eChapters

Energy is a critical component of the economic infrastructure, as it is the primary input required to support economic growth. Economic development and energy use have a close relationship. The higher a country’s per capita energy usage, the more developed it is and vice versa. Human civilization is dependent on several energy sources.

Definitions of Energy

Energy is a key topic in science and technology, as well as in society in general. In terms of energy, a typical definition found in popular literature as well as textbooks is “energy is the ability to do work” or, much more precisely, “energy is the capacity of a system to do work” [Atkins 1990].

Energy is described as the ability to generate change or carry out work, and that work can be separated into numerous easily identifiable tasks: Energy produces light, heat, motion, sound, growth, power and technology etc.

Energy in Agricultural Context (FAO)

Agriculture’s fundamental and foremost function is to produce food and other primary products, so contributing to food and nutritional security. Sustainable Agriculture and Rural Development (SARD) attempts to promote ecologically non-degrading, technically suitable, commercially successful, and socially acceptable development in the agriculture, fishery and forestry sectors. Achieving food security necessitates policies that promote social, cultural, political, and economic stability. Integrating agriculture’s economic, social, and environmental roles can help to attain these objectives.

Agriculture may provide a variety of non-food commodities and services. This can include its application as a viable, long-term source of energy. According to the FAO, agricultural activities and related land use directly contribute to non-agricultural functions such as social, environmental, economic and cultural products and services. They can have major advantages or disadvantages. Research reveals that, in addition to food security, agriculture contributes significantly to attaining sustainability at the local, national and global levels in rural development, energy and the environment. The efficient operation of the market encourages the identification and strengthening of these many functions, as well as the development of new techniques and technologies. Plant and crop-based resources are utilised as raw materials in a wide range of industrial goods, including wood for paper and board production, starches for adhesives, and vegetable oils for paints and resins.

Healthcare represents one of the most promising yet sensitive application domains for Large Language Models. LLMs can process extensive medical literature, electronic health records, clinical narratives and other forms of biomedical information to support diagnosis, research and patient care. This chapter explores the growing role of LLMs in healthcare, beginning with their development from general language models toward specialized biomedical and clinical systems. It examines applications in disease diagnosis, clinical decision support, medical documentation, literature analysis, drug discovery and personalized medicine. LLMs can assist with differential diagnosis, symptom extraction, medical question answering, clinical trial matching and interpretation of medical information. In drug discovery, they can analyze scientific publications, patents and clinical evidence to identify potential drug candidates, targets and opportunities for drug repositioning. Personalized medicine applications involve integrating genetic, lifestyle and treatment-response information to support patient-specific therapeutic decisions. At the same time, the chapter emphasizes major concerns involving patient privacy, hallucination, explainability, regulatory compliance and human oversight. The discussion highlights the importance of responsible integration of LLMs with clinical expertise and established healthcare practices

Precision agriculture uses spatially and temporally variable information to improve crop management, resource efficiency and agricultural productivity. This chapter examines the integration of artificial intelligence throughout the precision agriculture workflow. It introduces variable-rate technologies, georeferenced data collection and decision-support systems, followed by machine learning, deep learning, computer vision, reinforcement learning, fuzzy logic and expert systems. Applications include crop yield prediction, plant disease monitoring, soil property estimation, irrigation planning and autonomous agricultural operations. Remote sensing, satellite imagery, IoT sensor networks and edge computing are considered for real-time decision-making. The chapter also discusses agricultural robots and autonomous machinery, practical field applications, data limitations, hardware costs, connectivity and model interpretability.

Artificial Intelligence (AI) is becoming an important tool for addressing complex challenges in plant science and agriculture. This chapter introduces the fundamental concepts, methodologies and emerging paradigms of AI applied to plant research. It discusses machine learning, deep learning, convolutional and recurrent neural networks, and transformer architectures, with applications in plant phenotyping, disease diagnosis, genomics and precision agriculture. Different data modalities, including imaging, LiDAR, remote sensing, genomic sequences and metabolomics, are examined. The chapter also considers transfer learning, data augmentation, explainable AI, graph neural networks, federated learning and multimodal AI, together with challenges, ethical issues and future research directions

Abstract

The increase incidence of plant diseases have created challenging troubles in commercial agriculture and posed economical threats to both conventional and organic farming systems. To combat these problems there has been indiscriminate use of the synthetic chemicals that created different types of environmental and toxicological problems. Therefore attention has been directed towards exploitation of plant products or phytoextracts as novel chemotherapeutants in plant protection. Numerous botanical pesticides have been used globally and more has been discovered in due course of time. Pyrethroids, neem, etc are well established commercially as botanical pesticides and recently some essential oils of higher plants have also been used as antimicrobials as they are safe and widely accepted by the consumers. Use of phytoextracts may thus offer a new source of antibacterial, antifungal and antiviral agents against microorganisms. Botanical pesticides are best fitting for organic food production in industrialized countries and can plays greater role in the production and post-harvest protection of food products in developing countries.

