2017). To the best of our knowledge, no studies have utilized garden wastes as raw material for vermicomposting and utilized the same for extract production and for microalgal cultivation.
Therefore, the present study utilized the garden wastes, converted them into vermicompost and the extract was prepared by two methods (i) aerobic (ii) anaerobic, then the nutrient quality was estimated. The extracts were then added with BG11 medium at different proportions and the growth, cell size, and lipid productivity of the Chlorophyceae microalgae (Graesiella emersonii MN877773) were estimated. Following this, the best performing media combinations have been selected for studying the mineral content, fatty acid profiling and biodiesel quality. The same combination was also utilized for outdoor cultivation.
Section snippets
Isolation, identification, and culture conditions of algae
The microalgal inoculum was collected from freshwater tanks of ICAR-Central Institute of Fisheries Education, Kolkata, West Bengal. The algae were then morphologically identified following Bellinger and Sigee (2010) and Prescott (1962) under light microscopy (Nikon Eclipse –Ci, Japan) at 400× magnification and also characterized by using molecular tools (Ratha et al., 2012). For genomic DNA extraction and PCR amplification,100 mL algal culture was first centrifuged at 5000 rpm for 10 min at
Microalgae identification
Freshwater algal strains can produce quality proteins, bioactive compounds, and acts as a biodiesel feedstock globally (Duong et al., 2015). The present study has isolated the microalgae from the freshwater tank, and it was stained with Nile red to confirm them as oleaginous strain. It was identified as Graesiella emersonii (Shihara and R.W. Krauss) with the key morphological characters—cells varied from ellipsoidal to somewhat spherical in shape, cell wall relatively thick, double-layered.
Conclusion
In the present study, garden wastes were converted into vermicompost extract and the same was utilized for microalgal biodiesel production. The 1:1 combination medium of anaerobic vermicompost extract and BG11 yielded higher biomass, lipid content and lipid productivity of Graesiella emersonii MN877773 in laboratory culture conditions. The test media also produced large sized G. emersonii cells with good sedimentation properties which enables easy harvest. The lipid productivity was 18.2%
CRediT authorship contribution statement
Santhana Kumar V., Soma Das Sarkar: Conceptualization, Investigation, Sample processing Laboratory analysis, Data curation, Formal analysis, Writing – original draft, Writing – review & editing; Soma Das Sarkar: Maintenance of Vermicompost unit; Basanta Kumar Das: Conceptualization, Investigation, Funding acquisition, Overall guidance; Dhruba Jyoti Sarkar, Pranab Gogoi: Manuscript editing and laboratory analysis; Praveen Maurye, Tandrima Mitra, Anjon Kumar Talukder, Satabdi Ganguly: Sample
Data availability statement
All relevant data are within the manuscript and its Supporting Information files. The data are also in the process to link with organisational online data repository portal.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
The manuscript is the output of the Institutional Project No. FREM/17-20/14 of ICAR-Central Inland Fisheries Research Institute, Barrackpore, Kolkata and funded by the Indian Council of Agricultural Research, New Delhi, India. The schematic illustration of the waste to wealth concept of the present study has been performed using web-based graphical templates of BioRender (https://app.biorender.com/). The authors are grateful to Dr. Bimal Prasanna Mohanty, former Head, FREM Division, ICAR-CIFRI,
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