Executive Summary


Aquarius investigates differences in engineered chassis behavior in laboratory conditions versus simulated real-world aquatic environments. Through three case studies, we clarify critical differences in survival, gene expression, and functional performance of chassis under controlled laboratory and simulated natural conditions.

I. Marine Corrosion Prevention with Bacillus subtilis

Engineered B. subtilis strains showed enhanced biofilm traits in lab media but failed to form robust biofilms or prevent corrosion in simulated seawater environments. Natural strain 3610 outperformed engineered variants. RNA-seq and 16S analyses revealed environmental stress and microbial competition significantly impacted gene expression and chassis persistence.

II. Freshwater Harmful Algal Bloom (HAB) Remediation with Cyanophage and Acinetobacter baylyi

A. baylyi persisted in static laboratory cocultures but was outcompeted by microbial competitors in flowing lakewater microcosms. Under microcosm conditions, 16S amplicon sequencing and colony counts indicated a reduction in A. baylyi survival that corresponded with an increase in the relative abundance of competitor species. Preliminary RNA sequencing results identified differentially expressed genes that indicate differences in A. baylyi functioning across the two conditions.

III. Biofilm Removal in Household Pipes Using Phage Therapy

Phages lysed mycobacteria effectively in lab assays but degraded quickly and failed to persist or reduce biofilms in PVC pipe microcosms. Microscopy and 16S sequencing revealed complex biofilm communities and limited phage impact. We are analyzing novel RNA-seq data to identify biofilm-associated gene expression that may inhibit phage efficacy.


Bioinformatics & RNA-Seq Meta-Analysis

We conducted a meta-analysis of transcriptomic and metatranscriptomic data to identify genes and pathways differentially expressed between lab and environmental conditions. These insights are guiding our development of design principles for synthetic biology in aquatic systems.

Aquatic Case Study I:

Corrosion Prevention Using Engineered Bacillus subtilis in Marine Environments


Overarching Goal: To compare ability of engineered B. subtilis to prevent corrosion in lab conditions versus simulated real-world marine seawater conditions.

Experiment 1:

Construction of Engineered B. subtilis Strains


Data Analysis/Interpretation:

We conducted colony PCR for the constructed plasmid L0 SapI-J04450-TapA-SipW-TasA, only 2 out of 24 PCR reactions yielded a band of the expected length, suggesting that the SapI insert has a low ligation efficiency, possibly due to its short three-base-pair fusion sites, resulting in a high possibility of mismatch.

The integration vector pBS1C-N was designed to integrate into the AmyE locus in the Bacillus subtilis genome. Upon successful transformation, the vector disrupts the native amylase gene, thereby stopping the strain’s ability to hydrolyze starch. This disruption enables a straightforward functional screening method: colonies with successful genomic integration will fail to degrade starch and appear dark blue when stained with iodine solution, whereas wild-type colonies will be orange due to starch breakdown. Transformation into B. subtilis 168 yielded colonies for all four constructs showed dark blue in iodine staining, confirming the loss of starch degradation, showing that the vectors were successfully integrated into B. subtilis 168 genome. When labeling Petri dishes, the B. subtilis 168 tapA–sipW–tasA+ strain was abbreviated as TST for convenience.

Experiment 2:

Establishing growth curves to compare growth dynamics of B. subtilis 168, 3610, and the 4 engineered 168 variants under laboratory conditions


Data Analysis/Interpretation:

Both the 24- and 36-hour growth curves indicated that the concentration of the xylose inducer had no significant effect on bacterial growth in standard LB medium, which does not promote biofilm formation. The dark blue line shows that the absence of xylose resulted in no major difference compared to other concentrations. The four engineered strains and the unmodified laboratory strain Bacillus subtilis 168 exhibited similar growth rates, whereas the natural strain B. subtilis 3610 grew substantially faster. Additionally, after the experiment, visible cell clusters were observed in several wells containing B. subtilis SinI+ and B. subtilis BslA+ strains, which may explain the pronounced fluctuations in OD readings toward the end of the growth curve.

Experiment 3:

Evaluating the motility of B. subtilis 168, 3610, and the 4 engineered 168 variants


Data Analysis/Interpretation:

Only Bacillus subtilis 3610 exhibited both swarming and sliding motility, confirming that it remains the only strain possessing both EPS-driven sliding and flagellum-driven spreading. None of the engineered modifications produced sufficient EPS to support sliding motility. Among the engineered strains, B. subtilis 168 and its SinI+ variant spread across the entire Petri plate, demonstrating strong flagellum-dependent swarming. The B. subtilis 168 BslA+ and TapA–SipW–TasA+ variants covered approximately 67% of the plate surface, showing moderate swarming. In contrast, the B. subtilis 168 TasA variant displayed neither swarming nor sliding, possibly due to cellular toxicity associated with TasA overexpression.

