Biohydrogen Production from Industrial Effluents

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Biohydrogen Production from Industrial Effluents S. Venkata Mohan*, G. Mohanakrishna, S. Srikanth Bioengineering and Environmental Centre (BEEC), Indian Institute of Chemical Technology (IICT), Hyderabad-500607, India *Corresponding author: E-mail: [email protected]; [email protected]

1 INTRODUCTION The advent of the new century has witnessed an unchecked, overexploited use, and depletion of fossil fuels which has resulted in alarming environmental pollution and a steep rise in global warming causing an unusual increase in surface temperatures. Thus, the recognition and rapid development of alternative, renewable, carbon-neutral, and eco-friendly fuels is of paramount importance to fulfill the burgeoning energy demands. This has instigated more than ever rapid development of bioenergy to solve the looming energy crisis as well as to save the planet from the brink of an environmental catastrophe. Hydrogen (H2) has been considered as a sustainable energy carrier as it is clean (does not emit any toxic by-product or greenhouse gases), efficient (with a high-energy yield of 142 kJ/g; 2.75-fold greater than that of methane), and renewable. Currently, H2 is being produced mainly from fossil fuels, biomass, and water. H2 production through biological routes is considered as one of the opportunistic and sustainable ways to meet the future energy demand and to prevent fossil fuel-based environmental impacts. Biological approaches for producing H2 also facilitate the conversion of negative-value organic waste (Venkata Mohan, 2010, 2009).

2 BIOLOGICAL ROUTES OF H2 PRODUCTION Broadly, biological H2 can be produced through two main mechanisms: photosynthesis and dark fermentation. Photosynthesis is a light-dependent process, while dark fermentation (anaerobic) is a light-independent catabolic process (Venkata Mohan, 2010, 2009). Most of the biological H2 production processes are operated at ambient temperatures and pressures,

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22. BIOHYDROGEN PRODUCTION FROM INDUSTRIAL EFFLUENTS

regarded as less energy intensive and therefore considered as a potential alternative to the conventional physical/chemical methods usually opted for H2 production.

2.1 Photobiological Process Photobiological H2 production can be classified into direct biophotolysis, indirect biophotolysis, and photofermentation. Direct biophotolysis converts water into H2 and O2 in presence of sun light during photosynthesis (Figure 1). However, H2 production by photolysis of water is very slow due to the inhibition of hydrogenase activity by the oxygen released during photosynthesis (Miyake et al., 1999). In indirect photolysis, H2 generates through the biochemical reduction of organic compounds during Calvin-cycle. Photofermentation is a process where the organic acids/volatile fatty acids (VFA) such as acetate, butyrate, propionate, etc., are consumed as e donors for H2 production using light energy (Figure 1). Although hydrogenase activity is important nitrogenase activity is also crucial in this aspect. Light energy is not required for water oxidation in this case, and hence the conversion efficiency is higher compared to the photolysis (Miyake et al., 1999).

FIGURE 1 Schematic illustration of oxygenic and anoxygenic photosynthetic processes producing H2 in algae, cyanobacteria, and photosynthetic bacteria.

