Intergrated Human Practice
It is important not to remain our project in the lab, but to bring it out to the real world. We’ve investigated how we could apply our project concept to the real wastewater treatment infrastructure. Our project, an intrinsic biosensor in algae, was developed with the application of gene modification to wastewater treatment in mind. Thus, our human practice activities aimed to seek the realization of possibilities of the genetically modified wastewater treatment. To identify the current situation, we first visited four wastewater treatment offices in Incheon: Gwaja, Unbok, Gongchon, and Namhyang. Furthermore, for the application of our project, we had a meeting with prof. dr. ir. Di Wu, who is an expert on wastewater treatment.



Current Situation


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We visited Gwaja office and interviewed the assistant manager, Daeseok Park. Gwaja office has the biggest scale of infrastructure in Incheon. 350kt per day of foul water from Seo-gu district flows into the office. As the Bupyung-Juan Industrial park is located nearby, we realized that its main concern is dealing with unauthorized discharged wastewater. Especially, heavy metal concentration roars from the discharge. Mr. Park told us that specific elements of heavy metal in the illegally released wastewater are very difficult to remove. For example, the level of zinc in the wastewater rises to 15mg/L after the discharge, and this makes trouble to culture bacteria, considering bacteria can survive less than 0.48mg/L of zinc according to EPA (Environmental Protection Agency of U.S). In addition, for instance, if the inflow rate is increased over the acceptance level by the rainfall, they cannot help but release incompletely purified water. In case of disqualification of released water, the office must pay a fine, and this occasion has been frequently happening. Indeed, of the released water out of fifteen days of February 2021, only a single day was qualified. There is clearly a need for more effective treatment.


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At Unbok office, manager Jongki Lee guided us through the facilities and we had an interview. The office has tackled domestic sewage from the residential complex near the airport. During the interview, he emphasized the burden of the increasing cost of chemical reagents and filters. He mentioned that the price is especially burdensome these days, as the price of raw materials increased. This could be one of the reasons for the application of gene modification in wastewater treatment. Gongchon and Namhyang offices have treated the same types of wastewater as Unbok office. Three offices had similar characteristics.


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From visits to four wastewater treatment offices, we acknowledged some points to improve in wastewater treatment. In all facilities, microorganisms are utilized for the degradation of organic matter. This process is called activated sludge. It basically functions by encouraging the growth of microorganisms, with altering environments for dominantly growing different types of microorganisms at each stage. We noticed that the distinction among microorganisms is too simple. It has been simply distinguished depending on the preferred growth environment, such as the aerophile and the anaerobe. We felt a necessity of strain selection. If we select specific strains and allow to culture them dominantly rather than pre-existing organisms, the performance will be improved and that is the starting point of the application of gene modification.



Basic concept: Microalgae and Consortia

In terms of strain selection, we investigated applicable methods to this idea. Consortia between algae and bacteria were chosen as a good option. According to prior research, better growth of both organisms can be expected through signal and nutritional exchange. Especially, microalgae is an ideal organism since it efficiently decreases TN, TP, and concentration of heavy metals. (Li, 2022) and has a high content of neutral lipids, which is a raw material of biofuel. Indeed, we found that visited offices have just wasted cellular pellet from the activated sludge, or they simply used it as the solid refuse fuel recovered fuel. From the perspective of the net cost reduction, recycling the pellet to the bio-material is an attractive option. On the other hand, we started to doubt why microalgae are not used in the current wastewater treatment system.

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We had a meeting with prof. dr. ir. Di Wu, whose research field is wastewater engineering. During the meeting, he answered our question: Why are microalgae not used in Korea? He said that microalgae are not suitable organisms for the removal of organic matters, and it demands larger surface area to optimally culture with the sunlight, since it is autotroph. He said microalgae is suitable for treating daily wastewater rather than domestic and industrial wastewater. In the meeting, we also realized that microalgae are inappropriate to apply in Korea since the annual temperature difference in Korea is large.

Based on the accumulated knowledge from interviews, we started to investigate whether gene modification could complement the disadvantages of microalgae. First, it is identified that some strains living in Antarctica synthesize antifreeze protein, which is applicable to the Korean climate. (Gwak, 2014) Prior research also showed heterologous gene introduction of mercuric reductase into microalgae (Huang, 2006), which supports the removal of heavy metals. In addition, there have been many studies to improve biomass yield through gene manipulation. Our concept, consortia, is also a good choice to balance the performance between the degradation of organic matter and the removal of nitrogen and phosphorus. (Li, 2021)



Policy


In fact, the meeting with prof. Di Wu reminded us of an interview at one of the wastewater offices. We briefly introduced our plan and the staff advised us that convincing the Ministry of Environment is mandatory since there is a difference of interests between the field staff and the administrator. According to the advice, field staffs have an interest in the secondary benefits that are not covered by the standard, such as the degradation of microplastics. On the other hand, administrators have only an interest to satisfy the standard of purification. Everything else not covered does not matter to them. In addition, the current policy restricts offices to create additive values from recycling. This was why the valuable cell pellets were not recycled. He mentioned that it will take a long time to convince administrators of the implementation.



