Project Description

Background

As youth growing up in Shanghai, we have experienced and seen how the food delivery service has transformed people’s daily routines, lifestyles, and even the industrial structure of this energetic metropolis as well as the entire country. According to a report by the Shanghai Municipal Government (2023), merely on January 1st, 2023, there were approximately 151,000 delivery riders handling over 8 million delivery orders throughout the city (Shanghai Municipal Government, 2023). It is a commonsense that food, drinks, and snacks are usually some of the major reasons for people to place delivery orders, which inevitably require further consumptions of containers and packaging.

Staring at these numbers from statistics, we were somehow lost in our thoughts, and couldn’t stop but wonder: how much PET plastic was used to produce such a vast quantity of food containers and packaging?

The pollution concerns caused by the use of PET plastics have continuously drawn global attention. The wide application and long-term existence of plastic products has led to the accumulation of plastic waste, which has a negative impact on the ecological environment and biodiversity. However, the process of degrading plastic takes hundreds or even thousands of years to be finished. Not only that, but in the process, the plastic releases toxic chemicals and tiny plastic particles, which in turn pollute the soil, groundwater and surrounding ecosystems (Chariot Energy, 2024).

Through further research, we noticed even more striking numbers that foster our attention to the severity and urgency of finding better solutions to PET pollution. For instance, the 2021 PET Bottle Sustainability Report under the Background of Carbon Neutrality (Cailianpress & Frost & Sullivan, 2021) states that over 100 billion tons of PET bottles were consumed in China in 2020. It is logical to anticipate that this number has increased over the past four years, though we lack precise up-to-date statistical results. This emphasizes the need for immediate action.

Inspirations

When it comes to solutions for PET pollution, degradation is always a key concept. Plastic degradation refers to the process in which plastic is gradually broken down into smaller fragments or transformed into other substances under certain conditions. Common degradation modes discovered by scholars and have been implemented through industries and academia include: biodegradation, photodegradation, thermal degradation, etc. (Yousif, E., & Haddad, 2013).

Our passion on synthetic biology urged us to pay a special attention to biodegradation, as well as how synthetic biology can provide us with a creative path to address this problem. In 2016, Shosuke Yoshida and his collgues reported the discovery of the first IsPETase degradation enzyme, which can effectively degrade low-crystallinity PET plastics at the temperature of 30°C. IsPETase depolymerizes PET and releases soluble products, including mono(2-hydroxyethyl) terephthalate (MHET), which is further cleaved by the MHET enzyme (MHETase) into terephthalic acid (TPA) and ethylene glycol (EG) (Yoshida, 2016). To enhance the degradation efficiency of PET, a PETase/MHETase dual enzyme system has been developed. However, this enzyme has poor stability and cannot satisfy the practical application requirements for biodegradation.

The key enzyme for PET degradation is IsPETase. To improve its activity, American researcher Hongyuan Lu and his team have utilized machine learning to develop a modified enzyme, Fast-PETase, which can reduce the degradation time of plastics from centuries to mere hours or days (Lu, 2022). This breakthrough brings new hope for the effective degradation of PET.

Inspired by those previous work, we plan to use synthetic biological methods to recombinantly express Fast-PETase and MHETase. While prokaryotes like Escherichia coli are commonly used as vectors in relevant research, our interests and inquiry was drawn to the silkworm (bombyx mori).

China has a history of thousands of years in silkworm breeding and silk production. Silk holds a unique position in China’s cultural, artistic, and economic history, continuing to display significant commercial and artistic influence worldwide. Shanghai, where we are located, is situated in the middle and lower reaches of the Yangtze River. In ancient Chinese cultural concepts, this area is known as “Jiangnan” (the South to the Yangtze River), one of the epicenters of Chinese silk culture. This heritage gives us a natural affinity and enthusiasm for silkworms and silk, making it easier for us to connect with related stakeholders.