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Oxygenic photosynthesis occurs in algae and cyanobacteria, while anoxygenic photosynthesis is feasible in photosynthetic bacteria like purple sulfur (PSB) and purple nonsulfur bacteria (PNSB; Figure 1). During oxygenic process, photosystem II drives the first stage of the process by splitting water molecule into Hþ, e-, and oxygen. Electrons get transferred to the photosystem I through a cascade of proteins and are finally used in the Calvin cycle to fix CO2 into biosynthetic intermediates and storage compounds (Donald, 1995). Protons gets driven through ATPase and hydrogenase and reduced with the e from reduced ferridoxin (Fd) to produce H2 (Donald, 1995). In dark phase of process, the stored compounds are oxidized to form organic acids during respiration for energy generation. Hydrogenase catalyzes H2 production in both algae and cyanobacteria, while nitrogenase catalyzes the H2 production only in cyanobacteria (Donald, 1995). The function of hydrogenases in photofermentation is similar like acidogenic (dark) fermentation. However, both the hydrogenase and nitrogenase are sensitive to O2, and the inhibitory effect prevents the H2 production (Donald, 1995). In the case of cyanobacteria, oxygenic photosynthesis takes place in vegetative cells, while the nitrogen fixation along with H2 production takes place in heterocysts. Heterocysts have leghemoglobin which scavenge the O2 released during oxygenic photosynthesis and maintain low O2 concentration inside the cell, which increases the hydrogenase and nitrogenase catalytic activity for higher H2 production (Donald, 1995). PNSB has the advantage of being able to utilize various carbon sources, especially the short-chain fatty acids during anoxygenic photosynthesis (Shi and Yu, 2006) and are the most intensively studied anoxygenic phototrophs that produce H2. Anoxygenic photosynthetic bacteria obtain e from organic substrate but not from water and, therefore, the inhibitory effects of O2 on H2-producing enzymes can be avoided. Since the organic substrates were originally derived from CO2 fixed by green plants, anoxygenic photo-H2 production is carbon neutral. PNSB mainly depends on the nitrogenase, which is known for N2 fixation to NH3. In the absence of N2, nitrogenase acts as an ATP-powered hydrogenase, producing H2 exclusively, without feedback inhibition (Donald, 1995). The ATP required for this can be generated with a single e repeatedly energized through cyclic photophosphorylation to maintain Hþ gradient and thereby ATP levels. H2 production via nitrogenase has a specific activity but lower than [Ni–Fe] hydrogenase. Mo-nitrogenase has higher specific activity than the Fe-nitrogenase. Nitrogenase irreversibly catalyzes the reduction of molecular nitrogen to ammonium (nitrogen fixation) by consuming reducing power (e mediated by ferredoxin, NADþ, etc.) and ATP. H2 production catalyzed by nitrogenase is a side reaction at a rate of one third to one fourth that of nitrogen fixation. Nitrogen-fixing cyanobacteria are potential candidates for H2 production by nitrogenase, but it is an energyconsuming process due to breakdown of many ATP molecules (Donald, 1995).

2.2 Dark Fermentation Process Anaerobic conversion requires a series of four interrelated steps and five physiologically distinct groups of microorganisms to convert hydrocarbons from complex to simple molecules through H2 and acid as intermediates finally to carbon dioxide (CO2) and methane (CH4; Figure 2). Obligatory H2-producing acidogenic bacteria (AB) oxidize fermentation products to acid intermediates and H2, which also include acetate production from H2 and CO2 by acetogens and homoacetogens (Angenent et al., 2004; Venkata Mohan, 2009, 2010). Fermentative process starts with the conversion of glucose to pyruvate through glycolysis by both

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FIGURE 2 Schematic illustration of substrate conversion and H2 production mechanism during dark fermentation.

obligate and facultative anaerobic bacteria. Facultative anaerobes convert pyruvate to acetylCoA and formate catalyzed by pyruvate formate lyase (PFL) where H2 is produced from formate by the formate hydrogen lyase (FHL) complex. In obligate anaerobes, pyruvate is converted to acetyl-CoA and CO2 through pyruvate ferredoxin oxidoreductase (PFOR), and this oxidation requires reduced ferredoxin (Fd) which again depends on the redox condition (Venkata Mohan, 2010). Proton shuttling takes place between metabolic intermediates with the help of various redox mediators. The Hþ from the redox mediator is detached by a specific dehydrogenase (NADHdehydrogenase) and gets reduced to generate H2 in presence of the hydrogenase with the help of e donated by reduced ferredoxin (co-factor) (Venkata Mohan, 2010). Dehydrogenase enzymes are involved in the interconversion of metabolites and the transfer of Hþ between metabolic intermediates through redox reactions using several mediators (NADþ, FADþ, etc.; Venkata Mohan et al., 2010a; Venkata Mohan, 2009, 2010). Both dehydrogenase and hydrogenase activities are crucial to maintain Hþ equilibrium in the cell and to reduce them to H2. The basic functional differences between photo and dark fermentation processes are outlined in Table 1. During the initial phase of biohydrogen research, much attention was paid to the photobiological routes using specific strains and defined medium. Low rates of H2 production was observed because of the complex reaction system, inhibitory effect of O2 on hydrogenase and nitrogenase (Winkler et al., 2002), and lower utilization of waste (Srikanth et al., 2008, 2009; Venkata Mohan et al., 2008c) are some of the inherent

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TABLE 1 Functional Differences Between Dark and Photo Fermentation Processes as a Function of H2 Production Dark Fermentation

