PROMOTION OF PHOTOBIOREACTORS VIA THIRD AND FOURTH GENERATION ENGINEERED ALGAE AS A BIOFUEL SOURCE William Smith (WDS10@pitt.edu), Nasir Sharaf (NAS155@pitt.edu) Abstract— At the dawn of the new millennium it became quickly apparent that we globally could not meet the energy demands of the ever increasing population at the current rate of consumption. Clearly alternative fuel sources must be examined in order to provide sustainable energy for future generations. One possible source of fuel rests in oil-producing algae. Certain algae produce oil naturally and efficiently and thus are an obvious potential source for meeting humanity’s fuel needs. One issue is providing an environment for the growth and cultivation of biofuel producing algae. A solution is found through bioreactors. This paper will describe and evaluate appropriate bioreactor technologies, specifically those in photobioreactors (PBRs). The engineering and technologies of systems especially appropriate for biofuel-producing algae will be described and explained. The value of technologies and systems in use will be assessed, and the direction and value of current research and development of PBRs with particular applications to biofuel-producing Algae will be discussed. Key Words- algae, biofuel, bioreactors, fourth-generation, oilgae, Photobioreactors WHAT ARE PHOTOBIOREACTORS AND WHY ARE THEY IMPORTANT? As the year 2000 ushered in, the world and the U.S. faced a new range of unique, energy-related problems that they are still dealing with. These include the rising price of oil, the energy crisis, and the possibility of global warming. As a result of the environmental and economic implications of these growing issues, alternative fuel sources have been suggested as an attempt to mitigate the detrimental effects of the U.S. dependence on petroleum based fuel. Algae for oil production have been suggested [1] to best handle these ever present and rising problems and bioreactors have been suggested to best grow algae. But what is a bioreactor? A bioreactor is defined as a system that supports and maximizes biological processes. By extension, a photobioreactor also supports and maximizes biological processes by incorporating light. Admittedly, this is a rather broad definition, but still stands as legitimate because such a definition accounts for varied natural phenomenon such as calf stomachs, ponds, airlift reactors, membrane reactors, and termite guts [2] to be rightly included as bioreactors. In fact, as this paper will detail further, a pond (known as an open system) is one type of bioreactor that could potentially mass-produce algae [3]. The first half of this paper will continue to clarify and define what photobioreactors are, and the second part will aim to answer the question “why must photobioreactors be accessed to grow algae?” BIOREACTOR DESIGN In order to fully develop a definition for bioreactors and understand its intricacies, the hardware of a photobioreactor must inevitably be discussed. However, by how we previously defined bioreactors (and by extension photobioreactors) we cannot make any conclusive, definitive statements about bioreactors. We must limit our scope then to discussing bioreactors only used by industries. This will mean open systems, such as ponds, will still be included for discussion but natural phenomenon such as calf stomachs can be disregarded. This still leaves discontinuities as to what physically constitutes as a PBR since each reactor is different. For example, a vertical tubular biocoil design has to be fitted multiple external components including a heat exchanger, airlift, and back flow system while concentric loop airlift PBRs and Carboy PBRs had to be fitted with only a magnetic stirrer [4]. Although the physical structures vary with each type of PBR, all PBRs must accommodate for certain factors which in turn influences the design of the reactor. Instead of addressing the technical differences between every type of design, it would be far wiser to address the design theory that goes behind every PBR and how this theory is applied to various designs. After discussing the intimacies of design theory, this paper will examine “case studies” of flat panel, annual, and tubular designs [5]. General Design and Overview Photobioreactors are designed to maximize biological processes which in this paper are stringent on the proper growth and maturation of certain algal species. This means factors such as light, nutrient supplies, CO2, O2, pH, and temperature, among many other concerns, must be balanced perfectly to maximize algal growth and development [1]. With regards to light, an optimal reactor enhances light intensity, light penetration, the wavelength of light, and frequency of cell exposure to light. Mixing helps distribute radiation evenly to all the cells, and also allows the cells to evenly get the various nutrients they need. The algae also needs CO2 at faster rate than the simple diffusion from the Nasir Sharaf William Smith air to the medium and must similarly dispose of the excess O2 which is a byproduct of photosynthesis [6]. This is also accounted for through mixing. There are many more factors that can effect algae growth, but