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
Figure: Gel electrophoresis results for a colony PCR for pBS1C
Figure: Starch-iodine stain to check whether the constructed integration vector pBS1C got successfully integrated into B.subtilis 168 genome
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
Figures: The 36-hour growth curve of B. subtilis 168, 3610, BslA+, SinI+ under different inducer levels.
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
Figure: B. subtilis 3610 on 0.3%, 0.7%, 1.5% agar plates with 0.2% xylose.
Figure: B.subtilis 168 BslA+ on 0.3%, 0.7%, 1.5% agar plates with 0.2% xylose.
Figure: B. subtilis 168 SinI+ on 0.3%, 0.7%, 1.5% agar plates with 0.2% xylose.
Figure: B. subtilis 168 TasA+ on 0.3%, 0.7%, 1.5% agar plates with 0.2% xylose.
Figure: B. subtilis 168 Tap-SipW-TasA+ on 0.3%, 0.7%, 1.5% agar plates with 0.2% xylose.
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
Figure: MSgg agar plate with 0.03% xylose inducer spread on top, with each Bacillus subtilis strain directly spotted onto the agar surface
Figure: MSgg agar plate supplemented with 0.03% xylose inducer, with each Bacillus subtilis strain directly spotted onto the agar surface.
Figure: MSgg agar plate supplemented with 0.2% xylose inducer, with each Bacillus subtilis strain directly spotted onto the agar surface
Figure: LB agar plate supplemented with 0.03% xylose inducer, with each Bacillus subtilis strain directly spotted onto the agar surface
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
Phone pictures:
Figure: Steel chips taken out of microcosms after 3 days
Figure: Steel chips taken out of microcosms after 7 days
SEM Images:
Figure: SEM pictures of steel chips taken out of microcosms after 3 days and 7 days.
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
Figure: Relative abundance of bacterial species in seawater microcosms inoculated with different concentrations of Bacillus subtilis 168 BslA+.
Figure: Relative abundance of bacterial species in seawater microcosms inoculated with different concentrations of Bacillus subtilis 168 SinI+.
Figure: Relative abundance of bacterial species in seawater microcosms inoculated with different concentrations of Bacillus subtilis 3610.
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.
Figures: A sample of genes downregulated in microcosms compared to controls
Figure: A sample of genes upregulated in microcosms compared to controls
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.
Figure: Samples of raw data for observation of bacterial clearing and plaque formation in liquid and plaque assays, respectively
We observed bacterial clearing compared to control assays in 39 of 205 liquid assays. Putative cyanophage plaque formation, a strong indication of phage presence, occurred on 2 of 65 agar assays. One assay (see below) displayed multiple turbid plaques.
Figure: Substantial plaque formation on an agar assay
Resuspension of plaques in 5 mL liquid Microcystis culture yielded potential clearing in 3 of 4 instances. However, filtrate from the cleared assays did not produce re-clearing of a second round of liquid assays. Lysate harvested from the plaque-containing plate did not yield re-clearing.
Figure: Frequency of M. aeruginosa clearing and plaquing in liquid and phage plating cyanophage assays
Figure: Examples of clearing over time in a liquid assay “infected” with potential phage filtrate (left) versus a control assay “infected” with NFW (right).
Above: Filtrate was obtained from a previous assay. By day 5, the reinfection assay (left) was almost fully clear, while the control (right) retained its green coloration.
Above: Filtrate was obtained from a cyanophage enrichment. By day 3, the enrichment assay (left) had begun yellowing, and by day 4 had almost fully cleared. The control (right) retained approximately the same coloration throughout the experiment.
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
Figure: A. baylyi colony growth on LB agar spread plates vs. Days Post-Inoculation. Bacterial lawns were arbitrarily assigned the value of 600 colonies.
Figure: Spread plates approximately 1 day post-inoculation (left) versus 7 days post-inoculation (right). The top row of plates in each image were spread using samples from lakewater microcosms, the bottom row from control cocultures.
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
Figure: Samples of total species abundance data in microcosms and control cocultures at timepoints 1 and 7
Figure: Microcosm 16S amplicons after cleanup
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).
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.
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
Figure: Genes displaying statistically significant differential expression across control and coculture conditions. Positive log2(FC) values indicate upregulation in microcosms as compared to control cultures, while negative values indicate downregulation.
Figure: Successful microcosm RNA extractions
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
Table: Final phage titers for all three phage that were used for the microcosm experiments.
Figure: Plaque assays with Phage CrimD, Phage Neighly, and Phage Raid at 10^-6, 10^-8, and 10^-10 dilutions.
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
Table: Bacterial titers evaluated from microcosm effluent throughout each time point.
Figure: Average titer of effluent in CFU/mL on a log scale throughout a time period of 12 days. The microcosms were treated with phage on day 5.
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
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
We used the Hirox RV 2000 microscope to generate a 3-dimensional image of the biofilm, both in PVC pipes with and without phage treatment.
Figure: HIROX microscope image generated from a sample that was not treated with phage. The top image is in the original color while the bottom image is the pseudocolor assigned based on height.
Figure: HIROX microscope image generated from a sample that was treated with phage. The top image is in the original color while the bottom image is the pseudocolor assigned based on height.
Table: Percentage of each color distribution the pseudocolor image of the pipe.
Data Analysis:
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:
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.
Data Analysis/Interpretation:
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)
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.
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.
