We are examining how to utilize microbes and phytoplankton for decomposition of human-caused organic substances, such as filthy water and raw garbage discharged from urban environments. We also investigate how to efficiently extract energy from organic substances by using methane fermentation. These studies are relevant to the research on biomass energy, which is expected to be utilized in a recycle-oriented society.
In Japan, an annual emission of solid organic waste like food waste comes to almost 20 million tons, and its treatment has been quite problematic. Methane fermentation is receiving particular attention as an energy-producing treatment method of organic waste, because it is accompanied by the production of utilizable energy, methane gas. Wet-methane-fermentation treatment method is especially useful, because it allows solid organic waste to be directly thrown into its process. Indeed, improving this method is an important research theme in this laboratory, because various microbial communities are involved in processes of wet-methane-fermentation, such as hydrolysis, acid production, and methane production. In order to stably process the treatment method by stabilizing bacterial density, we have investigated how to maintain concentrated bacterial density in a wet-methane-fermentation reactor.
In anaerobic digestion, various microorganisms contribute to hydrolysis, acidogenesis, and methane fermentation processes, and it is necessary to maintain stable microorganism concentration in order to achieve steady waste treatment. Our laboratory has achieved a stable methane fermentation with 2 to 5-fold higher organic loading rate than standard fermentation method by recirculating sludge, containing microorgasms, back to the reactor (Right figure: Nagao et al., 2012). Furthermore, we found that by creating “resting period”, during which substrate supply is stopped, the microorganism concentration increases dramatically. Currently, we are aiming to reveal the mechanism behind the microorganism growth during resting period by studying the relationship between growth and digestate characteristics.
Due to eutrophication caused by population growth, mass generation of marine algae has been observed globally in recent years. Marine algae are washed ashore and cause a variety of environmental problems by deteriorating scenery and producing foul odors. Moreover, such drifted wastes have high moisture content and cost too much to burn them up. Aquatic biomass, including such algae, contains a lot of organic substances which are utilizable as biomass energy. However, aquatic biomass is inadequate for biological processing like methane fermentation, because persistent substances cause the decrease of decomposition rate, followed by a drop in biogas recovery efficiency. In order to improve the waste decomposition rate, it is imperative to increase substrate availability of microbes which are active in the methane fermentation process. Therefore, we are investigated how pulverizing aquatic biomass could contribute to improve energy recovery efficiency.
Algal biomass attracts attention not only for its importance in the waste disposal process, but also for its high productivity. Chlorella zofingiensis, a species of green algae, shows high cell multiplication rate and accumulates astaxanthin that is a useful substance with high commercial value. Establishing an efficient culture method of commercially high-value phytoplankton is instrumental for producing utilizable substances and energy, and this had been another research topic in this laboratory.
The UASB is a mid-to-high-concentrative method of sewage disposal through which methane gas is retrievable. The UASB triggers self-granulation of microbial community involved in methane fermentation and form granules of 0.5-2.0 mm in diameter in the sludge. Granules have excellent sedimentation properties and hold highly concentrated microbes, so it is useful for heavily-loaded operations. For these practical characteristics, the USAB has been globally adopted since the 1980s. Using this method, we have conducted a research aiming to recover methane gas from raw garbage.
However, the UASB is not suitable for treating solid waste. It is more useful for disposal of moist waste. In order to make solid raw garbage applicable for the UASB, we solubilized them and lower its solid concentration. After that, we disposed raw garbage through the USAB method and investigated methane gas recovery in the process. Also, in order to formulate granules appropriate for raw-garbage-effluent disposal, we studied granule production from digestive sludge using raw-garbage effluent. In addition, in Japan, where its land is surrounded by the ocean, fishing is an important industry and high-salinity effluent is discharged from the processing plants of marine products. From this perspective, salinity resistance of granules had been also studied in this laboratory.
In Japan, nearly 78% of waste winds up in a landfill after incineration. Meanwhile, in many developing countries like Indonesia, wastes are not sorted, and industrial discharges are directly dumped in landfills. Due to this inappropriate waste treatment, organic matters within the disposed wastes are biodegraded in the landfill, and greenhouse gas, such as CO2 and Methane, are emitted. Moreover, rainfall on the landfill produces leachate with dissolved waste constituents. Because most landfills in developing countries do not have facilities for gas recovery, water stop or leachate treatment, discharges from landfills have been causes of environmental problems as they accelerate global warming and contaminate groundwater and the ocean.
Soka University had undertaken a joint study with Surabaya Institute of Technology (ITS) since 2004. Through this joint study, we aimed to develop a low-cost leachate treatment which is feasible for developing countries. Studies have been investigating chemical quality of leachate from the Benowo landfill.
The LCA is a method which quantitatively evaluates environmental impacts of a product/system by looking at its whole process from production to disposal. Adopting this method to assess environmental effects of a disposal process helps us to specify a more appropriate and environmental-friendly disposal method. In Japan, nearly 80% of domestic waste is incinerated, the recycling rate of organic waste, such as food waste, only remains about 9%. In such situation, the Food Recycling Law became effective in 2001 (amended later in 2007), and a recognition system of “food loop” was established. This is a food-recycling process in which food waste is locally processed into composts or feeds and bought by local food-related companies for their businesses. In this way, “local production for local consumption” is further encouraged. Not only important for promoting food waste recycling, comprehensive evaluations like the LCA are also important to specify and establish an appropriate eco-friendly disposal process to realize a low-carbon society. Focusing on this food loop, we were assessing environmental and economic effects of food-waste disposal process. By doing so, we comprehensively evaluated environmental effects of food loop and find out its advantages and disadvantages.
Microalgae are superior to terrestrial plants in terms of carbon dioxide assimilation rate, and therefore algal biomass can be produced effectively incorporating nutrients from organic wastewater. Microalgae also produce fatty acids, protein, and carotenoid that can be transformed into medical, cosmetic, health, and feeding products. Currently, our laboratory focuses on both biomass production and wastewater treatment using microalgae.
Activated sludge processes are widely used wastewater treatment using aerobic bacteria. However, it requires a large amount of cost and energy due to mechanical aeration for O2 supply and chemical additives for nutrient removal. In 1957, Oswald et al. proposed an alternative wastewater treatment using algal-bacterial system, which uses microalgae with bacteria. In this system, bacteria remove organic matter in wastewater using O2 supplied by algal photosynthesis, and microalgae remove nutrients using CO2 released by bacterial respiration. Therefore, both organic matter and nutrients can be removed at relatively low cost and energy without mechanical aeration and chemical additives compared to the conventional aerobic wastewater treatments. Our laboratory is studying the treatment of organic wastewater at high loading rates using 1.2 m3 of high rate algal pond (HRAP) and the removal of bisphenol A using algal-bacterial consortia.
A unicellular green alga, Chlorella zofingiensis is known to produce astaxanthin, a type of carotenoid that has recently become commercialized. The body content of astaxanthin in C. zofingiensis is relatively smaller than Haematococcus plurivalis, its fast growth rate may improve the productivity of commercial astaxanthin production, if mass cultivation system of C. zofingiensis is established.
In a standard algal cultivation method, increasing cell density led to a lower growth rate because of “self-shading” that prevents effective light penetration. Therefore, in order to achieve a high density culture of C. zofingiensis, we developed a tubular photobioreactor cultivation system that avoids self-shading and effectively utilize photo energy, combined with carbon dioxide and nutrient supply control system.