Project Description

Project Description

Abstract


The island municipality of Puerto Rico, Vieques, remains contaminated from decades of military activity with the high-energy compound RDX (hexahydro-1,3,5-trinitroso-1,3, 5-triazine), posing severe risks to human health and local ecosystems. To address this issue, we engineered a genetic circuit in Escherichia coli for RDX biodegradation and biocontainment. The system integrates two modules: (1) a biodegradation module containing an RDX-inducible riboswitch that regulates xplA and xplB, encoding cytochrome P450 and its flavodoxin reductase responsible for degrading RDX into formaldehyde and nitrite, and (2) a killswitch module that detects these byproducts to trigger colicin-mediated cell lysis. The circuit will be implemented in a four-stage Serial Bioreactor System designed to promote bacterial growth, induce degradation, treat byproducts, and ensure safe environmental discharge. Our system provides a controlled and sustainable synthetic biology approach for mitigating RDX contamination and supporting environmental restoration in Vieques.

graphical-abstract

Our Problem


During World War II, global demand for explosives like TNT, ERW, and PETN ignited a dramatic search in manufacturing [1]. But among them, one explosive stood out for its immense power and stability: Royal Demolition Explosive (RDX). RDX is a secondary high explosive that is widely used by the military in shells, bombs, and demolition charges [2]. Large-scale production of RDX began in the United States in 1943, where it was often blended with oils, waxes, and other explosives to create effective military munitions. However, due to manufacturing impurities and environmental degradation products, RDX remains a major source of explosive contamination at active and former U.S. military sites [3]. Currently, there are 31 out of 1,699 hazardous waste sites contaminated by RDX catalogued as Superfund National Priorities List by the EPA [4]. Some of the countries most affected by this contamination include Israel, United States, Germany, and the Anones Lagoon in Vieques, Puerto Rico.

Although Puerto Rico is known for its rich culture, vibrant music, and deep connection with the land and sea, during the 1940s it was used as a military training site. For a span of 60 years, Vieques’ Municipality was used to test live ammunition in two-thirds of the island, leaving multiple unexploded artillery in terrestrial and marine environments [5]. The tests were conducted 180 days per year, eight miles away from 9,000 to 14,000 of Vieques civilians [6]. This practice left behind an array of contamination of heavy metals and organic compounds, including a vast quantity of RDX [5]. Furthermore, the Anones Lagoon, the greatest contamination site in Vieques, is directly connected to the Caribbean Sea, meaning the water’s current can transport the contaminants to open water.

Acute exposure to RDX has been associated with neurotoxic effects like seizures, nausea, and loss of consciousness [7]. Chronic exposure studies have suggested liver, kidney, and reproductive effects, and the compound has been classified with “suggestive evidence of carcinogenic potential” [8].

In Vieques, Puerto Rico, the ATSDR evaluated soil, water, and air samples and concluded that measured concentrations at that time did not exceed health-based guidelines, while noting the importance of continued monitoring [9]. Later analyses have identified energetic compounds and metals in marine organisms, such as lobsters and snails, pointing to potential bioaccumulation in aquatic ecosystems [10].

Epidemiological assessments reported differences in cancer incidence between Vieques and the rest of Puerto Rico during certain periods, highlighting the need for more research on possible exposure–health links [6].

mapa-rdx

Source: Cary, T. J., Rylott, E. L., Zhang, L., Routsong, R. M., Palazzo, A. J., Strand, S. E., & Bruce, N. C. (2021, May 3). Field trial demonstrating phytoremediation of the military explosive RDX by XPLA/XPLB-expressing switchgrass. Nature News. https://www.nature.com/articles/s41587-021-00909-4

Why RDX?

High-energy compounds like RDX are persistent and toxic contaminants that have been detected in soil, groundwater, and even air near military testing and training sites. The stability of these types of molecules makes them resistant to natural degradation processes, therefore making the exposure to RDX linked to harmful effects on both ecosystems and human health, including neurological disorders and carcinogenic risks. These concerns contribute to the need of developing effective remediation strategies.

Attempts at addressing RDX contamination have faced significant challenges. Traditional methods such as incineration, soil excavation, or pump-and-treat systems are expensive, energy-intensive, and often generate secondary environmental impacts. Biological methods could be useful, however they frequently depend on specialized microorganisms that are difficult to cultivate or maintain in natural environments. Such limitations reveal the need for an accessible and environmentally friendly solution that can be simulated in real-world conditions.

Synthetic biology as an emerging field offers an innovative way to apply engineering principles to biology, enabling the creation of modular devices that perform specific functions.Previous research has demonstrated that the enzymes XplA and XplB are capable of degrading RDX into less harmful products such as nitrite and formaldehyde. Although these metabolites remain toxic, their formation enhances the overall detoxification process, as they can be more readily captured or further transformed into non-toxic end products. Leaning upon these findings, our project proposes the development of R-DetoX 2.0, a genetic device that integrates detection and degradation functions into a single system.