Experiment 4:

Determining effect of our genetic modifications on biofilm robustness and structure through characterization of biofilm and colony morphology of laboratory and engineered strains of Bacillus subtilis


Data Analysis/Interpretation:

Bacillus subtilis 3610 formed a distinct, slightly brown biofilm, while only the SinI+ variant exhibited biofilm-like folds and wavy colony margins. All other engineered strains produced smooth, flat colonies lacking biofilm characteristics.

When comparing media, LB medium did not support biofilm development and is therefore suitable for general culture rather than biofilm assays. In contrast, both SinI+ and B. subtilis 3610 formed biofilm structures on MSgg medium.

Regarding inducer application, sprinkled xylose on MSgg agar surface resulted in uneven colony morphology, likely due to heterogeneous inducer distribution across the surface. In contrast, adding xylose into the MSgg medium resulted in structured colonies. Adding 0.03% or 0.2% xylose produced no significant change in biofilm development, indicating that these concentrations were insufficient to elicit measurable promoter activation difference or alter biofilm formation dynamics.

Experiment 5:

Evaluating corrosion protection abilities of each strain on steel surfaces in a simulated marine environment


Data Analysis/Interpretation:

Visually, the seawater control group, which was not inoculated with B. subtilis, exhibited a thick oxidation layer on the steel surface, while moderate oxidation was observed in the B. subtilis 168 treated samples. Oxidation on the remaining samples was minimal and much less apparent. Scanning electron microscopy (SEM) further revealed extensive corrosion on both the three-day and seven-day control plates. Dennis Manos, the CSX Professor of Applied Science in William and Mary, interpreted the structures as oxidation structures along with tetrahedral crystal habit of magnetites and needle-like lepidocrocite structures. In contrast, the three-day B. subtilis 168 sample displayed distinct corrosion lines interspersed with deposits of irregularly shaped compounds—patterns similar to nano-structured calcium silicate(Johnston et al., 2008). Similar surface features were also present in the three-day B. subtilis 3610 sample and showed up in a region of the seven-day SinI+ plate. Notably, in other regions of the three-day B. subtilis 3610 plate, as well as on the three-day and seven-day BslA+ and SinI+ samples, we observed a novel surface structure: parallel, unidirectional apparently inorganic crystals forming across the steel in an anisotropic morphology that appears to follow the underlying substrate grains. Our phone and SEM pictures suggested the Bacillus subtilis in the microcosms noticeably altered the corrosion behavior and protected against corrosion. These formations differ markedly from previously published SEM images of B. subtilis–related corrosion (Guo et al., 2017; Wang et al., 2020), which were obtained under sterile laboratory conditions. In contrast, our study employed non-sterile microcosms designed to mimic natural marine environments, which showcased that these unique crystalline structures may arise from species interactions in aqueous environments.

Experiment 6:

Analysis of gene expression differences between lab and microcosm environments in strains with strong corrosion protection


Data Analysis/Interpretation:

16S sequencing revealed substantial colonization by non-Bacillus subtilis species across all seawater microcosm samples, indicating that mixed microbial communities developed under non-sterile conditions. Among the three tested strains: wild-type B. subtilis 3610, SinI+, and BslA+, the wild-type strain showed minimal persistence within these communities, whereas both engineered strains displayed moderate survival. Community composition varied strongly with inoculum concentration. In microcosms inoculated with 25% bacterial culture, Ochrobactrum dominated the population and emerged as the most abundant non-Bacillus genus. In contrast, microcosms inoculated with only 0.5% bacterial culture were consistently enriched in Acinetobacter. These results suggest that inoculum concentration not only shapes community composition but may also influence competitive interactions among resident taxa, providing a potential ecological explanation for the observed differences in corrosion-protection outcomes described in Experiment 4.

RNA sequencing results revealed that sporulation-related genes were downregulated in all three Bacillus subtilis strains under marine microcosm conditions. In contrast, metabolic genes were upregulated across all strains, with the SinI+ and BslA+ variants showing increased expression of genes involved in ATP binding, rRNA binding, and translation. Notably, the BslA+ strain exhibited specific upregulation of genes associated with flagellar assembly, suggesting an enhanced motility response to the seawater environment. The RNA sequence strongly supports that strains were behaving differentially in simulated natural environments and lab environments.