More importantly, the silk glands of silkworms, functioning as bioreactors, have successfully expressed various biologically active human cell growth factors (Chen et al., 2018), serum albumin (Qian et al., 2018), and lactoferrin (Xu et al., 2019), among other functional target proteins. Additionally, as natural long protein fibers, silkworm silk exhibits excellent biodegradability and biocompatibility, making it a prioritized candidate for the development of various medical biomaterials. It stands out as a natural protein raw material with significant application potential. Additionally, silk itself is an excellent high-molecular protein material. Previous researches has shown that silkworm’s advatnage in several fields: nanotechnology, syntic material and syntic biology beased on its high quality and stable gene expressing (Huang, 2018).

Our Project Goal

The goal of our research project is to construct gene expression vectors targeting Fast-PETase and MHETase genes. By utilizing techniques such as silkworm embryo microinjection and screening, we intend to create silkworm strains capable of high-level and specific expression of plastic-degrading enzymes in their glands and the silk.

Based on the successful production of this new silk material, ultimately, we aim to develop silk products with the ability to degrade plastic products, and implement them into realistic pollution-control scenarios.

References

Chariot Energy. (2024, May 28). How long does it take for plastic to decompose? https://chariotenergy.com/blog/how-long-until-plastic-decomposes/

Chen, W., Wang, F., Tian, C., Wang, Y., Xu, S., Wang, R., ... & Xia, Q. (2018). Transgenic silkworm-based silk gland bioreactor for large scale production of bioactive human platelet-derived growth factor (PDGF-BB) in silk cocoons. International journal of molecular sciences, 19(9), 2533.

Huang, W., , Ling, S., , Li, C., , Omenetto, F. G., , & Kaplan, D. L., (2018). Silkworm silk-based materials and devices generated using bio-nanotechnology. Chemical Society reviews, 47(17), 6486–6504. https://doi.org/10.1039/c8cs00187a

Lu, H., Diaz, D.J., Czarnecki, N.J. et al. Machine learning-aided engineering of hydrolases for PET depolymerization. Nature 604, 662–667 (2022). https://doi.org/10.1038/s41586-022-04599-z

Qian, Q., You, Z., Ye, L., Che, J., Wang, Y., Wang, S., & Zhong, B. (2018). High-efficiency production of human serum albumin in the posterior silk glands of transgenic silkworms, Bombyx mori L. PLoS One, 13(1), e0191507.

Shanghai Municipal People's Government. (2023, January 4). The average daily express volume reaches 10 million pieces, with over 150,000 delivery riders on duty. Shanghai's express and delivery capacity has largely returned to normal [Translated title]. Shanghai Municipal People's Government.https://www.shanghai.gov.cn/nw4411/20230104/0fa1d48b16894ea39ca48b5d2cb447dc.html

The 2021 PET Bottle Sustainability Report under the Background of Carbon Neutrality (as cited in 21st Century Business Herald, 2021) states that over 100 billion tons of PET bottles were consumed in China in 2020. https://m.21jingji.com/article/20210902/herald/85c1ea20a2ea55d2e8828ea026c8c692_zaker.html

Xu, S., Wang, F., Wang, Y., Wang, R., Hou, K., Tian, C., ... & Xia, Q. (2019). A silkworm based silk gland bioreactor for high-efficiency production of recombinant human lactoferrin with antibacterial and anti-inflammatory activities. Journal of biological engineering, 13, 1-12.

Yoshida, S., Hiraga, K., Takehana, T., Taniguchi, I., Yamaji, H., Maeda, Y., Toyohara, K., Miyamoto, K., Kimura, Y., & Oda, K. (2016). A bacterium that degrades and assimilates poly(ethylene terephthalate). Science (New York, N.Y.), 351(6278), 1196–1199. https://doi.org/10.1126/science.aad6359

Yousif, E., & Haddad, R. (2013). Photodegradation and photostabilization of polymers, especially polystyrene: review. SpringerPlus, 2, 398. https://doi.org/10.1186/2193-1801-2-398