Photofermentation

Light is not required

Light is required

H2 production occurs during substrate degradation

H2 production occurs during substrate synthesis

Utilizes wastewater as substrate

High strength and toxic wastewater cannot serve as substrate

Acidophilic pH favors H2 production

Near-neutral pH is favorable

CO2 releases along with H2 generation

CO2 gets fixed to carbon source along with H2 generation

Hydrogenases class of enzymes involve in H2 production

Both hydrogenases and nitrogenases involve in H2 production

Absence of O2 favors hydrogenases activity

O2 generated during photolysis shows inhibitory effect on both hydrogenase and nitrogenase activity

Volatile fatty acids (VFA) are generated during acidogenesis along with H2

VFA can be a good substrate for H2 production

Reduced NADþ acts as proton source

Reduced NADPþ acts as proton source

H2 partial pressure is reduced through the reversible hydrogenases

H2 partial pressure is reduced through the uptake hydrogenase

disadvantages linked with the photobiological process. High activation energy to drive hydrogenase and the low solar conversion efficiencies are also considered as major limitations for this process (He et al., 2005). Dark fermentation process gained importance due to its feasibility of utilizing wastewater as substrate and using mixed cultures as biocatalyst. Dark fermentative process does not rely on the light, utilizes a variety of carbon sources such as organic compounds, wastes, wastewaters, or insoluble cellulosic materials, requires less energy, technically much simpler, requires low operating costs, and is more stable (Angenent et al., 2004; Venkata Mohan, 2009, 2010). Simplicity, efficiency, and lesser foot prints are some of the strong features of the dark fermentation process which makes it practically more feasible for the mass production of H2. Much of the literature reported on biohydrogen production concerned to wastewater utility was on dark fermentation process. On the contrary, photosynthetic bacteria can readily utilize the organic acids generated form dark fermentation process to produce additional H2.

3 BIOCATALYST Selection of appropriate biocatalyst or inoculum significantly influences the fermentation end-product formation. Initial reports on biohydrogen production are confined more towards the usage of pure cultures as biocatalyst with defined substrate. Diverse groups of microorganisms, viz. anaerobic (facultative and obligate), photoheterotrophic and microalgae are capable of producing H2 through the degradation of organic substances. Bacteria capable

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of producing H2 are reported to distribute across 10 of the 35 bacterial groups (Nandi and Sengupta, 1998) and widely exist in natural environments such as soil, cow dung, anaerobic sludge, municipal sludge, compost, etc. which can be used as inoculum. Obligate anaerobes, thermophiles, rumen bacteria, methanogens, and few types of facultative anaerobes were reported to produce H2. Production rate of H2 was comparatively lower in the case of facultative anaerobes (Chong et al., 2009). When aerobic condition prevails, facultative anaerobes consume O2 and then switch to anaerobic fermentation which favors H2 production (Chong et al., 2009). Obligate anaerobes, categorized as mesophiles and thermophiles, are able to produce H2 in the pH range of 4-7 (Chong et al., 2009). Species of Clostridium sp, Thermoanaerobacterium sp, Caldicellulosiruptor sp, Actinomyces sp., Porphyromonos sp, etc. are obligate anaerobes, whereas the species like Escherichia coli, Enterobacter, Citrobacter, Klebsiella, etc. come under facultative group were reported to produce H2 (Chong et al., 2009). H2 production from wastewater has more significance where mixed cultures are used as biocatalyst with diverse biochemical functions. Recently, much focus is observed on the use of anaerobic microflora enriched from various sources. From the view of engineering aspects, mixed cultures are usually preferred because of low cost, operational flexibility, diverse biochemical functions, stability, and possibility of using of wider range of substrates (Wang and Wan, 2009). Moreover, mixed culture operation restricts the sterile requirement (Angenent et al., 2004; Venkata Mohan, 2010).