Aquatic Case Study II:

Freshwater Algal Bloom Remediation


Overarching Goal: To compare behavior and ability of cyanophages and/or Acinetobacter baylyi to remediate HABs in lab conditions versus simulated real-world conditions.

Experiment 7:

Microcystis Cyanophage Isolation for Harmful Algal Bloom Remediation


Experimental Goal:

To isolate (and potentially engineer) novel Microcystis cyanophages for harmful algal bloom (HAB) remediation as a case study to compare phage behavior in laboratory conditions versus simulated real-world environments.

Data Analysis:

Plaque formation on a Microcystis lawn is a strong indicator of phage presence, however we were unable to consistently propagate any putative cyanophage.

Interpretation:

Our results highlight a need for SynBio solutions that consider the ecological complexities of real-world water systems in which they must ultimately be deployed. Our attempts to isolate and engineer cyanophage offer a case-study in the effects of real-world chassis behavior and community dynamics on the effectiveness of SynBio-based aquatic remediation solutions.

Importantly, our results indicate that M. aeruginosa may have strong anti-phage defense systems that complicate phage isolation and could limit the feasibility of phage-based HAB treatments in the field. We have identified two major limitations of cyanophage isolation and cyanophage-based HAB treatment:

First, M. aeruginosa may rapidly evolve phage resistance. About 7% of M. aeruginosa’s genome is composed of transposases that can rearrange the species’ abundant mobile genetic elements (Frangeul et al., 2008) and drive evolution in the field and in the lab (Stark et al., 2024). Constant re-shuffling of the genome can rapidly generate novel phage-resistant genotypes—and our discussion with IHP experts indicated that resistance evolution can occur even at the level of a single culture. Rapid host resistance evolution at the culture level may prevent continual propagation of newly-isolated phages in the lab, and analogous evolution at the HAB population level would likely limit in vivo deployment.

Second, M. aeruginosa phages may exhibit high rates of lysogeny (integration and latency within the host genome), particularly during HAB formation (Huang et al., 2025). Lysogeny could limit novel cyanophage isolation, as there may be few free-floating phage available to isolate. Interestingly, the turbidity of our plaques may indicate a level of lysogeny, which could explain the putative cyanophage’s inconsistent propagation. Lysogeny often provides host cells with immunity to other infecting phages (Buchner et al., 2024), and lysogeny’s prevalence in HABs could limit cyanophage treatment viability in vivo by preventing reinfection.

Experiment 8:

Comparison of Acinetobacter baylyi Behavior in Laboratory vs Simulated Real-World Microcosms


Overall Experimental Goal:To test habitat remediation with Acinetobacter baylyi ADP1-ISx as a case study comparing bacterial behavior (persistence and gene expression) in laboratory conditions versus simulated real-world environments in order to inform the development of design principles for synthetic biology applications in aquatic systems.

Experiment 8a:

Estimating A. baylyi survival in microcosms and control cocultures via colony counts


Data Analysis:

Control coculture spread plates consistently formed A. baylyi lawns throughout the time course, while microcosm spread plates yielded decreasing A. baylyi colony counts over the span of the experiment.

Interpretation:

The reduction in microcosm A. baylyi colony formation over time (and as compared with the control) suggests that the microcosm conditions adversely affected A. baylyi survival over the course of the experiment.

Experiment 8b:

Quantifying species abundance in microcosms and control cocultures via 16S amplicon sequencing


Data Analysis:

The average microcosm A. baylyi population declined from an initial 73.58% abundance (on day 1) to 7.83% abundance (day 7). Control abundances on day 7 were approximately comparable to those measured on day 1 (at 77.41% on day 7 as compared to 81.33% on day 1).

Relative Abundance Data

Figure: Mean A. baylyi Relative Abundance in Cocultures and Microcosms vs Days Post-Inoculation. Error bars display 95% confidence intervals for each mean.

Interpretation:

The substantial reduction in microcosm A. baylyi relative abundance over the course of the experiment (and as compared to the control) suggests that A. baylyi was outcompeted by native lakewater organisms within a week after initial microcosm inoculation.

Microscopy Image

Figure: A sample of native Lake Matoaka organisms, including various diatoms, cyanobacteria, and green algae under a standard light microscope. Our 16S results suggest that native microbes outcompeted A. baylyi in lakewater microcosms.