addressing everyone merits a paper unto itself. For simplicities sake, we will keep these discussed factors in the back of our minds and continue on to more the more pressing concerns of bioreactor design As alluded to previously, there are two species of systems, open and closed. Open systems include ponds, ponds fitted with rotating mechanisms, and raceway ponds (ponds designed to continue the flow of the algae) [1]. Open systems, like closed systems, must be attached to a harvesting system. Open systems present several technical issues such as preventing contamination and maintaining a mono-cultured environment which is just another added challenge on top of maximizing production, sometimes in the face of predation. Evaporation also has been known to offset production estimates [1]. In essence, the primary fallacy with open systems can be summed up as lack of control over the process. Closed systems are generally limited to (at least in the scope of this paper) devices containing the algae and the materials necessary to produce biofuels. Closed systems offer the advantages of control over the entire process, but are often stated to be more financially costly. Nevertheless, the potential for lowered costs in the future have generated interest in closed systems as the major choice for biofuel production [1]. Closed systems can be further divided into closed outdoor systems and closed indoor systems. Closed outdoor systems offer the advantages of maintaining a monoculture, increased biomass concentration for easier harvesting, and control over certain features like pH and CO2 levels [6]. Closed indoor systems offer greater control over environmental stress that can negatively influence even closed outdoor systems. For example, closed outdoor systems are still reliant on “seasonal, latitudinal, and diurnal variations in light conditions” which closed outdoor systems accommodate with “florescent lights, optical fibers or light emitting diodes or plates” [6]. Clearly, closed systems afford far more options with regard to design and must be studied further. The three most common types of PBRs must be addressed in order to address the variation on closed system designs (all of which are closed systems). reactor types. They hold the disadvantages of low photosynthetic efficiency and are more easily damaged from aeration [1], which actually costs more to do [7]. Tubular (horizontal) types are long pipes that are generally mounted in parallel loops on scaffolds with pumps to provide circulating flow throughout the system (Figure 1C). Tubular designed systems are noted to have the highest biomass concentrations (up to 6 g/L) [7] and the highest volumetric biomass density [1]. This design can arguably represent the central problem with all PBR designs – though so effective that the tubular type is the choice for the world’s largest PBR, it is extremely expensive and requires a lot of auxiliary energy [7]. Horizontal types are also noted to have “very limited possibilities for commercial scale applications” [1]. Annual designs, or column or vertical designs, are the final designs to be discussed. Generally, they consist of one large hollow cylinder with an additional internal surface to discourage dark zones (Figure 1B) [7]. This structure gives them the best light/ dark cycles, and thus a high photoefficiency, while taking up the least space. While, on a small scale, or in a laboratory, these PBR designs may be best suited for algal growth, industrially they face the most challenges for scalability and have high support costs [7]. Figure 1 A shows a flat panel PBR, B shows an annual PBR, and C shows a tubular [7] Conclusively, we can say little to nothing about which PBR is best to use. The reality is that it depends on the situation and what purpose PBRs are to be implemented for. Annual designs are indicated to be best for laboratory research and small scale production [7], but industrial, largescale endeavors may benefit more from flat plane [8]. In the end, however, regardless of design each PBR does the same exact thing. This paper has covered the hardware and theory into the construction of PBRs, but little of how PBRs function. Indeed, if innovation is to be expected, a thorough understanding of the operation of a PBR is necessary. Three Specific Types of Bioreactor Design The most commonly seen PBRs are the Flat Plate, Annual (also referred to as column or vertical) , and the tubular (or horizontal) models [1] [7]. A flat plane is the most common setup for its simplicity. It is described as “a plastic bag shaped by a wire netting” into a green wall panel which are often scaled up in the horizontal direction or setup in parallel with other fences (see Figure 1) [7]. Flat plane reactors hold the advantages of a shorter oxygen path, which means less dissolved oxygen buildup. They are also known for their low power consumption especially when compared to tubular BIOREACTOR PROCESSING AND OPERATION In addition to understanding the components and so-called “nuts and bolts” of our biofuel producing equipment we must also understand how the equipment works. This is important because knowing the reasoning behind whatever is being produced will allow for