Abstract 

A field investigation entitled, “Studies on growth and yield of aerobic rice in summer season under various moisture regimes and planting techniques in upland condition” was carried out at Regional Research Station, Gayeshpur, Nadia, West Bengal of Bidhan Chandra Krishi Viswavidyalaya. The field experiment was laid out in a split plot design with three replications. The treatment consisted of three irrigation regimes in main plots viz., IW/CPE =1.0, IW/CPE =1.5 and IW/CPE = 2.0 and four treatments on planting techniques in sub plots viz., P1: Sprouted seeds, P2: Non-sprouted seed, P3: Soaking seeds overnight (12 hrs), P4: Soaking seeds overnight (12 hrs) followed by shade drying.

Abstract
 
The word “sustain” is derived from the Latin verb ‘sustinere’(to keep in existence or maintain) and implies long-term support or permanence. The accepted definition of sustainable agriculture has proved to be elusive, given the extraordinary diversity and complexity of agricultural land use, and the perspective taken including producers, consumers, policy makers and workforces. Sustainable agriculture is defined as ‘the ability of farmland to produce food grain and other agricultural products to satisfy human needs indefinitely as well as having sustainable impacts on the broader environment and maintained equilibrium in productivity level’. That in other words, requires agriculture to avoid severe or irreversible damage to the endogenous or external ecosystem services upon which it depends, notably soil fertility, irrigation water, genetic variability and pollinating agencies and have acceptable impacts on the broader environment under the environmental stewardship.

ABSTRACT
Increased environmental pollution and high demand over supply for conventional fossil fuel sources have led to the exploration of other renewable energy sources. Out of the potential alternatives, methane has come up with a promising unconventional fuel source. Several technologies have been developed to establish methanation, including biomethanation, chemical methanation and gas-to-liquid technology. Several factors like process parameters, catalysts and reactors have been studied for process optimisation and making methane production commercially viable. Although methane as a greenhouse gas is a contributor to global warming, its combustion produces relatively ‘environment friendly’ gas CO₂, and H₂O. The released CO₂ is fixed into biomass by plant through photosynthesis process. Only rarely does methane combustion produces CO when combusted in an oxygen-limited condition. Thus, methane production and combustion are carbon neutral process. This chapter focuses on the application of methane as a source of alternate energy. Various technologies used, recent advances and challenges faced in methanation process are discussed.

Abstract

The bio-drainage system used to control the water logging hazards and restore the ground water table depth at a level favourable for other crops to grow. The water utilization efficiency per unit area of land improved through bio-drainage and associated cropping activities. The huge quantity of shallow and good quality groundwater that remains perpetually unutilized by the prevalent lowland cultivation system was effectively used by the biological drainage system. Thus the bio-drainage is expected to alleviate the land degradation problem due to high depth of water stagnant, to restore the crop cultivation programme on a sustainable way, to improve the water management practices, to improve the economic conditions of the lowland farmers and finally, to conserve the ecological values of this fragile agro-ecosystem.The objectives of efficient bio-drainage system are to evaluate ET and depended on growth characteristics of different trees and vegetation species having bio-drainage potential in the waterlogged land thereby to study the water table behaviour in the land under plantation and in the surrounding region and use the result in developing suitable plantation geometry to ensure desired water table draw-down, to assess interaction between bio-drainage plantation and co-existing crops and/or companion crops, to assess the value of the tree species through fodder, fuel wood and timber use, and to development of a new technology for land reclamation and evaluating its impact on soil, water and plant bodies in the basin.