- Whole-transcriptome shifts in natural waters
- Global regulators override engineered promoters in the wild
- Inducible systems behave differently outside the flask
- Community interactions and quorum effects
- "Bottle effects” & sampling artifacts
- Plasmid retention & engineered-gene stability drop without selection
- Real-world aquatic microcosm tests of engineered reporters
Seawater vs. lab exponential growth (E. coli): After 20 h in seawater, ~937 genes were upregulated and ~~320 downregulated relative to lab medium; stress and starvation programs dominated the response (microarray). This shows broad re-wiring away from growth programs you typically assume in the lab.
Global stress regulators (e.g., RpoS/stringent response) gate expression when nutrients or conditions fluctuate—common in lakes/estuaries—so payload promoters that look “constitutive” in rich media can attenuate or become heterogeneous in situ. Recent reporter libraries that track multiple E. coli global regulators over time are useful references to explain these shifts.
Arabinose (PBAD) “all-or-none” induction: intermediate inducer levels create mixed ON/OFF subpopulations; fixing uptake (araE overexpression) yields more homogeneous induction—but in aquatic settings, uneven inducer diffusion/consumption often re-creates heterogeneity, weakening engineered outputs.
Cross-talk & performance drift: Work improving PBAD compatibility with IPTG (AraC evolution) underscores how inducer mixtures affect circuits; such mixtures and degradations are typical in environmental water, not in lab broth.
In mixed aquatic communities, quorum signaling and quorum-quenching alter transcription of motility, biofilm, nutrient uptake and public-goods genes—this cross-talk can silence or mis-time engineered outputs that looked clean in monoculture. Reviews focused on marine systems and WWTPs document these QS-mediated expression changes.
How you collect the sample changes the expression you measure. A comparison of traditional Niskin bottle collection vs. in situ filtration showed different community gene-expression profiles, highlighting that ex-situ handling can distort conclusions about “field” expression of engineered strains.
In the lab, antibiotics/auxotrophies maintain plasmids; in natural waters, no selection → rapid plasmid loss or mutation, reducing reporter/cargo expression. Multiple methodological studies quantify higher plasmid loss rates without selection and discuss stabilization strategies (TA modules, CRISPRi-based maintenance, antibiotic-free systems)—all relevant because environmental release removes antibiotic selection.
GFP-tagged E. coli microcosms in freshwater/marine-like conditions showed reduced persistence and signal vs. lab culture, with survival and detectable fluorescence dropping over time—consistent with stress-driven and plasmid-loss explanations.
Engineered biosensors deployed in untreated water samples often require adapting induction/assay protocols because inducer availability and matrix effects blunt reporter expression (e.g., lead/PFOA biosensors).
Overall: There is lower mean expression, more heterogeneity, and time-dependent drift in natural waters, driven by stress responses, QS cross-talk, and plasmid/circuit instability. Characterization in realistic matrices (filtered lake/sea water, defined low-nutrient media, redox/UV cycles) + field-mimicking induction schemes is essential before in situ use. Reviews on environmental deployment and genetic-stability design patterns summarize practical strategies (kill-switches, metabolic load reduction, chromosomal integration, resource-insulated parts).
Environment-enriched (often ↑ in seawater/soil/hosts/particles vs LB/glucose lab)
- Iron scavenging (Fe-limitation)
- Phosphate starvation (Pho regulon)
- Nitrogen & sulfur scavenging
- Osmoprotection / desiccation
- Oxidative/UV stress defenses
- Motility & chemotaxis (foraging)
- Adhesion/biofilm & surface sticking
- Broad substrate uptake & catabolism
- Membrane remodeling for stress
- Defense & phage pressure
- Competence / gene exchange (in situ cues)
- Storage polymers
tonB–exbB–exbD (energize OM receptors), OM receptors fepA/cirA/fecA/fhuA/fpvA/hasR, siderophores entCEBA (enterobactin), pvd/pch (pyoverdine/pyochelin), dhb (bacillibactin).
High-affinity uptake pstSCAB, regulators phoBR/phoPR, phosphatases phoA/phoD, organo-P phn (phosphonate).
amtB–glnK (NH4+), nitrate/nitrite narGHI/nirBD/nas, taurine/alkanesulfonate ssuEADCB, tauABCD.
Release valves mscL/mscS, compatible solutes uptake proU/proVWX, opuA/opuC/opuD, synthesis betT–betIBA (GB), ectABC (ectoine), otsAB (trehalose).
Peroxide/superoxide: katG/katE, sodA/sodB, ahpCF, dps, msrA/B, trxA/B, gor; DNA repair uvrABC, phr, recA. Regulators oxyR/soxRS, perR, sigB.
Flagella program flhDC/fliA/fli, chemotaxis cheA/cheY and MCPs, motors motA/motB.
Gram-: EPS/export wza/wzc/wzb, curli csg, pel/psl/algD (Pseudomonas). Gram+: epsA-O, tapA–sipW–tasA (Bacillus). Often under QS: luxS/AI-2, las/rhl/pqs, aphA/opaR (Vibrio).
ABC/TRAP/outer porins (dctPQM, dctA, oprD), complex carbon: aromatic ring cleavage ben/cat/pca, chitin/cellulose/hemicellulose hydrolases (chiA/chb, celAB, xylAB).
FA tuning: desA/desC (desaturases), cfa (cyclopropane FA), hopanoids hpn (e.g., Z. mobilis).