innovation to streamline that process to work towards optimal levels. As we will see, 2 Nasir Sharaf William Smith proper process management can “further improve the performance of the system and meet energy demands” [7]. Recall how certain principles must be accommodated for in order to construct a properly functioning PBR. We discussed how design accounts for light, particularly with the annual design. But what of the other factors, factors such as temperature and pH? How does one receive measurements concerning biomass and how does one feed and provide the nutrients that the algae require for optimized growth? Though we lightly touched on how mixing provides some of the nutrients need by the algae and how mixing provides CO2, we would do well to further explain the process. Understanding the processes behind PBRs serves a purpose beyond academic understanding. As also noted processes can be streamlined to decrease energy and fiscal costs [7] and thus merits scrutiny. By doing so one will inadvertently have to analyze and assess the processes in order to fit the whole process into an ecological, economical and social scenario [7]. Thus, the following sections will showcase the internal processes and provide a hint towards the economic feasibility of PBRs. along the strongest mass transfer gradient are recommended [7]. Process Integration Recall from the General Design and Overview section how photobioreactors must account for variables such as temperature, oxygen removal, etc. Several of these factors are useful in certain situations but a hindrance in others. One can streamline the process by carefully organizing the process to become an integrated process that could potentially have cost saving benefits [7]. This adds another feasible, pragmatic financial gain to bioreactors. As alluded to previously, atmospheric CO 2 is not enough for proper algal cultivation. One suggested source of CO2 is combustion plant emissions and their steady supply of CO 2 waste [7]. Though certain restriction apply (natural gas byproducts are perfectly acceptable, but coal-powered emissions have detrimental amounts of sulfur and nitrogen oxide), the synthesis of combustion power waste streams and PBRs have the potential to decrease costs and promote so called “green technologies”. Another possible energy optimizing process is membrane gassing. In this method, a “gas-permeable membrane creates the surface for CO2 dissolving and O2 removal directly at the gas intake” to allow for more degrees of freedom in process operation [7]. This lowers the loss of CO2 via leakages and results in a homogenous dispersion of CO2, which minimizes mixing. This process thus saves energy. Process Management As there are several factors that influence PBR performance and algal growth, it is better to focus on a few factors whose presence is strongly felt. Temperature is one such factor. Though temperature can be affected by the PBR itself and certain algae strains can compensate for temperature changes better than others, temperature and its effects are largely reliant on the global position of the PBR. For example, in Southern regions of the U.S. and Australia excess heat is a large issue, whereas in northern climates like Central Europe and the northern regions of the U.S. one must find innovative ways to warm up the PBRs [7]. One possible solution is phase changing materials, which are commercially available in “wallpapers for flats” that control the room temperature at the value of phase transition. This means PBRs could be controlled to an adjustable level and not in a more haphazard night/day average [7]. Managing what and when the PBR is fed is also another way to control outputs. The medium that is fed to the PBR is composed of the minimum nutrients (e.g. phosphate) the algae needs, with the exception of nitrogen. Nitrogen is intentionally lowered to prevent the production of nucleic acids and proteins and instead forcing the microalgae to store CO2 and light energy in lipids, which are central to oil formation [7]. However, this has only been done in laboratory settings thus far [7]. Other nutrients like CO2 can be gassed in. It is recommended that gassing occurs the most during the day, when there is the most photosynthetic activity, and reduced to bare minimum at night, when there is the least. To monitor these and other nutrient intakes and subsequent productivity, two pO2, pH and pCO2 sensors ENGINEERED ALGAE PRODUCTION Algae is easily grown, developed, and sustained in many diverse habitats all by itself. The problem is that algae that excrete oil is not only difficult to grow in large amounts, but it is not found everywhere, especially in areas that don’t receive sunlight for at least half a day’s time [9]. Once the algae are successfully cultivated though, the metabolism process begins. Splicing genes together and producing environments for the algae to adapt in order to create a strand of algae that produces fuel on a much grander scale that can survive harsh climate changes and shifts in diet easily. Now that the algae are adapted to the environment and a larger population of algae exists, the catalyst of carbon dioxide is pumped through tubes that mix with the algae. These translucent tubes allow light to pass through and provide the algae the light needed for photosynthesis. The sugar created from photosynthesis added with the carbon dioxide in accordance to the various ways the algae produces these materials results in either ethanol, butanol, isoprene, or biodiesel. The processes that provide each of these outputs are specific to the algae strand that is being utilized; therefore the time and energy spent developing each fuel is completely unique from the rest, making the engineering and creation process strenuous and critical to success. 