Abstract
 
Adoption of agricultural practices is cost effective bioremediation techniques to mitigate arsenic problems and can contribute substantially to the cause of removal of arsenic and other heavy metal contamination of soils and water thereby quality enrichment in marketable agricultural produce leading to increased crop productivity in the area of intensive cropping under irrigated eco system. Though the farmers are already practicing some traditional techniques to mitigate the arsenic problems in soils and water, like cultivation of crops which are less affected to arsenic and heavy metals pollution, growing hyper accumulating crops and so many practices wherein the modern methods are not prevalently used by the farmers due to the lack of scientific validity of these techniques, particularly in the context of prevailing socio-economic conditions. Moreover, acceptance of these improved practices by the small farmers of this region is an evolutionary process and should be intensively proved. Hence, extensive studies need for bio or phyto-remediation of heavy metals including arsenic contamination for quality marketable agricultural produce, which ultimately can realize better crop productivity.

ABSTRACT
Methanogens are primarily anaerobic Archaebacteria representing the most primitive earthly creatures, alive since about 3.5 billion years. While oxygen inhibit their activity, they adapt well in a variety of ecological niche, viz., the intestinal tracts of insects and animals including ruminants, sewage digesters, groundwater and deep soil/water, etc. They are involved in biomethanation that converts organic polymers, including the complex recalcitrant lignocelluloses, to CH₄ and CO₂. Enhancing the process by optimising the physical, chemical and molecular parameters is an interesting biotechnology. Molecular research is rapidly progressing on the genomics, gene and its regulation, and methanogenesis as it expresses. Identifying novel species expressing methanogenesis and manipulating the genetic make-up including through cloning in recent years will set goals and leads for future investigations. The biomethanation enzyme Methyl-CoM-reductase (Mcr) constitutes about 10% of the methanogen protein. Due to its abundance and significance, elucidating its structure and its synthesis and regulation mechanism has received much attention recently. Mcr-coding genes from methanogens have been cloned and sequenced. An approach at the molecular level to enhance biomethanation seems to lie in metagenomics. The microbiology, biochemistry, the roles of the participating microbes, their molecular biology and applications in methanogenesis are discussed in this chapter.

ABSTRACT
Biomethanation comprises of four interdependent stages in series, hydrolysis, acidogenesis, acetogenesis and methanogenesis. Methanogenesis, the final stage of biomethanation, is accompanied with the reduction of substrates that include organic acids such as CH₃COOH, and others such as CO₂ and CH₃OH to CH₄ by methanogenic and methanotrophic archaea, usually under anaerobic conditions. Strictly anaerobic methanogenic archaea are found in the ruminant intestine, sewage digester, groundwater and deep soil/water etc. In methanogenesis, H₂ acts as the electron donor while substrates CO₂, CH₃OH and probably CoM-S-S-CoB (for CH₃COOH) act as terminal electron acceptors and reduce to methane, a process known as anaerobic respiration. This conversion is associated with the electrogenic proton motive force along with sodium motive force to drive the ATP synthesis by A0A1 ATP synthase, known as respiratory phosphorylation. The mechanism of conversion of methane from CO₂ by methanogens with cytochromes is same as those without cytochromes except that the reduction of heterodisulphide CoM-S-S-CoB is performed by the membrane-bound VhoACG-HdrDE complex for former while by cytoplasmic MvhADG–HdrABC complex for the later.

ABSTRACT
Recent challenges for fossil fuels, associated environmental issues with disposal of organic garbage, and the rising costs for energy has encouraged researchers to search for alternate energy sources. Massive uncontrolled biogas from landfills, sludge and organic material degradation under anoxic conditions is an environmental management issue. Methane emission to atmosphere has a tremendous green house effect, but this can also be a valuable renewable energy resource. Biogas from kitchen wastes through anaerobic digestion by methanogens is such an alternate technology. Kitchen wastes are considered one of the best raw materials for biogasification. Biogas is mainly composed of 50-74% methane (CH₄), 25-28% carbon-di-oxide (CO₂), other volatile compounds including hydrogen sulphide (H₂S), water vapour and other trace gas compounds. The impurities in it, like Hydrogen sulphide (H₂S) which is corrosive, downgrade its quality. Purified biogas of higher calorific value attracts attention as a substitute fuel for additional applications. Its purification using various suitable scalable and economically-viable scrubbing technologies to enhance its quality and performance as an alternate fuel is an important step in this direction. Thus, a technology to generate and purify biogas from kitchen waste has significant prospects in the energy sector, and also as a promising enterprise to employ the youth.