By combining an activation mechanism called a riboswitch specific to RDX with degradation enzymes and a fluorescent reporter, R-DetoX 2.0 serves as a dual-purpose prototype that not only identifies the presence of RDX but also actively aims to break it down. This strategy emphasizes accessibility, efficiency, and environmental safety, offering a potential breakthrough for remediation efforts.

In choosing this project, we aim to integrate existing bioremediation attempts and practical applications. A successful system could provide a sustainable, cost-effective tool to clean up contaminated sites worldwide, demonstrating how synthetic biology can transform persistent environmental problems into opportunities for innovative solutions.

contamination

Key Goals


  1. Optimize the genetic circuits developed by previous iGEM RUM teams; by improving the biodegradation of RDX, focusing on reducing the total number of base pairs in the construct, identifying a more efficient promoter to enhance gene expression under aerobic conditions, and implementing the use of a riboswitch.

  1. Carry out enzymatic activity assays; to evaluate the functionality of the XplA and XplB enzymes and determine their ability to degrade RDX, analyzing factors such as optimal pH, temperature, and cofactor use.

  1. Clone the optimized genetic circuits; verify correct construction through gel electrophoresis, and transform the constructs into a suitable E. coli host for functional testing.

  2. Implement biosafety measures, including a kill switch in our genetic circuit, to ensure safe handling and reduce environmental risks associated with the construct.

  1. Bring attention to local and global issues caused by explosive contamination, particularly in regions like Vieques, and advocate for sustainable, science-driven solutions.

The Solution


Source: RUM-UPRM 2022

Prototype designed to detect and degrade RDX in contaminated environments, potentially in Puerto Rico and around the world. It features two key devices. The first uses a riboswitch that senses RDX, triggering the production of enzymes that breaks it down into less toxic byproducts. The second is activated by those byproducts, formaldehyde and nitrite activating bacterial lysis to ensure the safe containment of E. coli. This recombinant bacterium is integrated into a bioreactor system. The first one grows the engineered bacteria that then reacts with contaminated water, which is then treated in an electrochemical reactor that aims to reduce the byproducts into harmless compounds. Finally, the treated water is tested to confirm degradation completion and environmental safety.

In the Lab


Laboratory work for this project involves in silico assembly and verification of the RDX detection and degradation prototype. After optimizing the sequence, it is sent off-site for DNA synthesis. Upon receipt of the synthesized DNA, it is transformed into Escherichia coli DH5α electrocompetent cells. The construct is then tested for RDX detection at low concentrations. As mCherry serves as the reporter gene, the medium should exhibit a reddish hue after overnight incubation in the presence of RDX. The construct is also tested in a medium without RDX to confirm that the reporter gene is not activated in its absence. Once accurate detection is verified, bench-scale bioreactors are implemented for degradation tests conducted by the engineering team.

WorkFlow-General

In the Field


To prevent exposing the environment to any potential biological risks, the engineering team designed SeBiS (Serial Bioreactors System), a controlled setting where the biological prototype will interact with the contaminated water. It is composed of a bioreactor system and an electrochemical reactor. The first system of bioreactors will focus on increasing the density of our prototype by scaling up recombinant bacteria from a laboratory flask to a larger bioreactor. As soon as the desired density is reached, this bacterial culture will be transferred onto the second bioreactor. Here, the contaminated water from the lagoon will encounter our biological prototype.

Detection and degradation of RDX should start to take place. An agitator will be integrated within this bioreactor to optimize contact between the cells and the dissolved RDX. After the second bioreactor, the substance will pass through an activated carbon filter to absorb Formaldehyde, and is then transferred into an electrochemical reactor where a change in the molecular structure of nitrite will be induced, converting it into less toxic byproducts; potentially nitrogen. At the end of SeBiS, the water will be analyzed to test water quality to make sure it has acceptable properties to be returned to the environment. Ultimately, this bioreactor system can be integrated into treatment plants for further degradation of highly energetic compounds, like RDX.

Future visions


Having completed the successful assembly and verification of the riboswitch-based detection construct (Device 1), our next objective is to finalize the complete RDX detection and degradation system by integrating the degradation genes xplA and xplB under inducible regulation. While the initial synthesis orders encountered difficulties—likely due to constitutive overexpression and vector incompatibility—these issues have now been addressed by redesigning the constructs to include the σ³⁸ stationary-phase and σ³² heat-shock inducible promoters, as well as by using the pUCIDT (Kan) vector for improved compatibility. The corrected constructs have been resubmitted and confirmed by IDT to have yielded perfect colonies, with delivery expected by mid-October 2025. Upon arrival, we will proceed with transformations, validation via restriction digestion, and functional assays to assess both RDX detection and degradation performance. Concurrently, future work will focus on incorporating Device 2—a kill switch—to ensure biocontainment and improve the biosafety of the engineered E. coli chassis, as well as facilitating RDX assimilation by enhancing the bacterium’s permeability to the compound.