CRISPR–Cas, RM systems, toxin–antitoxin (mazEF, relBE).
comEA/EC/FA (Gram+), type IV pili/pilus assembly; tfoX/Y (Vibrio on chitin).
ppk/ppx (poly-P), glycogen glgABC, PHB phbCAB.
Lab-enriched (often ↑ in rich, aerated exponential culture)
- Fast growth / translation machinery
- Central carbon for rapid glycolysis
- Amino acid & nucleotide biosynthesis
- Cell division & envelope biogenesis
- Housekeeping chaperones (heat shock during fast growth)
- Motility/Biofilm OFF
rRNA operons rrn, ribosomal proteins (rpl, rps), tRNA synthetases, elongation factors fusA, tufA/B.
ptsG/manXYZ (PTS sugar uptake), pgi/pfkA/pykF, TCA/respiration modules; overflow pta–ackA, ldhA (acetate/lactate).
ilv/leu/aro, pur/pyr (especially in minimal but nutrient-replete growth).
ftsZ/ftsA/zipA (divisome), mur/fab (peptidoglycan/FA biosynthesis), LPS core/synthesis in Gram-.
rpoH (σ32), dnaKJ, groESL, ibpAB.
Many lab conditions repress costly flagella/EPS; QS modules often low.
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.
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.
Up-Regulated in Aquatic Environments:
- Membrane fluidity & pressure/cold adaptation
- Osmoregulation & ion balance (salinity swings)
- Light & photoprotection (surface waters, algae/cyanobacteria)
- Nutrient scavenging at oceanic concentrations
- Oxidative stress & UV-derived ROS
- Community interactions: competition, cooperation, viruses
- Motility & microscale foraging
Desaturases (desA/desC, fabA/fabB regulators), cyclopropane synthase (cfa), Psp stress operon: tune unsaturated/cyclopropane fatty acids to keep membranes functional under cold/high hydrostatic pressure. Overexpress desaturases; inducible cfa for transient shocks.
Chassis tip: Shewanella piezotolerans/baltica show clear transcript shifts under cold/HHP; their parts and promoters are a great starting library.
Compatible solute synthesis/transport: ectoine (ectABC), glycine betaine transporters (proVWX, betT/betAB), mechanosensitive channels (mscL/mscS). Install tunable uptake + synthesis; add an osm promoter to couple growth to external salinity profiles (marine ↔ brackish).
NPQ/photoprotection modules in diatoms and algae: LHCX family (e.g., lhcx1/2), carotenoid cycle genes. LHCX2 responds sensitively to iron limitation; wire this to a promoter reporting Fe stress to regulate antenna size or repair.
DNA photolyase (phr), uvrABC excision repair: upweight for high UV.
Phosphate: pstSCAB, phoBR regulon; Iron: TonB-dependent receptors, siderophore uptake; diatom Fe-inducible loci (e.g., ISIP1, co-expressed with LHCX2 under Fe limitation). Overexpress high-affinity transporters; use riboswitches for dynamic uptake.
Nitrogen: amtB (NH4+), urea (ureABCDEFG), cyanate (cynS), nitrate/nitrite transporters; glnB (PII) links C–N balance in cyanobacteria—use as a sensor or controller node for C/N flux.
Peroxiredoxins (ahpC), catalase-peroxidase (katG), superoxide dismutases (sodA/sodB), thioredoxin systems. Build a layered ROS defense with a fast peroxide sensor controlling membranes and repair enzymes.
Bacteriocin/bacteriocin-like peptides & export: Prochlorococcus co-culture DEGs reveal small exported peptide families (e.g., CCRG genes) induced by neighbors—use such motifs for programmable interference or communication.
Quorum sensing (LuxI/LuxR) wired to resource uptake or motility; biofilm/EPS (e.g., wza/wzc, pel/psl) for particle/surface association at the right time.
Phage defense: CRISPR-Cas, BREX/DISARM as swappable cassettes to harden open-water deployments.
Chemotaxis/flagella (cheA/cheY, motAB, fli genes): program “forage and settle” behaviors—chemotaxis on labile DOM or phosphate gradients, then EPS-mediated attachment.
Down-Regulated in Aquatic Environments:
- High-rate translation & ribosome biogenesis
- DNA replication initiation & cell division
- PTS sugar uptake & lab-sugar catabolism
- Overflow metabolism (acetate/lactate “Crabtree-like”)
- Flagellar assembly & motility (pelagic starvation context)
- Low-affinity phosphate transport (Pi-replete lab bias)
- Heat-shock (σ³²/RpoH) program at 37 °C
Genes/modules: rrn rRNA operons; ribosomal proteins (rpl/rps loci), translation factors (tufA/B, fusA, tsf, infA/B/C), tRNA synthetases. Slow growth dominates in oligotrophic waters; the stringent response ((p)ppGpp) suppresses rRNA/tRNA and ribosome biogenesis, shifting resources to stress survival. Growth-law work shows ribosome fraction scales with growth rate, so low μ in the field ⇒ low ribosome program.
Genes/modules: Initiation/elongation (dnaA, dnaN, dnaG, gyrA/B), divisome (ftsZ, ftsA, zipA, ftsQLB).
Why down in situ: Nutrient limitation triggers (p)ppGpp-mediated suppression of replication initiation; explicit starvation studies in Vibrio show replication initiation shut-off during stringent response. With slower cycles, division genes fall too.
Genes/modules: PTS core (ptsH/ptsI/crr), glucose PTS (ptsG), mannose PTS (manXYZ), lab sugar regulons (lac, mal, etc.).