The result of gene manipulation is bound to the regulation of the use of genetically modified organisms. The policy in Korea demands the risk assessment to use Living modified organisms (LMO). LMO is monitored by Korea Disease Control and Prevention Agency. In case of the wastewater treatment, the authority will demand documents before its implementation. (Korea Disease Control and Prevention Agency, 2021)
The required documents are below:

① Application for permission to install and operate production process use facilities (LMO Act Enforcement Regulations, Attachment No. 34)
② Design drawings or copies of production process use facilities
③ Documents proving the scope of production process use facilities and rights related to their ownership or use
④ Basic design drawings of hazard prevention facilities or copies thereof
⑤ Equipment, technical capability, manpower and safety management regulations required for the use of LMM
⑥ Equipment, technical capability, manpower and safety management regulations to prevent human and environmental risks of LMM
⑦ Safety Management Standards for Operation of Production Process Utilization Facilities

After submission, Healthcare & Safety committee in the agency will evaluate and announce the result in 60 days by issuing the permit for installation and operation of production process use facilities.




Current biocontainment

In terms of disinfection process, wastewater treatment facilities already had some process for biosafety. They have mainly used chlorination or UV-radiation to purified water. We studied whether current bio-containment system still can be used for microalgae. In fact, microalgae has insensitive to chlorination and UV-radiation. According to research, while 99% of bacteria in the sludge will be killed with less 10kJ/m2 of UV-C radiation for seconds (Roeber, 1975), over 10kJ/m2 for minutes is reported to be enough to function for microalgae (Pfendler, 2018). In case of chlorination, it is revealed that microalgae accelerated to grow while bacteria is inhibited to grow at low free chlorine concentration. (Hu, 2020) From prior research, we concluded that more secure bio-containment system or sensitive biosensor is needed to application of gene manipulation into wastewater treatment in the wastewater treatment offices.




Market

hp-img In the case of Gyeonggi-do Research Institute of Health and Environment, which developed a wastewater purification system by raising microalgae as a single unit without genetic manipulation, it was able to reduce 50% of the electricity cost used in the existing sewage and wastewater system, and received love calls from many companies.


Economic value is the best drive to implement an idea. The size of the domestic water treatment market increased by 3% for 5 years from 91 billion dollars to 106 billion dollars. One of the most grown markets, sections of the infrastructure, and the process have shown great improvement from 30 billion dollars to 38 billion dollars. Furthermore, the sewage market constantly raises 5% of the investment to develop the efficiency of sewage purification.

In the case of Gyeonggi-do Research Institute of Health and Environment, it developed a wastewater purification system with microalgae. After the introduction of the system, it can reduce 50% of the electricity cost used in the existing sewage and wastewater system, and this system became known to its potential customers. Furthermore, since ESG management draws attention and the regulation for the environment becomes stricter, there is a clear demand for eco-friendly sewage and wastewater treatment process systems.



References


Gwak, Y., Jung, W., Lee, Y., Kim, J. S., Kim, C. G., Ju, J. H., Song, C., Hyun, J. K., & Jin, E. (2014). An intracellular antifreeze protein from an Antarctic microalga that responds to various environmental stresses. FASEB journal : official publication of the Federation of American Societies for Experimental Biology, 28(11), 4924–4935. https://doi.org/10.1096/fj.14-256388

Hu, X., Meneses, Y. E., & Aly Hassan, A. (2020). Integration of sodium hypochlorite pretreatment with co-immobilized microalgae/bacteria treatment of meat processing wastewater. Bioresource Technology, 304, 122953. https://doi.org/10.1016/j.biortech.2020.122953

Huang, CC., Chen, MW., Hsieh, JL. et al. Expression of mercuric reductase from Bacillus megaterium MB1 in eukaryotic microalga Chlorella sp. DT: an approach for mercury phytoremediation. Appl Microbiol Biotechnol 72, 197–205 (2006). https://doi.org/10.1007/s00253-005-0250-0

Li, D., Liu, R., Cui, X., He, M., Zheng, S., Du, W., Gao, M., & Wang, C. (2021). Co-culture of bacteria and microalgae for treatment of high concentration biogas slurry. Journal of Water Process Engineering, 41, 102014. https://doi.org/10.1016/j.jwpe.2021.102014

Li, D., Liu, S., Yang, Y., Guo, L., Lyu, B., Yang, R., Zhang, X., Wang, Y., Yang, F., & Chen, Q. (2022). Metal-algae interaction contributes to the water environment heterogeneity in an Urbanized River. Ecological Indicators, 139, 108875. https://doi.org/10.1016/j.ecolind.2022.108875

Korea Disease Control and Prevention Agency. (2021, April 16). Notification and permission of installation and operation of facilities using LMM production process: National safety management of genetically modified organisms: Biosafety: Policy information. Korea Disease Control and Prevention Agency. Retrieved October 12, 2022, from https://www.kdca.go.kr/contents.es?mid=a20302090700

Park, J. (2021, February 25). 가좌하수처리장 방류수보름간 '합격'은 하루 뿐. 인천일보. Retrieved October 12, 2022, from http://www.incheonilbo.com/news/articleView.html?idxno=1081479

Pfendler, S., Alaoui-Sossé, B., Alaoui-Sossé, L., Bousta, F., & Aleya, L. (2018). Effects of UV-C radiation on Chlorella vulgaris, a biofilm-forming alga. Journal of Applied Phycology, 30(3), 1607–1616. https://doi.org/10.1007/s10811-017-1380-3

Roeber J. A. (1975). Ultraviolet disinfection of activated sludge effluent discharging to shellfish waters. Cincinnati, Ohio :Municipal Environmental Research Laboratory, Office of Research and Development, U. S. Environmental Protection Agency,