Also, to assess the efficiency and completeness of RDX degradation, we aim to quantify known byproducts, formaldehyde and nitrite, expected in a 1:1 stoichiometric ratio. Nitrite will be measured using the colorimetric assay of the Griess reaction combined with UV-Vis spectrometry for quantification. Formaldehyde will be detected by HPLC following DNPH derivatization, with optional confirmation via the Tollens test [11].

In order to validate the overall performance of the assembled system, we plan to conduct a fluorometric assay using the mCherry (Part:BBa_K2136016) reporter to monitor gene expression kinetics and metabolite accumulation over time. This data will be complemented by high-performance liquid chromatography (HPLC) to quantitatively monitor RDX degradation and product formation at defined intervals. By plotting enzyme concentration versus time across varying initial substrate concentrations, we will measure initial reaction rates, determine the rate of degradation and use this data to estimate Michaelis–Menten parameters (Km, Vmax y kcat) for the engineered enzymatic steps, using lineweaver burk plot. These results will provide a comprehensive kinetic profile of the biodegradation process, critical for modeling a large-scale bioreactor performance.

Beyond the lab, we are committed to expanding our educational and social impact program aimed at engaging local communities in the emerging field of synthetic biology and its potential to address pressing environmental challenges. We aim to empower communities through accessible science education, including an annual iGEM-RUM Research Showcase where participants of all backgrounds can showcase their work, and a student-focused camp ‘SynBio 101’ that guides participants through the process of launching their own synthetic biology projects with mentorship from our team, culminating in final hypothesis-based presentations.

References


[1] G. P. Novik, "Analysis of samples of high explosives extracted from explosive remnants of war," Science of the Total Environment, vol. 842, p. 156864, 2022.

[2] T. Gorontzy, O. Drzyzga, M. Kahl, D. Bruns-Nagel, J. Breitung, E. von Loew, and K. H. Blotevogel, "Microbial degradation of explosives and related compounds," Critical Reviews in Microbiology, vol. 20, pp. 265–284, 1994.

[3] United States Environmental Protection Agency, "Technical fact sheet: Hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) (EPA Publication No. P100T2AN)," NEPIS, Fact Sheet, Sep. 2017. [Online]. Available: "https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=P100T2AN.TXT"

[4] H. Abadin, C. Smith, L. Ingerman, F. T. Llados, L. E. Barber, D. Plewak, and G. L. Diamond, Toxicological profile for RDX. Atlanta, GA: Agency for Toxic Substances and Disease Registry, 2013.

[5] A. Caro, "Diversity and microbial community structure at a former military ranges in Vieques (Puerto Rico)," M.S. thesis, Univ. Puerto Rico Mayagüez, Mayagüez, PR, 2008. [Online]. Available: "https://scholar.uprm.edu/handle/20.500.11801/967"

[6] H. Sanderson, P. Fauser, R. S. Stauber, J. Christensen, P. Løfstrøm, and T. Becker, "Civilian exposure to munitions-specific carcinogens and resulting cancer risks for civilians on the Puerto Rican island of Vieques following military exercises from 1947 to 1998," Global Security: Health, Science and Policy, vol. 2, no. 1, pp. 40–61, 2017, doi: 10.1080/23779497.2017.1369358.

[7] L. J. Burdette, L. L. Cook, and R. S. Dyer, “Convulsant properties of cyclotrimethylenetrinitramine (RDX): spontaneous, audiogenic, and amygdaloid kindled seizure activity,” Toxicology and Applied Pharmacology, vol. 92, no. 3, pp. 436–444, 1988, doi: 10.1016/0041-008X(88)90183-4. [Online]. Available: "https://pubmed.ncbi.nlm.nih.gov/3353989"

[8] U.S. Environmental Protection Agency, IRIS Toxicological Review of Hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) (Final Report, EPA/635/R-18/211F), Washington, DC, USA, 2018. [Online]. Available: "https://cfpub.epa.gov/ncea/iris/iris_documents/documents/toxreviews/0313tr.pdf"

[9] Agency for Toxic Substances and Disease Registry, Public Health Assessment for Isla de Vieques Bombing Range, Vieques, Puerto Rico, U.S. Department of Health and Human Services, Public Health Service, 2003. [Online]. Available: "https://www.atsdr.cdc.gov/hac/pha/reports/isladevieques_02072003pr/"

[10] National Oceanic and Atmospheric Administration, Contaminants in Marine Resources of Vieques, Puerto Rico, NOAA Coastal Science Program, 2011. [Online]. Available: "https://coastalscience.noaa.gov/data_reports/contaminants-in-marine-resources-of-vieques-puerto-rico/"

[11] G. Pinto Cañón, M. Martín Sánchez, J. M. Hernández Hernández, and M. T. Martín Sánchez, "El reactivo de Tollens: de la identificación de aldehídos a su uso en nanotecnología. Aspectos históricos y aplicaciones didácticas," Anales de Química de la Real Sociedad Española de Química, vol. 111, no. 3, pp. 173–180, 2015.

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