3.1 Pretreatment of Biocatalyst Shifting or regulating the metabolic pathway towards acidogenesis and inhibiting methanogenesis facilitates higher H2 yields (Srikanth et al., 2010b; Venkata Mohan, 2009, 2010). Pretreatment of biocatalyst plays a vital role in the selective enrichment of mixed consortia for the metabolic shift towards acidogenesis (Venkata Mohan et al., 2008e, 2009b; Venkata Mohan, 2009, 2010; Zhu and Beland, 2006). Typical anaerobic mixed cultures are unable to produce higher H2 as it gets consumed by the H2-consuming methanogenic bacteria (MB). Effective way to enhance H2 production from anaerobic culture is to restrict or to terminate methanogenesis by allowing H2 to become a metabolic end product. Unique function and physiological difference between AB and MB forms the main criterion for the preparation of the biocatalyst (Venkata Mohan et al., 2008e; Zhu and Beland, 2006). H2-producing bacteria can form spores which protect them, in adverse environmental conditions (high temperature, extreme acidity and alkalinity), but methanogens lack such capability (Venkata Mohan et al., 2008e; Zhu and Beland, 2006). Various methods for the biocatalyst pretreatment are reported (Venkata Mohan et al., 2007b; Venkata Mohan, 2008, 2009, 2010; Wang and Wan, 2008a). Some of the reported pretreatment methods used and their functional property on microorganism are listed in Table 2. Different pretreatment methods have different functional property and comparison of such pretreatment methods helps to obtain an efficient pretreatment method (Wang and Wan, 2008a). Combining different pretreatment methods also showed a positive effect on H2 production process (Srikanth et al., 2010b; Venkata Mohan et al., 2007d, 2008f; Venkata Mohan et al., 2008e, 2009b). Untreated consortia have higher bacterial population with a wide variety of biochemical functions facilitating diverse metabolic activities. On the contrary, pretreatment facilitates the selective enrichment of bacterial population leading to less diversity in their biochemical functions towards acidogenesis

4 RENEWABLE WASTEWATER

TABLE 2 Pretreatment Method

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Pretreatment Methods Used to Enrich Biocatalyst for H2 Production Conditions

Function

Acid

Extreme acidic microenvironment (pH < 4)

Enrich spore-forming bacteria by specifically suppressing the MB.

Alkaline

Alkaline microenvironment (pH > 9)

Nonspecific inhibition of MB

Heat shock

Extreme temperature (>80 C)

Suppress non-spore-forming bacteria and helps to harvest spore-forming bacteria.

Load shock

In the presence of higher substrate concentration

Leads to the accumulation of high organic acids which prevents MB growth

Oxygen shock

In the presence of oxygen/air (0.5 mg/l)

MB are obligative anaerobes, exposure to oxygen lowers their adenylate charge and leads to death

Chemical

2-bromoethanesulfonic acid (BESA,100 mmol)

Inhibits coenzyme-M reductase complex (chief component for methanogenesis)

Iodopropane

Iodopropane is a corrinoid antagonist that prevents the functioning of the B12 enzymes as a methyl group carrier

Acetylene


KNO3 (10 mmol/l)


Combination of two or more pretreatment methods

To achieve more specific enrichment of AB

Combined

(Srikanth et al., 2010b). Untreated consortia support Hþ reduction during methanogenesis rather than the interconversion of metabolites, which is presumed to be necessary for H2 production (Srikanth et al., 2010b). In spite of the improved H2 production, marked reduction in the substrate degradation was observed after using the pretreated cultures (Srikanth et al., 2010b), which can be attributed to the inhibition of MB.

4 RENEWABLE WASTEWATER Wastewater is being produced continuously and has been increased in volume with time due to industrialization. Remediation of wastewater being energy intensive adds up the expensiveness and increases the economic burden on the industry. Reducing the treatment cost and finding ways to produce useful products from wastes such as H2 have been gaining importance. The biodegradable organic fraction present in wastewater associated with inherent net positive energy makes it as an ideal candidate for H2 generation. Generation of bioenergy from renewable wastewater with simultaneous treatment reduces the overall cost and makes the whole process environmentally sustainable (Venkata Mohan, 2009, 2010). Technical feasibility, simplicity, economics, societal needs, and political priorities are some of the vital aspects considered to choose the bioprocess that will be used to treat wastes in

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the future (Angenent et al., 2004). Availability of large quantities of wastewater, presence of degradable carbon material, cost and the need for their treatment make them a potential substrate for producing H2 (Venkata Mohan, 2009, 2010). Table 3 depicts some of the reported studies where wastewater was used as substrate to generate H2 by biological routes. TABLE 3