Why down in situ: In the ocean, ABC/SBP transport dominates (high-affinity scavenging) while PTS is rare/inefficient at nM substrates; copiotrophs that carry PTS down-shift it in low-nutrient seawater. Comparative genomics & theory show an ABC↔PTS rate-affinity tradeoff underlying oligotroph vs copiotroph lifestyles.
Genes/modules: pta–ackA (acetate), poxB (pyruvate oxidase), ldhA (lactate).
Why down in situ: Overflow pathways are hallmarks of glucose-rich, aerated lab growth; under carbon-limited seawater they’re unnecessary and typically repressed.
Genes/modules: Master/flagella (flhDC, fliA, fliC), motors (motA/B), chemotaxis (cheA/cheY).
Why down in situ: Under prolonged starvation in seawater, several vibrios damp flagellum assembly to save ATP; motility often re-emerges near particles/blooms (exception).
Genes/modules: Pit system (pitA, pitB) vs high-affinity PstSCAB–PhoU.
Why down in situ: In low-P waters, cells induce Pst and Pho regulon while low-affinity Pit is disfavored/curtailed; Pit tends to operate under Pi-replete lab conditions.
Genes/modules: rpoH (σ³²), chaperones dnaKJ, groESL, proteases (hslUV, lon, ftsH).
Why down in situ: Ambient seawater (~4–25 °C) rarely triggers the RpoH/heat-shock axis that is prominent at 30–37 °C lab growth; cold-shock modules may be used instead.
Core, conserved toolbox (works across many bacteria)
- Osmotic shock / salinity
- Iron acquisition (Fe-poor)
- ROS/UV
- Phosphate scavenging
- Membrane tuning / motility & sticking
- General stress programs
Release valves: mscL, mscS → OE (low-leak) to prevent lysis in rapid hypo-osmotic dips.
Compatible solutes (uptake & synthesis): betT, betIBA (choline → glycine betaine), proVWX/proU (GB/Pro uptake), opuA/opuC (Firmicutes), opuD (GB uptake), ectABC (ectoine), gbsAB (GB synthesis in Gram+).
→ REG by salinity/σS/σB or QS; preload pools for shocks.
Energy for outer-membrane receptors: tonB–exbB–exbD → mild OE (1–2×).
Siderophore biosynthesis/uptake (species-specific) + OM receptors (fepA/cirA/fecA/fhuA, fpvA, etc.) → REG by Fe limitation (Fur/PerR logic) with guardrails vs. ROS.
Peroxides/•OH/superoxide: katG/katE, sodA/sodB, ahpC/ahpF, trxA/trxB, gor → basal OE of katG/sodA, stress-inducible ahpC/trx.
DNA repair: uvrABC, phr, recA → constitutive/UV-inducible.
Regulators: OxyR/SoxRS (Gram-), PerR/SigB (Gram+).
pstSCAB–phoBR (Gram-) / pstSCAB–phoPR (Gram+) → REG via Pho promoters for low-P; add phoA/phn where organo-P needed.
FA remodeling: desA/desC (desaturases), cfa (cyclopropane FA) → OE or REG (cold/pressure/solvent); avoid over-stiffening.
Motility: flhDC (master), cheA/cheY, motA/motB → REG/QS toggle for particle-association vs. free-living.
EPS/export: wza/wzc/wzb (Gram-), eps/tapA–sipW–tasA (Bacillus matrix), pel/psl (Pseudomonas).
rpoS (σS) in many Gram-, sigB (σB) in Firmicutes → REG to gate costly defenses.
Heat/cold shock: rpoH (σ32), groESL, dnaKJ, ibpAB, cspA → inducible modules.
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.
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.
Field-mode priorities (environment-enriched engineering levers)
- Osmotic shock & salinity
- Iron acquisition (Fe-poor water)
- ROS & redox control (surface waters, metal-rich particles)
- UV/DNA damage repair (sunlit epilimnia)
- Phosphate scavenging (low-P lakes & particles)
- Sulfur & nitrogen scavenging (DOM-rich, sulfate/nitrate limited)
- Membrane fluidity & cold adaptation
- Motility/chemotaxis ↔ biofilm/matrix toggle (foraging vs sticking)
- Sporulation (last-ditch survival)
Knobs: opuA / opuC / opuD (GB/carnitine uptake), gbsAB (choline→glycine betaine), ± ectABC (ectoine; heterologous or native if present), MS channel yfkC (MscS-like).
Why field-up: Freshwater/estuarine microbes see rapid hypo-osmotic dips (rain/runoff) and patchy salt. Opu uptake fills compatible-solute pools fast; GbsAB converts choline to GB when available; ectoine is a high-value osmolyte for chronic salt/ desiccation; YfkC dumps solutes on sudden dilution to prevent lysis.
Suggestions: REG (salinity/σ^B): put opu and gbsAB under a σ^B or salt-responsive promoter; run yfkC at low-leak OE for “airbags always armed” without chronic leak. Optional: add ectABC(+ask) under a salt switch for brackish deployments. Guardrails: Too-high Opu overfills cytosol (viscosity/growth cost). Cap max expression; consider a “salinity AND growth” gate (e.g., σ^B AND growth-on).
Knobs: dhbACEBF (bacillibactin synthesis), feuABC (bacillibactin uptake), fhuBGC (ferrichrome), other TBDRs; feoAB (Fe²⁺ under microoxia); regulator fur (Fur).