3 Nasir Sharaf William Smith demonstrates the growth efficiency affected by the switch from one PBR to the next. Cultivation & Growth Algae grow in many places in the world, but only certain algae can produce oil. Algae that possess lipids can excrete oil and are now being genetically metabolically engineered to be less susceptible to climate change, to withstand other symptoms, such as infection or disease, causing loss of algae, and to enable a production of greater amounts of oil for the same amount of nutrients. This effectively creates “super algae” that can reach peak efficiency in the production of oil. Currently, 30 specific brands of algae are being researched and tested to find the algae strand that is most compatible with the ever-growing human need for fuel [10]. The engineered algae’s growth starts out in a lag and works into an exponential, linear, and finally a peak growth life cycle. It is believed that the initial lag is used as time for the algae to adjust to the surroundings and to develop a large population to use the resources that are given. Theoretically once the initial lag has ended, the amount of sunlight should proportionally yield the growth rate of the algae and the constitution of the algae. There is, however, a slight dip in the rate of growth which is labeled as “maximum occupancy” [9]. This term refers to the point where the general mass of the algae divided by the density of the algae approaches the maximum volume of the PBR. Like most organisms, algae needs sufficient room to grow, live, and function. Without the necessary space, the algae growth rate declines. As expected if more space were provided, which is entirely dependent on necessary funding, the algae growth rate will continue to rise. Figure 2 is based on lipid production from light intensity illustrates the level of importance of light intensity in the algae growth process. The cultivation potential map almost produces the same range of information but yields to specific points on the map. Figure 3 This graph is a general representation of the initial growth vs. time for the fourth generation of microalgae. The growth units are in duplication speed and the time units are in seconds [9]. Sustainability & Treatment Since the algae uses sun irradiation to grow and produce fuel, it is essential for the algae to be exposed to intense rays usually from three hundred to three hundred and sixty-five days year [12]. The microalgae also depend on the structure of the PBR and its composition to enable the flow and even distribution of light, heat, nutrients, and catalysts to each algal structure. For a better observation of these systems, see the general design and overview section of this paper. The loss of microalgae is only attributed to the extreme cases of light, pH levels, nutrient and temperature depravation and supplementation which in a controlled environment happen rarely [12]. Because energy is such a readily used accommodation by most all citizens, inaccessibility of the suns light for the microalgae could provide fatal blows to the daily life of the individual and, subsequently, the economic market. To ensure that never happens, many research facilities have implemented the use of lighting system for cloudy and foggy days. The use of carbon dioxide, nitrogen, and phosphorous the main ingredients for predictable growth rates of algae and for a metabolite process of obtaining oilgae [10]. The amount of supplementation for the algae is subject to the overall health of the algal community. The issue with going into any detailed specifics on the general spectrum of algae is that every stand of algae is dependent on different catalysts, amounts of nutrients, and environmental structure. Sadly, the specific information needed for each brand of algae is beyond the scope of this paper. Figure 2 Displays potential lipid production across the U.S. color specific light intensity (Red representing most intense and blue representing least intense) [11] GENERATION-BASED EXTRACTION METHODS Many factors, such as climate change, pressure shifts, contamination, and the structure of the PBR affect the growth efficiency of the algae though not as drastically as the un-engineered counterparts. The table below This section will discuss the particular types of engineered algae along with the benefits and disadvantages of each. Past attempts have been made to use algae as a biofuel and with 4 Nasir Sharaf William Smith recent technology advancements new breeds of algae are available [10]. The discussion and implementation of such new age algae is important if the project should succeed. As