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Establishing Pseudomonas fluorescens as a chassis organism

iGEM team Heidelberg 2023 aims to introduce Pseudomonas fluorescens as a new chassis organism for the iGEM competition. We established standardized protocols and characterized certain growth limitations. We chose to use P. fluorescens as it is an excellent organism to conduct plastic degradation experiments as it is naturally capable of degrading polyurethane (Wilkes and Aristilde, 2017), polythene (Thomas et al., 2015), polyethylene (Mouafo Tamnou et al., 2021; Lakshmi and Selvi, 2021). Furthermore, the organism is facultative anaerobes and capable of utilizing inorganic compounds such as nitrates as terminal electoral receptors. This is beneficial in terms of scalability for industrialization purposes as the production rate is not dependent on local oxygen supplies (Kampers et al., 2021). An important aspect for usage in the context of iGEM is that P. fluorescens is classified as S1 and can be cultivated in the laboratory. Despite these benefits, P. fluorescens is an under utilized model organism. We tested various factors necessary for the cultivation of this organism in order to identify the optimal growth conditions and antibiotic resistance.

Growth rate assays were conducted on M9 minimal media with different carbon sources. As seen in figure 1, 18 different carbon sources were tested. P. fluorescens could grow on nine of them. For our experiments, LB broth was primarily used. The antibiotic resistances of P. fluorescens were also tested using ampicillin (amp), chloramphenicol (cm), kanamycin (kan), and streptomycin (strep). The 1x concentration of each antibiotic are as followed: amp (100 µg/mL), cm (20 µg/mL), kan (25 µg/mL), and strep (100 µg/mL). An antibiotic dilution series of each antibiotic were prepared and plated in a 96-well plate along with P. fluorescens. An OD600 nm measurement was taken every 10 min for 20 h. Figure 2 shows the growth of P. fluorescens in the different antibiotics. Amp does nothing to prevent cell growth, which is supported by the literature (BacDrive DSM50900, n.d.).The other three antibiotics reduce the cell growth depending on the used antibiotic concentration. Cm prevented some cell growth, however, kan and strep were best at preventing cell growth. For our experiment, strep was used at a concentration of 200 µg/mL. A concentration of 100 µg/mL should be enough according to our initial results. However, based on our following experiments it was not sufficient to cause selection pressure. We recommend using kan as an alternative for strep, because we observed spontaneous mutations against strep after around 16 h of cultivation.

Figure 1: Pseudomonas fluorescens growth rate on M9 minimal media.
Figure 2: Pseudomonas fluorescens development of antibiotic resistance.
Pseudomonas fluorescens Competent Cells and Electroporation Protocol
Human practices

As creating presentations can be quite laborious, we want to share the presentation we created for our school lecture with future iGEM teams. Even though the presentation is adapted to our design and project, we are sure that it can be helpful as an inspiration for future school presentations. Just click here to find the presentation and our educational stickers on our education site.

Drylab Creating a digital twin of Pseudomonas fluorescens
A preexisting genome-scale metabolic model by Huang et Ling (2019) was used as the foundation of the adjusted model. After testing the model, we discovered several problems and improved the model for WT P. fluorescens for future use. In total 57 key reactions and 30 metabolites were added, leading to more reliable results. You can download the model here.
References

Jayashree Lakshmi P, Vanmathi Selvi K . (2020) Genetic analysis of low-density polyethylene degrading bacteria from plastic dump sites. Indian Journal of Science and Technology .13(48):4732-4738. https://doi.org/10.17485/IJST/v13i48.2066

Kampers, L.F.C., Koehorst, J.J., van Heck, R.J.A. et al. A metabolic and physiological design study of Pseudomonas putida KT2440 capable of anaerobic respiration. BMC Microbiol 21, 9 (2021). https://doi.org/10.1186/s12866-020-02058-1

Lakshmi, P. J., & Selvi, K. V. (2021). Genetic analysis of low-density polyethylene degrading bacteria from plastic dump sites. Indian Journal of Science and Technology, 13(48), 4732–4738https://doi.org/10.17485/ijst/v13i48.2066

Mouafo Tamnou, E. B., Tamsa Arfao, A., Nougang, M. E., Metsopkeng, C. S., Noah Ewoti, O. V., Moungang, L. M., Nana, P. A., Atem Takang-Etta, L.-R., Perrière, F., Sime-Ngando, T., & Nola, M. (2021). Biodegradation of polyethylene by the bacterium pseudomonas aeruginosa in acidic aquatic microcosm and effect of the environmental temperature. Environmental Challenges, 3, 100056. https://doi.org/10.1016/j.envc.2021.100056

Pseudomonas fluorescens: Type strain: DSM 50090, ATCC 13525, ICPB 3200, NCIB 9046, NCTC 10038, WDCM 00115, JCM 5963, BCRC 11028, CCEB 488, CCM 2115, CCUG 1253, CECT 378, CGMCC 1.1802, CIP 69.13, IAM 12022, IFO 14160, LMG 1794, NBRC 14160, NCDO 1524, NCIMB 9046, NCPPB 1964, NRRL B-14678, VKM B-894: Bacdiveid:12851. BacDive. (n.d.). https://bacdive.dsmz.de/strain/12851

Thomas, B. T., Olanrewaju-Kehinde, D. S. K., Popoola, O. D., & James, E. S. (2015). Degradation of Plastic and Polythene Materials by Some Selected Microorganisms Isolated from Soil. World Applied Sciences Journal, 33, 1888–1891. https://doi.org/10.5829/idosi.wasj.2015.33.12.10139

R.A. Wilkes, L. Aristilde, Degradation and metabolism of synthetic plastics and associated products by Pseudomonas sp.: capabilities and challenges, Journal of Applied Microbiology, Volume 123, Issue 3, 1 September 2017, Pages 582–593, https://doi.org/10.1111/jam.13472