Why field-up: Dissolved Fe is picomolar-nanomolar in many waters; siderophore biosynthesis/uptake dominates.
Suggestions: REG (Fe-limitation): drive dhb/feu/fhu from native Fur-repressed promoters (Fe-OFF = ON). Light OE of feoAB for hypolimnia/low O₂. ROS guardrails: Couple Fe-uptake to PerR/σ^B outputs (e.g., Oxy-like NOT gate) to avoid Fenton overload when H₂O₂ spikes. Pitfalls: Siderophore overproduction is metabolically pricey; use ceilings and OFF in Pi-replete, Fe-replete lab phases.
Knobs: katA (major vegetative catalase), katE (secondary), sodA, ahpCF, trxA/B, tpx, storers dps. Regulators: perR (peroxide), sigB (general stress), Spx (thiol-stress).
Why field-up: UV/light and metal recycling on particles drive H₂O₂ / O₂⁻ pulses; Bacillus relies on PerR (OxyR analog) and σ^B.
Suggestions: Basal OE: small katA / sodA baseline. Inducible: put ahpCF / tpx / trx on PerR- or σ^B-responsive promoters. Add a “redox fuse”: an Spx-activated kill-switch ceiling to avoid runaway ROS when Fe uptake is high. Pitfalls: Over-catalase can blunt oxidative signaling needed for acclimation; keep basal OE mild.
Knobs: phr (photolyase), uvrA/B/C (NER), recA.
Why field-up: Direct UV photoproducts in surface waters.
Do this: Constitutive low phr + UV-inducible NER. For dark deployments (hypolimnion/groundwater), keep them native to save energy.
Knobs: pstSCAB–phoPR (Pho regulon), phoA / phoD (secreted alkaline phosphatases), ± phosphonates (phn operon), cell-wall remodeling tuaABCDEFG (teichuronic acid synthesis under Pi limitation).
Why field-up: Pi is often limiting; Bacillus replaces wall teichoic acids with teichuronic acids to spare phosphate.
Do this: REG (Pho): use P_pstS / PhoPR-responsive promoters to drive high-affinity uptake and phoD secretion. Include tua under Pho to lock in the low-P envelope program (less Pi in the wall = more for growth). Pitfalls: Over-secretion of AP can be costly; meter via Pho activity reporter.
Knobs (S): ssuEADCB (alkanesulfonates), tauABCD (taurine).
Knobs (N): nasABC (assimilatory nitrate), nirBD (nitrite→NH₄⁺), regulators TnrA/GlnR.
Why field-up: Inorganic S/N can be scarce; organosulfur and nitrate/nitrite pulses are common.
Suggestions: put ssu/tau behind sulfur-limitation logic (CysB-like) and nas/nir behind TnrA-ON (N-limitation) to widen usable nutrient space.
Knobs: des (Δ5 desaturase), bkd (branched-chain FA precursor supply), fabF/B tuning.
Why field-up: Homeoviscous adaptation for cold/pressure; branched FAs in Gram+ modulate membrane rigidity.
Do this: Mild REG of des for cold regimes; upweight bkd for more iso/anteiso FAs in chill/low-energy deployments. Pitfalls: Over-desaturation can impair growth at moderate temperatures.
Motility knobs: sigD (σ^D master), fli/flg structural genes, cheA/cheY, motA/B.
Matrix knobs: epsA–O (EPS), tapA–sipW–tasA (amyloid fibers), bslA (hydrophobin).
Why field-up: Two modes matter: swim to find patches; stick to exploit particles/surfaces.
Suggestions: Build a QS/σ^B/energy-aware toggle: when carbon high + shear low → matrix ON (EPS/tasA/bslA); when carbon low/shear high → motility ON. Use the native regulators: Spo0A–SinI/SinR–SlrR–DegU to flip states cleanly (avoid half-on burden). Pitfalls: Matrix constitutive OE tanks growth in pelagic starvation; keep conditional.
Knobs: spo0A (master) + phosphorelay; Rap phosphatases.
Why field-relevant: True long-term survival; but not your default “field-mode growth”.
Suggestions: Keep sporulation competence intact but raise the threshold: e.g., require multi-input AND (carbon starvation + oxidative + high cell age). Provide a recovery path (germination genes) for lab passage. Pitfalls: Don’t accidentally wire everything to Spo0A and lock growth.
Lab-biased programs (make switchable or down-tuned in field mode):
- High-rate translation & ribosome biogenesis
- DNA replication & cell division
- PTS sugar uptake (simple lab sugars)
- Overflow metabolism (acetate/lactate)
- Heat-shock programs prominent at 30–37 °C
- Low-affinity phosphate transport
Knobs: rrn operons; ribosomal proteins (rpl/rps); tuf/fus/tsf/inf.
Why lab-up / field-down: Low specific growth rates in situ (stringent response) → less rRNA/tRNA/ribosome demand.
Engineering: Keep native control; if you use growth boosters in the lab, ensure hard OFF in field mode (ppGpp-sensitive promoters are your friend).
Knobs: dnaA/dnaN, gyrA/B, ftsZ/ftsA/sepF, divIC/ftsL.
Why lab-up: Rapid lab growth demands strong replication/division; in the field, cells pace themselves.
Engineering: Avoid constitutive overdrive; let starvation/dormancy signals suppress the divisome.