expressed in table the variance of steps between growing and gathering oil in the third and fourth generation biofuel are definitively significant. In the third generation the need to separate the algae from the fuel is required by either a sedimentation type process or by various draining methods. Also with the addition of separating the oil from the algae, the process of converting the oil into a biodiesel incorporates more steps that initially made the use of this technology unattractive. In the latest generation however, the oil naturally, through genome influence, divides from the algae. Harvesting the algae and preparing for commercial use is the only step after oil is being produced in this new biofuel production method. Within the processes of the third generation algae, the last step of trans-esterification, which converts fat into biodiesel oil, requires the use of strong bases, acids and a treatment center for this method to occur. Just by eliminating one step many appliances and wasted space is saved, making the entire scope of the project incredibly more efficient in converting to fourth generation algae. Generation Variance The fourth generation of engineered algae exists as follows: Chlorophyta, rhodophyta, phaeophyta, Bacillariophyceae, Euglenids, Dinoflagellates. These are the specific phylum that incorporates the strands of algae that are complete, verifiably operational, and are currently being tested. An average of about 7 different strands of algal genome sequences per phylum, of which there are over a hundred, exist that are being industrially utilized and considered. The third generation of engineered algae did not progress far, the entirety of research spent in that series of time was on the basic characteristics of the algae and it’s general behaviors.[13] Of the complete eukaryotic microalgae that have been investigated with gene transformation, which share the same phylum as the complete list of sequences, only thirty are actually stable enough to be tested and considered viable for commercial use. There are two different generation of algae. These two are the third and fourth generation of production possible biofuels, the first two being sugar cane and cellulosic bioethanol. “The main difference between fourth generation biofuel production and the previous generations is that only the former applies the “cell factory” concept for the production of gaseous and liquid biofuels. The photosynthetic organisms are thus driven by solar energy from the sun for continuous production of biofuels using CO2 as the raw material. The common feature of 4th generation biofuel production methods is that they will secrete the end products out of the cells, which will avoid the costly fermentation and/or processing of biomass feedstock applied in current biofuel production” [14]. The third generation was discontinued because of the lack of algae that could sustain intense environments, making research difficult and area specific, and the prospective integration of lipid advancements. Figure 4 displays the four generations of biofuel and their step by step process lifecycle. [10] Fuel Extraction ETHICAL AND ECONOMIC CONCERNS IN LIGHT OF COMMERCIALIZATION Over the course of a generation the technological advancements of microalgae has eliminated most all steps from cultivation to harvesting fuel. If such a short time had such a monumental effect that energy corporations, such as algae tec., are being utilized and governmentally funded then it’s only a matter of time before algae energy become stable, renown method of providing clean efficient energy. Not only that, but going from genetically engineered algae that produces fuel to genetically engineered algae that instantaneously produces fuel is progress that cannot, and has not, been ignored by any and all interested parties that can benefit from this technology. This part of our conference paper will discuss the positive and negative aspects to implementation, establish a theoretical basis to predict risks and chance of successful production, and how this new technology will affect the economic status of United States. Incorporating this into our paper is essential; in any large project every risk and possible result must be accounted for to insure the greatest yield of success. Introducing a new energy technology into the world of lobbyists, media, private and public interest groups and with the competition of other technologies that may or may not 5 Nasir Sharaf William Smith already control the market is full of risks and uncertainty. Some corporations could take measures to stay on top of the energy market by stunting the growth of many alternative sources. A prime example of the failure of alternative green technology by big industries is the electric car. ultimately decide the accessibility of PBR technology [15]. While these estimates provide a possible trajectory towards the future of PBR technology, further advancements in this technology will force the future to unfold either in accordance with our estimates or against. Overview of Production Costs Effect on Socioeconomic Market This part will relate the cost of materials, labor, and time spent to the amount of fuel produced. This