Various Types of Wastewater Used as Substrates for H2 Production

Type of Fermentation

Industry Category

Dark

Food processing industry

Dairy-based industries

Alcoholbased industries

Plant/ Agriculturalbased waste

Type of Industrial Wastewater

References

Food processing wastewater

Van Ginkel et al. (2005), S¸entu¨rk et al. (2010), Zhu et al. (2009a)

Coffee manufacturing wastewater

Jung et al. (2010)

Tofu wastewater

Kim and Lee (2010), Kim et al. (2010)

Starch-based wastewater

Chen et al. (2008), Zhang et al. (2003)

Citric acid wastewater

Yang et al. (2006)

Slaughterhouse waste

Go´mez et al. (2006)

Sweet sorghum syrup/extract

Saraphirom and Reungsang, (2010), Antonopoulou et al. (2008, 2010)

Liquid swine manure

Wu et al. (2010), Zhu et al. (2009b)

Dairy processing wastewater

Venkata Mohan et al. (2007a, 2008e), Gustavo et al. (2008), Ren et al. (2007)

Dairy waste permeate/ waste lactose

Banks et al. (2010)

Cheese processing wastewater

Ferchichi et al. (2005), Yang et al. (2007)

Cattle wastewater

Tang et al. (2008)

Brewery wastewater

Chang et al. (2008), Shi et al. (2010)

Wine process wastewater

Yu et al. (2002), Froylań et al. (2009)

Molasses-based wastewater

Venkata Mohan et al. (2008f), Vatsala et al. (2008), Lay et al. (2010)

Vinasse

Buitroń and Carvajal (2010), Fernandes et al. (2010)

Vegetable-based market waste

Mohanakrishna et al. (2010a)

Paper mill waste

Idania et al. (2005), Lakshmidevi and Muthukumar (2010)

Lignocellulose-derived organic acids

Zhu et al. (2010)

Wheat straw hydrolysate

Kongjan and Angelidaki (2010)

Cassava stillage

Luo et al. (2010a,b), Sreethawong et al. (2010)

Citrus peelings

Venkata Mohan et al. (2009a)

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TABLE 3

Various Types of Wastewater Used as Substrates for H2 Production—Cont’d

Type of Fermentation

Industry Category Organicbased industries

Oil-based industries

Others

Photo

Type of Industrial Wastewater

References

Phenol-containing wastewater

Tai et al. (2010)

Organic wastewater

Show et al. (2010)

Chemical wastewater

Venkata Mohan et al. (2007b,c,d, 2010d), Vijaya Bhaskar et al. (2008)

Glycerin from biodiesel production

Fernandes et al. (2010), Liu and Fang (2007)

Palm oil mill effluent (POME)

Vijayaraghavan and Ahmad (2006), Wu et al. (2009)

Olive mill wastewater

Ntaikou et al. (2009)

Landfill leachate

Liu et al. (2010), Hafez et al. (2010)

Filtrate of activated sludge

Guo et al. (2010)

Probiotic wastewater

Sivaramakrishna et al. (2009)

Olive mill waste

Ena et al. (2010), Eroglu et al. (2010)

Potato steam peels hydrolysate

Afsar et al. (2010)

Sugar refinery wastewater

Yetis et al. (2000)

Dairy wastewater

Venkata Mohan et al. (2008), Srikanth et al. (2008), Seifert et al. (2010)

Tofu wastewater

Zheng et al. (2010), Zhu et al. (2002)

Ground wheat solution

Argun et al. (2009)

Starch fermentation

Laurinavichene et al. (2008)

The composition of the microbial community survived in the long-term operated anaerobic sequencing biofilm reactor producing H2 from the treatment of various types of wastewaters showed significant diversity (Venkata Mohan et al., 2010d; Figure 3). Major nucleotide sequences were affiliated to Class Clostridia followed by Bacteroidetes, Deltaproteobacteria, and Flavobacteria. Long time operation with diverse operating conditions might have resulted in the survival of robust and selectively enriched bacteria which are capable of producing H2 under acidogenic conditions. Almost all the microbial community structure analysis showed the presence of clostridium as dominant group. Clostridia (gram positive, rod shaped) associated with Firmicutes group are obligate anaerobes capable of producing endospores and also able to survive at nutritional limiting conditions and even at higher temperatures.