Knobs: ptsG, ptsH (HPr), ptsI (EI), manP (mannose PTS).
Why lab-up: PTS excels at high-flux glucose; natural DOM is dilute/complex → ABC/TRAP + SBPs are favored.
Engineering: Make PTS inducible for lab scale-up; default OFF in field mode.
Knobs: pta–ackA (acetate), ldh (lactate), poxB (pyruvate oxidase).
Why lab-up: Shake-flask, sugar-rich conditions; in situ carbon limitation doesn’t support overflow.
Engineering: Keep repressible; favor full respiration/fatty-acid use in field mode.
Knobs: HrcA regulon (dnaKJ, groESL, grpE), CtsR (clpC/P).
Why lab-up: Lab temperatures trigger these; ambient waters often activate cold/oxidative, not heat shock.
Engineering: Keep inducible; avoid high basal load in field mode.
Knobs: pitA (if present).
Why lab-up: Works fine in Pi-replete lab media; disfavored in low-P waters where Pst dominates.
Engineering: De-emphasize; rely on Pst/PhoPR.
Summary: Bacillus subtilis 168 Lab biased (down tune in field)
- High rate translation & ribosome biogenesis
- DNA replication & cell division
- PTS sugar uptake (simple lab sugars)
- Overflow metabolism (acetate, lactate)
- Heat shock regulons at 30–37 °C
Genes: rrn operons; rpl*/rps*; tufA; fusA; tsf; infA/B/C
Field Action: Default OFF in field; inducible for lab scale up
Bench Promoter: Inducible bench promoters (IPTG/xylose)
Hints: ppGpp/CodY on in field
Guardrail: Avoid energy/proteome drain in oligotrophy
Why: Lab programs elevated in rich, aerated culture
Genes: dnaA/dnaN; gyrA/B; ftsZ/ftsA/sepF; divIC/ftsL
Field Action: Default OFF in field; inducible for lab scale up
Bench Promoter: Inducible bench promoters (IPTG/xylose)
Hints: ppGpp/CodY on in field
Guardrail: Avoid energy/proteome drain in oligotrophy
Why: Lab programs elevated in rich, aerated culture
Genes: ptsG; ptsH; ptsI; manP
Field Action: Default OFF in field; inducible for lab scale up
Bench Promoter: Inducible bench promoters (IPTG/xylose)
Hints: ppGpp/CodY on in field
Guardrail: Avoid energy/proteome drain in oligotrophy
Why: Lab programs elevated in rich, aerated culture
Genes: pta ackA; ldh; poxB
Field Action: Default OFF in field; inducible for lab scale up
Bench Promoter: Inducible bench promoters (IPTG/xylose)
Hints: ppGpp/CodY on in field
Guardrail: Avoid energy/proteome drain in oligotrophy
Why: Lab programs elevated in rich, aerated culture
Genes: hrcA (dnaKJ, groESL, grpE); ctsR (clpC/P)
Field Action: Default OFF in field; inducible for lab scale up
Bench Promoter: Inducible bench promoters (IPTG/xylose)
Hints: ppGpp/CodY on in field
Guardrail: Avoid energy/proteome drain in oligotrophy
Why: Lab programs elevated in rich, aerated culture
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.
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.
Acinetobacter baylyi ADP1 suggested to up tune in field:
- Osmoprotection
- Choline→GB & regulation
- Aromatic DOM catabolism
- Fe acquisition
- ROS/UV & DNA repair
- Outer-membrane porins
- Lab-biased storage lipids
- Domestication context
ADP1 uses BCCT transporters (e.g., ACIAD3460) for glycine betaine; it has osmo-dependent and osmo-independent choline transporters; GB uptake improves high-salt survival.
betIBA and two BetT-like routes (osmo-independent BetT1 vs. osmo-dependent BetT2) described; wiring them to salinity/choline sensors matches physiology.
Native β-ketoadipate island (ben/cat/pca; pobA; BenM/CatM/PcaU) is a hallmark of ADP1 and is routinely up when aromatic substrates are present.
In Acinetobacter spp., iron uptake relies on TonB–ExbB–ExbD and numerous TBDRs; A. baumannii uses acinetobactin, while ADP1 is generally viewed as a non-pathogenic environmental strain that can pirate exogenous siderophores—so emphasize TBDRs/Feo and Fur-logic rather than siderophore biosynthesis. (Inference drawn from genus-level reviews + ADP1 genome resources.)
ADP1 shows ROS-linked responses under oxidative/biocide stress; pair catalases/SOD with PerR-like peroxide defenses and NER/photolyase for surface waters.
Nutrient vs. toxin influx trade-offs (OmpA/CarO/OprD-like) documented for Acinetobacter; use modest, context-dependent tuning.
ADP1’s wax ester pathway (atfA, acr1) is prominent under high C/N in the lab—handy for production, but usually a carbon sink in dilute waters.
Recent work catalogs lab domestication mutations in ADP1 that alter competence, carbon use, and aggregation—useful when reconciling lab vs. field behavior.