ABSTRACT
There is a quantum global growth in both number and size of dairy industries in recent times. These industries discharge thousands of liters of wastewater characterised by a heavy chemical oxygen demand (COD), biological oxygen demand (BOD), nutrients, inorganic salts, besides detergents and sanitisers each day (Kushwaha et al., 2011). High carbohydrates, fats and proteins contents in such waste streams originating from milk pose challenge to conventional municipal sewage treatment systems (Demirel et al., 2005). The easily biodegradable dairy effluent leads to precipitation of casein which is toxic and has a strong odour. Without adequate treatment, these effluents could pose serious threats to the receiving water bodies and disturb the ecosystem (Satpathy et al., 2017). For such heavily loaded organic effluents, biogasification through anaerobic digestion seems a promising strategy. This cost-effective energy generation process is also effective in environmental management compared to its other eco-friendly renewable source counterparts, such as, hydro, solar and wind (Satpathy, 2017). The Upflow Anaerobic Sludge Blanket (UASB) reactors are the most popular anaerobic systems to treat the fluctuating organic loads in dairy effluents. Anaerobic filter (AF), Upflow Anaerobic Filter (UPAF), Fixed-bed anaerobic reactor, Anaerobic Hybrid Reactor (AHR) etc. are few other systems that are demonstrably competent removing COD upto 90% and generating biogas. Successful anaerobic systems reported yielded (with upto about 85% CH₄ content) 0.32-0.34m3 CH₄/kg COD removed. Biomethanation process and reactors designs are constantly being optimised for effective treatment of the effluents while maximising the biogas production. The energy-rich gas thus obtained could further be utilised for heat and electricity at the domestic level, and also as a vehicular fuel. Residual digestate can also be used as organic manures (Angelidaki et al., 2007).

Abstract

Biological drainage relies on vegetation, rather than engineering mechanisms to remove excess soil water through evapo-transpiration. It is often considered attractive because it requires only an initial investment in site development (planting of a “bio-drainage crop”) and (potentially) returns a benefit when the bio-crop is harvested for fodder, wood or fibre. Presently about one-third of the world’s irrigated area faces the threat of waterlogging. Considering long-term viability of bio-drainage, the systems would be subjected to the same scrutiny as other plant-based biological systems with regards to nutrient and salt-balance and soil considerations. Moreover, large-scale adoption of bio-drainage crops could include considerable tracts of land and socio-economic considerations.

ABSTRACT
Rice straw is one of the most abundant lignocellulosic agricultural wastes in India and can be used as a major resource for biogas production. The structure of rice straw is complex and is made up mainly of cellulose, hemicelluloses and lignin. The lignin physically shields the cellulose and hemicelluloses, the main components which can be converted to energy, and hinders the access of microbial enzymes to these carbohydrate moieties. To overcome this making the straw a potential resource of biogas production, effective pretreatment is necessary that can efficiently hydrolyse the straw and make it accessible to cellulolytic enzymes and methanogens. Various pretreatment methods which are employed currently in the market are discussed here. For a process to be economically feasible it is necessary that the pretreatment be efficient as well as cost effective. To gain some insights into this aspect, the techno-commercial feasibility of Biomethanation of rice straw has been discussed.

ABSTRACT
Nisargruna biogas technology has been developed in BARC for processing different types of biodegradable waste. This technology is based on biphasic separation of aerobic and anaerobic stages. Introduction of aerobic predigester has increased the efficiency of the process in terms of enhancing the quality and quantity of methane and also reducing the retention time of the process. Process parameters of the plant were studied and found that the modified design has proved very effective in faster digestion of complex waste. The technology has been commercialised and has spread across different parts of country for processing variety of wastes including kitchen waste, municipal waste, agriculture waste, textile waste and poultry waste. Microbial population from different stages of the plant was also studied and found their ability to convert waste to biogas, containing mainly methane.

Keywords: biogas, biphasic digestion, green energy, methane, microbial fermentation, Nisargruna, waste management

Abstract

A field experiment was conducted in an aericendoaquept (pH, 6.67; organic carbon,  CEC,) to study the relative efficiency of different organic manures on the changes in some selected soil properties growing rape (cv. B-9) in a randomised block design replicated thrice using different combinations of organic and inorganic chemical fertilizers (T1- NPK 100%, T2- Compost 100%, T3- Compost 50% + NPK 50%, T4- Vermicompost 100%, T5- Vermicompost 50% + NPK 50%, T6- FYM 100% and T7- FYM 50% + NPK 50%). However, the objectives of the study was to assess the relative efficiency of organic manures with respect to availability of nutrients in relation to yield of rape affected by combined application of organic manures and chemical fertilizers. The results show that the amount of available N, organic carbon content, CEC and K contents were found highest in the treatment T5 where Vermicompost 50% + NPK 50% was applied combinedly.