Experiment 8c:

Quantifying differential gene expression of A. baylyi in microcosms and control cocultures via RNA sequencing


Data Analysis:

After 24 hours, the most highly upregulated genes in A. baylyi microcosms as compared to control cocultures (indicated by high log2 fold change values) included genes encoding an NAD(P)/FAD-dependent oxidoreductase, an ATP-dependent Clp protease ATP-binding subunit, a mechanosensitive ion channel, and a PA1571 family protein. A. baylyi genes significantly downregulated in the microcosms included genes encoding LyrR family transcriptional regulators, a MATE family efflux transporter, and the epoxyqueuosine reductase QueH.

Interpretation:

Preliminary evidence of differential gene expression after 24 hours suggests that specific aspects of A. baylyi’s behavior and functioning are concretely affected by real world conditions and that A. baylyi likely does not function as effectively in a real world environment as it does in traditional in vitro cocultures. We are currently in the process of analyzing and interpreting RNAseq data to quantify A. baylyi differential gene expression between microcosms and control cocultures at all three timepoints.

Overall Interpretation:

Our results illustrate that engineered chassis may not persist and function as effectively in real-world environments compared with the lab settings in which they are typically tested. Synthetic biologists should test their constructs in simulated real-world environments in order to identify and address limitations associated with the effects of in vivo conditions prior to deployment.

We conclude that Acinetobacter baylyi’s survival and functioning may be limited in a real lakewater environment, despite effective persistence in cocultures. We observed a substantial decline in A. baylyi relative abundance (according to 16S sequence data) under simulated lakewater conditions, indicating that A. baylyi was outcompeted by native lake species. Colony counts further suggest that A. baylyi’s population declined over the course of the microcosm experiment, suggesting that lakewater conditions adversely affected survival.

Aquatic Case Study III:

Removal of Biofilms in Household Pipes


Overarching Goal: To compare ability of phages to lyse biofilms in lab conditions versus real world conditions of household pipes

Experiment 9:

Determining efficiency of specific mycobacteriophages to lyse mycobacteria under laboratory conditions


Data Analysis/Interpretation:

Phage titers ranged from approximately 10^10 to 10^13 PFU per milliliter of lysate. Phage CrimD and Phage Neighly formed webbed lysis at 10^10 dilutions and Phage Raid at 10^8 dilutions, successfully killing most of the mycobacterial lawn. This illustrated the ability of phage to kill mycobacteria even at high dilutions.

Experiment 10a:

Determining titer of viable bacteria in the microcosm effluent before and after phage infection


Data Analysis:

There was not a significant difference in the bacterial titer before and after phage infection (p-value = 0.604), which was determined using a Welch t-test.

Interpretation:

Phage treatment did not have a significant effect on bacterial titer in the effluent, suggesting that one treatment of phage was not significant in decreasing bacterial population in the biofilm.

Experiment 10b:

Determining phage survivability in microcosm conditions


Raw Data:

Initial phage titer inoculated uniformly throughout the microcosms: 4.5*10^12

Titers Table

Figure: Phage titer from effluent after 24 hours.

Data Analysis/Interpretation:

Phage titer decreases substantially after 24 hours in microcosm effluent, likely due to the proteases and other degradation factors that are inherent to realistic and dynamic environments.

Experiment 10c:

Testing phage presence in microcosm effluent at the final time point


Raw Data:

There were no visible plaques in the plaque assays from the final effluent.

Data Analysis/Interpretation:

The lack of phage presence in the effluent at the final time point signifies that phage did not adhere strongly enough to the biofilm or phage no longer were able to sustain themselves in the biofilm. This may be because of the decrease in bacterial population or the structure of the biofilm preventing the phage from surviving for long periods of time.

Experiment 10d:

Determining the structure of the biofilm in the pipe following phage treatment


Data Analysis:

Hirox table

Figure: Average color distributions on biofilm surfaces with phage and without phage treatment.

Interpretation:

The PVC pipes that were treated with phage had what resembled plaque-like holes in biofilm formation, with less surface area covered by biofilm compared to the biofilm that was flushed with standard tap water with no phage added. There were also less visible red bacteria, signifying that the RFP-transformed mycobacteria was less present after phage treatment.

The colors represent the distribution of height throughout the biofilm. Since we saw no significant differences in maximum and minimum heights, we chose to focus on the height distribution based on the pseudocolors that were assigned by the HIROX microscope program. Blue represents the lowest height range, green being the second lowest, yellow being greater, and red being the highest height range.

There is a trend (p-value = 0.067) of lower range colors being predominant in the pipes treated with phage, meaning that although the range of biofilm height remains relatively consistent, the height distribution is skewed towards the lower end after phage treatment. The lack of disparity in maximum height is consistent with literature that suggests that phage clusters in regions upon infection of the biofilm, and the extracellular matrix itself is not heavily affected by phage treatment (Testa, 2019).