Acinetobacter baylyi ADP1 Lab biased/upregulated (suggested to down tune in field)
Genes: rrn operons; rpl/rps; tuf/fus/tsf/inf
Field Action: Keep native control; repress in field via ppGpp; lab only induction
Bench Promoter: Inducible bench promoters
Hints: ppGpp ON in field
Guardrail: Proteome burden in oligotrophy
Why: Ribosome fraction tracks growth rate
Genes: dnaA/dnaN; gyrA/B; ftsZ/ftsA/zipA/sepF
Field Action: Avoid constitutive OE; allow starvation/dormancy to suppress divisome
Bench Promoter: Inducible only
Hints: Starvation sensors gate OFF
Guardrail: Division push causes stress in dilute waters
Why: Replication/division downshift during limitation
Genes: PTS core (if present) + high flux glycolysis
Field Action: Default OFF in field; prefer high affinity ABC/SBPs
Bench Promoter: Induce with lab sugars only
Hints: Carbon limitation gates OFF
Guardrail: Inefficient at nM sugars
Why: Natural DOM is dilute/complex
Genes: acetate/lactate routes
Field Action: Keep OFF in field; favor respiration
Bench Promoter: Carbon/oxygen sensors
Hints: Repress when C limited
Guardrail: Low yield without benefit
Why: Overflow is lab artifact of high carbon + aeration
Genes: dnaKJ; groESL; grpE; clpC/P (HrcA/CtsR)
Field Action: Keep inducible; avoid high basal at ambient water temps
Bench Promoter: Native heat shock promoters
Hints: Only when >30 37°C
Guardrail: Chronic load taxes proteome
Why: Field programs skew to cold/oxidative
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.
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.
Below is a list of modules that are up repeatedly up in natural waters vs lab that are good targets to overexpress and modules that are typically down in natural waters which are good to reducing expression.
Environment-enriched modules
- Iron acquisition (Fe-poor water)
- Outer access
- Phosphate scavenging (P-poor water/particles)
- Carbon/osmoprotection tied to the mycomembrane
- ROS & redox defenses (surface waters / metal stress)
- Hypoxia / energy limitation (stratified lakes, biofilms)
- Envelope remodeling / permeability (nutrient-poor water)
Mycobactin / carboxymycobactin biosynthesis: mbt clusters (mbtI–mbtN). Action: REG by low-Fe (IdeR-off); mild OE ceiling. Why: core siderophores for Fe capture.
Exochelin pathway (M. smegmatis-specific): fxbA (+ exochelin biosynthetic/transport genes). Action: REG by low-Fe (IdeR-off). Why: additional extracellular siderophore in M. smegmatis.
Siderophore import/reduction: irtAB (inner-membrane ABC importer; reduces Fe-cMBT). Action: OE 1–2× with low-Fe promoter.
Type VII secretion for Fe uptake: ESX-3 locus (esxG/H, ecc, mycP3, etc.). Action: keep REG by Fe/Zn; avoid KO. Why: required for mycobactin-mediated iron acquisition.
Regulator: IdeR (DtxR-family). Action: keep intact; use IdeR-responsive promoters for “Fe-on” logic. Why: master Fe homeostasis; couples Fe uptake with oxidative stress defenses.
MspA/MspC porins. Action: OE mspA (± mspC) to raise solute/Fe flux; use native σ^A promoter or stress-tunable. Why: major hydrophilic conduit; porin loss reduces Fe/phosphate/glucose uptake.
High-affinity transport: pstSCAB–phoU1/phoU2. Action: REG via the SenX3–RegX3 system; avoid constitutive OE. Why: dedicated low-P uptake; two PhoU paralogs tune signaling.
Aux systems under low P: phnDCE (phosphonate). Action: REG by low-P; pair with P starvation reporters.
Trehalose recycling/uptake: LpqY–SugABC; treS, otsA/otsB for trehalose metabolism. Action: REG by stress; consider OE of LpqY–SugABC to save ATP in envelope turnover; “field-mode” trehalose pool.
Mechanosensitive channel (osmotic dips): mscL (and MscS-like homologs). Action: keep a low-leak OE baseline. Why: emergency solute dump under hypo-osmotic shocks.
Peroxides & superoxide: katG (I/II/III), sodA, ahpC/D, tpx, trx/gor. Action: basal OE of katG/sodA; put ahpC/tpx under ROS-inducible control. Why: M. smegmatis encodes multiple katG; ROS stress strongly induces this axis.
Dormancy/hypoxia regulon: dosR–dosS/dosT ± PrrAB cross-talk. Action: keep DosR circuit intact; you can drive “low-O₂ mode” cassettes from DosR targets. Why: essential for hypoxic survival; stabilizes ribosomes.
Porins: mspA/mspC OE as above. Why: improves influx of hydrophilic solutes/Fe.
Mycolic-acid desaturation: desA1, desA2 (regulated by MadR). Action: REG to tune fluidity; modest OE for cold/low-energy regimes; avoid over-stiffening. Why: desaturation is essential; MadR links envelope stress to desA1/2.
Cyclopropanation/methyltransferases: cmaA1/2, pcaA, mmaA1/2. Action: REG/KO to adjust permeability vs robustness; (pathogenesis-linked effects mostly from Mtb, but orthologs inform tuning in M. smegmatis).
GPL biosynthesis & export: mps/tmtpC/gpl cluster, mmpL11; groEL1 assists biofilm matrix. Action: REG by surface cues; OE to increase sticking when desired. Why: GPL acetylation affects sliding/biofilm; mmpL11 exports MA-lipids needed for biofilm.