range of information is necessary for a scaled numerical comparison between risks versus benefits. Note, this will solely be statistical data to provide objective comparison insofar as that is possible. Recall the factors that decided the technological design of PBRs. These factors also will decide the economic feasibility of PBRs. Initial investment costs are estimated at $74.03 per m2 or a fixed cost of $169,543.81 [15]. The fixed cost of $169,543.81 can be considered an initial approximation as costs are likely to rise as external infrastructure such as pipelines are added and “wear and tear” damages such as leakages in the nitrogen and CO 2 sources will add to such costs. Profitability is depended on a wide variety of the aforementioned factors and each has a specific impact on profitability with minimum impact from $0.09 per megawatt hour (the variable being H 2O) to a maximum impact of $71.01 megawatt hour from predictably post-biodiesel [15]. It should be noted that these profitability estimates have been made without other potentially profitable byproducts estimates included. Integrating other fuel sources into the fuel market will drastically change the possibilities for this project and affect the daily lives of many making it a key topic for consideration. The effect on the economic market will be characterized by hypothetical scenarios that will represent predictions on stock variance, shifts in the energy industry, and swings in international affairs [15]. In the past there have been a number of green technologies that have failed due to lack of social acceptance, economic uncertainty, and from corporate influence. The need to consider the electric car becomes apparent when we observe the magnitude of money and time spent on it and the private support it received. The electric car, in just three short years, went from potential success to an abrupt failure [16]. Some attribute the fault completely on private companies while others say it was simply before its time [16]. Photobioreactors, like many technologies today, would be more efficient if design specific advancements were made but based on recent research results it is not before its time. PBR’s are receiving support and funding from many industries and countries such as the United States, the Australian company Algae Tec., and various Middle Eastern countries are now implementing PBR’s into green specific research facilities [17]. There has been no evidence that companies have been making similar moves to buy out, eliminate, or otherwise marginalize PBR technology. The aim of our statement is not to create conspiracy, only to recognize the possibility of another collapse of a clean, efficient technology. Feasibility of Large Scale Commercialization Production on a large scale is necessary to cause even a noticeable effect on the fuel market therefore making it imperative to discuss the likeliness of this project gaining momentum. Here, the aforementioned statistical data will be analyzed and applied to the possibility of large scale commercialization. Numbers are meaningless with analysis. Though PBRs have a high yield per unit area, land is possible the single factor deciding whether PBRs produce more than they consume. Even if PBRs “break even” compared with technologies such as solar PV and solar heat PBRs occupy a small portion of the economic market [15]. This isn’t to say PBRs don’t have their place as PBRs have certain advantages give them a competitive edge compared to other green technologies. One mentioned previously was the O2 produced as a byproduct that may be marketable. Other advantages include the efficient use of land (even inhospitable lands traditional agriculture could not thrive in) and the directly produced hydrogen, which could potentially fuel future devices (think hydrogen fuel cells) [15]. Succinctly, one could say that the PBR market does not look bleak, but equally so, not promising. Of course, the sensitivity to energy prices with regard to investment will FUELING THE FUTURE: PROSPECTIVE APPLICATIONS Through our careful examinations of the technologies of photobioreactor design and through its interactions with the algae it cultivates we have established it as a strong potential source of alternative energy. We have discussed its designs to great length and the process underwent in the PBR. We have seen the cultivation, harvesting, and genomic engineering of various algal cultures. Through all this we can contend that PBR’s may potential be the source for a cleaner, more environmentally stable future. REFERENCES [1]A. Kunjapur, R. Eldridge. (2010, March 23). “Photobioreactor Design for Commercial Biofuel Production 6 Nasir Sharaf William Smith Using Microalgae.” ACS Publications. [Online] Available: http://pubs.acs.org/doi/full/10.1021/ie901459u Available: http://pubs.rsc.org/en/content/articlehtml/2011/ee/c0ee00593 b [2]G. Liden. 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(2011, April 19). “Lipid Light Intensity Graph.” RSC Publishing. [Online] 7 Nasir Sharaf William Smith ACKNOWLEDGMENTS We would like to thank Roger Wyss, Mike Anzaldo, Mike Galla, Blair Suter, and Diane Kerr for their insightful aid and consistent assistance. 8