Experiment 10f:

Determining bacterial community structure of microcosm biofilm


Raw Data:

Kraken/Braken

Table: Outputs from running the 16s sequence through Kraken2 and Bracken with species and abundances.

Data Analysis:

The 16s sequencing results suggest that the biofilm largely consisted of acinetobacter, but contained various other species. There is no mycobacteria sequence identified, although there is actinobacterium sequence identified, which may be the mycobacteria.

Interpretation:

Because the biofilm was grown in a nonsterile environment, there were expected to be other species present in the biofilm to closely simulate household water system conditions. However, 16s sequencing is limited to bacterial species, and does not provide full insight into the community structure of the biofilm.

RNA-Seq Meta-Analysis


Overarching Goal: To identify differentially expressed genes and pathways in chassis organisms by comparing laboratory versus environmental transcriptomic and metatranscriptomic data

Experiment 11a:

Analysis of transcriptomic data comparing laboratory versus environmental samples


Raw Data:

DESeq2 Outputs from Galaxy workflow and literature DE gene datasets.

Lit Review

Data Analysis/Interpretation:

DE Gene Data

Differential expression analysis showed transcriptional changes between lab and environmental conditions. These results emphasize the importance of designing chassis with environmental adaptation in mind.

Experiment 11b:

Analyzing differences between metagenomic and metatranscriptomic taxonomic results


Raw Data:

Final outputs of running our comparison pipeline (metaG_metaT)

metaT/metaG

Figure: Taxonomic results of running metagenomic and metatranscriptomic FASTQ files.

Data Analysis/Interpretation:

The comparison reflects the yield differences between a metagenomic and metatranscriptomic processing done in the sample location from a singular study. This result reflects the importance of running both metagenomic and metatranscriptomic sequencing to understand both historical and current species presence within a sampling location.

Experiment 11c:

Functional analysis of DE genes


Raw Data:

Complete DAVID functional analysis output, unfiltered

Data Analysis/Interpretation:

After applying a Benjamini-Hochberg correction (α = 0.05), we observed a number of significant p-values, but relatively fewer adjusted p-values meeting the cutoff. Nonetheless, the pathways that did remain significant, primarily related to stress response, membrane transport, and metabolic adaptation aligned with those identified through AI-assisted analyses. These correlations suggest that our meta-analysis is capturing biologically meaningful trends, though further data expansion and processing are needed to strengthen statistical power and confirm emerging patterns.

Experiment 11d/e:

Al analysis of DE genes & Curation and Vetting of AI results


Summary Results:

Differentially Expressed Genes When Comparing Bacterial Gene Expression in the Lab vs Natural Aquatic Environments

Here we present summary results for differentially expressed genes when comparing bacterial gene depression in laboratory conditions and in natural aquatic environments.

Using Differentially Expressed Gene Lists to Suggest Engineering Approaches to Make Engineered Chassis Fieldable in Aquatic Systems

Here we provide genes and target modules that repeatedly show in situ up-regulation in natural aquatic environments as well as down regulated in natural aquatic environments — and suggestions on what to engineer. Below are practical edit ideas associated with pathways known to flip between lab and field. We list gene families (examples) and why they matter in water.

Aquatic Laboratory vs Environment Differential Gene Expression

Specific Case Study: Bacillus subtilis

Here we present a summary of genes differentially regulated between lab and natural aquatic systems, and potential engineering approaches to enhance survival and persistence, of Bacillus subtilis in natural environments, for one of our case studies: the use of Bacillus subtilis to prevent or at least diminish corrosion.

Case Study: Acinetobacter baylyi ADP1

Here we present a summary of genes differentially regulated between lab and natural aquatic systems, and potential engineering approaches to enhance survival and persistence, of Acinetobacter baylyi ADP1 in natural environments, for one of our case studies: the use of Acinetobacter baylyi ADP1 to remediate HABS.

Specific Case Study: Mycobacterium smegmatis

Although we are using phage to remediate Mycobacteria biofilms in pipes, there is insufficient information regarding phage behavior of phage in laboratory and natural environments. Therefore we present gene analysis between page behavior in laboratory and natural environments. Here we present a summary of genes differentially regulated between lab and natural aquatic systems, and potential engineering approaches to enhance survival and persistence, of Mycobacteria smegmatis in natural environments, for one of our case studies: the use of mycobacteria phage to destroy mycobacterial biofilms in household plumbing. This is still relevant given that the biofilms may likely behave differently in actual aquatic (household plumbing) environments compared to laboratory settings.

Combined Species Table Laboratory vs. Environment Differential Gene Expression

References