Lab-enriched modules (often down in natural waters)
- High-rate translation & ribosome biogenesis
- DNA replication/division
- Heat-shock at 30–37 °C (classic lab temps)
- Low-affinity phosphate transport
- Overflow pathways (acetate/lactate) from sugar-rich shake flasks
rrn, rpl/rps, EF/Tu (tuf), EF-G (fus). Action: make repressible in “field mode.” Why: slow growth in situ; stringent response suppresses these. (General growth-law logic; also reflected under DosR programs in mycobacteria.)
dnaA/dnaN, ftsZ/ftsA/zipA. Action: avoid constitutive overdrive; keep native control for low-μ. (DosR-linked dormancy reduces replication pressure.)
dnaKJ, groEL/ES (keep but don’t force high basal expression for field mode). Why: ambient waters rarely trigger strong heat-shock; oxidative/cold responses dominate. (General)
pitA/B (when present). Action: prefer PstSCAB–PhoU–RegX3 under low-P; avoid Pit-only reliance.
Prefer respiration/fatty-acid utilization in field mode; don’t hard-wire pta–ackA/ldhA overflows. (General lab-bias.)
Overall Summary:
Mycobacterium smegmatis Field mode (environment enriched)
- Iron acquisition (mycobactin/exochelin)
- Outer permeability porins
- Phosphate scavenging
- Trehalose recycling & metabolism (envelope/osmoprotection)
- Mechanosensitive channel (osmotic dips)
Genes: mbtI mbtN (mycobactin/cMBT); fxbA (exochelin biosynth/transport); irtAB (siderophore import/reduction); ESX 3 (esxG/H, ecc, mycP3); IdeR (regulator)
Action: REG siderophore biosynth/import by low Fe; keep ESX 3 intact; mild OE irtAB
Promoter: IdeR OFF promoters (Fe limitation); ESX 3 native promoters
Hints: Fe sensor (IdeR OFF) AND ROS LOW gate
Guardrail: Couple Fe uptake to ROS LOW to avoid Fenton overload
Why: Core Fe capture in dilute waters; ESX 3 required for mycobactin Fe use
Genes: mspA, mspC
Action: Moderate OE (tunable promoter) to increase hydrophilic influx
Promoter: A like constitutive or mild inducible
Hints: Cap expression; combine with toxin sensitivity monitor
Guardrail: Higher porin levels increase antibiotic/toxin influx cap OE
Why: Porins dominate small solute entry; boosts Fe/P/glucose uptake in poor media
Genes: pstSCAB phoU1/phoU2; SenX3 RegX3 (Pho control); phnDCE (phosphonate)
Action: REG Pst via RegX3; enable phosphonate transport when Pi scarce
Promoter: PpstS/Pho responsive promoters
Hints: Use Pho activity reporter to meter AP load
Guardrail: Avoid constant Pho ON burden from secreted enzymes
Why: Low P waters select high affinity uptake and phosphonate salvage
Genes: LpqY SugABC (trehalose uptake/recycling); treS; otsA/otsB
Action: REG stress responsive; OE LpqY SugABC to recover trehalose from envelope turnover
Promoter: Native trehalose module promoters; stress responsive logic
Hints: Cap trehalose pool with ceiling or drain
Guardrail: Trehalose overaccumulation can slow growth
Why: Saves ATP and supports mycomembrane maintenance/osmoprotection
Genes: mscL (± MscS like)
Action: Low leak baseline OE
Promoter: Weak constitutive promoter
Hints: Leakage reduces turgor if too high
Guardrail: Avoid chronic leak
Why: Prevents lysis during rapid hypo osmotic shocks
Mycobacterium smegmatis Lab biased (down tune in field)
- High rate translation & ribosome biogenesis
- DNA replication & cell division
- Heat shock program (30 37 °C bias)
- Low affinity phosphate transport
- Overflow pathways (shake flask artifact)
Genes: rrn operons; rpl/rps; tuf/fus/tsf/inf
Action: Keep native control; repress in field via ppGpp; lab only induction
Promoter: Bench: Pami (acetamide) / Tet; Field: stringent responsive rrn promoters
Hints: ppGpp sensor gate for OFF in field
Guardrail: Avoid proteome/ATP burden in oligotrophy
Why: Ribosome fraction tracks ; low in situ growth rates
Genes: dnaA/dnaN; gyrA/B; ftsZ/ftsA/zipA/ftsQLB
Action: Avoid constitutive OE; allow starvation/dormancy to suppress divisome
Promoter: Bench inducible (Pami/Tet); field OFF via starvation cues
Hints: Prevent filamentation/stress at low nutrients
Guardrail: Constitutive push stresses cells in dilute waters
Why: Replication/division are downshifted in natural waters
Genes: dnaKJ; groEL/ES; hsp; proteases (lon, ftsH, clp)
Action: Keep inducible; avoid high basal in field
Promoter: Native heat shock promoters only
Hints: Reduce basal at ambient temps
Guardrail: Chronic load taxes proteome
Why: Field conditions emphasize cold/oxidative, not strong heat shock
Genes: pitA/pitB (if present)
Action: De emphasize; rely on Pst/RegX3 under low P
Promoter: Pho responsive control (PpstS)
Hints: Disable in Pi poor water
Guardrail: Pit inefficient at low Pi
Why: Low P environments select high affinity Pst
Genes: pta ackA; ldhA (if present); poxB like routes
Action: Keep OFF in field; favor respiration and FA utilization
Promoter: Carbon/oxygen sensors; bench only inducible
Hints: Avoid acid stress/low yield in low C waters
Guardrail: Overflow gives low yield with little benefit in situ
Why: Overflow requires high sugar + aeration; uncommon in natural waters