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FIGURE 3 Neighbor-joining tree representing microbial diversity of long-term operated anaerobic reactor producing H2 (constructed using Mega 4.0) showing closely related phylogenetic relationships of 16S rDNA from Gene Bank (Venkata Mohan et al., 2010d).

5 FACTORS INFLUENCING H2 PRODUCTION 5.1 Redox Condition Redox condition is especially important for fermentative H2 production process where the activity of AB is considered to be crucial and rate limiting (Fan et al., 2006; Venkata Mohan et al., 2008a; Venkata Mohan, 2009, 2010). Based on the organisms and their growth conditions, changes in external pH can bring about alterations in several primary physiological parameters,

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including the internal pH, concentration of other ions, membrane potential, and proton-motive force. Redox condition also influences the efficiency of substrate metabolism, protein and storage materials synthesis, and release of metabolic byproducts. Under acidic conditions, pyruvate converts into VFA along with H2 by AB. Neutral operation leads to the formation of CH4 and CO2 by MB, while basic operation leads to solventogenesis. Repression of MB indirectly promotes H2 producers within the system (Venkata Mohan et al., 2007d, 2008e; Zhu and Beland, 2006). AB functions well below pH 6, while for MB optimum range is between 6.0 and 7.5 (Venkata Mohan, 2010, 2009). The pH range of 5.5-6.0 is reported to be ideal to avoid both methanogenesis and solventogenesis (Venkata Mohan et al., 2007d, 2010a; Venkata Mohan, 2009, 2010). Good H2 yield was observed by maintaining pH in and around 6 compared to near-neutral pH (van Ginkel et al., 2001; Venkata Mohan et al., 2007d; Venkata Mohan, 2010). However, highly acidic pH (0.6 V) (Srikanth et al., 2010a). Hydrogen was successfully produced from various substrates such as cellulose, glucose, VFA, proteins, swine, waste water, and also with the effluents collected from the ethanol-H2 fermentative reactor (Cheng and Logan, 2007). This process makes possible to generate H2-utilizing effluents generated from acidogenic fermentation (Wagner et al., 2009). Multielectrode MEC was also reported for the continuous production of biogas (Rader and Logan, 2010).

9 FUTURE OUTLOOK Nonutilized residual organic fraction remaining as a soluble fermentation product after acidogenic process is one of the most important aspects to be paid significant attention. Various routes to utilize this residual organic fraction of acidogenic process as substrate need to be explored. Multiple process integration approaches towards the utilization of wastewater effectively and completely with simultaneous bioenergy recovery are to be evaluated for economic viability of the process and commercialization. Controlling the system redox conditions (buffering capacity) leads to protest from the persistent acidophilic microenvironment due to soluble acid intermediates and thus resulting in increased H2 yields. Photobiological processes especially with wastewater as substrate have not yet been fully exploited and are relatively less studied. Photosynthetic culture has the advantage of high substrate conversion efficiency to H2 because of its ability to mineralize glucose to CO2. The potential of photosynthetic culture in utilizing wastewater directly as well as the dark fermentation effluents should be evaluated. Photosynthetic sulfur and nonsulfur bacteria can be considered and evaluated with sulfur-containing wastewater where they can utilize different forms of sulfur as electron donor. Process engineering, understanding biochemistry and microbiology aspects based on functional role of membrane components and mechanism of proton reduction, community analysis, culture development aspects, design and development of bioreactor systems for dark and photofermentation operations are some of the key areas where considerable focus is required. Metabolic engineering is one of the promising areas which can be advantageously used to enhance H2 production rate using recombinant DNA technology. Developing a process to convert existing/operating anaerobic reactors producing methane to H2 production will pave way for large-scale implementation of this technology. Biohydrogen technology requires

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multidisciplinary research to make the process environmentally sustainable and economically viable.

Acknowledgments Author thanks the Director, IICT, for his encouragement and acknowledges the inputs of A Kiran Kumar, S Veer Raghavulu, G Velvizhi, M Prathima Devi, M Lenin Babu, R Kannaiah Goud, M Venkateswar Reddy, G Venkata Subhash, K Chandra Sekhar, Rashmi Chandra, and P Chiranjeevi. This work was supported by Ministry of New and Renewable Energy (MNRE), Government of India in the form of National Mission Mode project on Biohydrogen production [No. 103/131/2008-NT].

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