INTRODUCTION
Recent improvements in genetic engineering tools have enabled scientists to systematically engineer organisms that produce various value-added chemicals, including biofuels, therapeutic products, food, and bioplastics (
1–3). At first, most of these engineering efforts were focused on widely used model organisms, such as
Escherichia coli,
Saccharomyces cerevisiae, and
Synechococcus sp. MIT9509 (
4–8). This emphasis resulted in an array of genetic tools that have been effectively developed for valuable biomolecule biosynthesis and for conducting physiological studies (
8–22). However, the reliance on organic carbon as the primary carbon source poses a limitation for heterotrophic model organisms, contributing to elevated bioproduction costs (
15–17). Recent studies have highlighted numerous advantages in utilizing non-model organisms for bioproduction (
23–25). Over the past decade, one such group of microbes that has gained attention is the purple nonsulfur bacteria exemplified by
Rhodopseudomonas palustris TIE-1 (TIE-1) (
26–28),
Rhodospirillum rubrum (
29,
30) and
Rhodomicrobium (
21,
31). TIE-1, a Gram-negative purple nonsulfur photosynthetic bacterium is renowned for its versatile metabolism, rendering it an excellent host for diverse bioproduction and pathway studies (
26,
27). TIE-1 exhibits four primary metabolisms: chemoautotrophy, photoautotrophy, chemoheterotrophy, and photoheterotrophy (
26,
27). These different metabolisms enable TIE-1 to use a wide variety of carbon sources such as carbon dioxide (CO
2) and many organic acids. TIE-1 can use ammonium salts such as ammonium chloride (NH
4Cl) or fix nitrogen from dinitrogen gas (N
2) as a nitrogen source (
26). Moreover, it can use multiple electron sources including hydrogen (H
2) or ferrous iron (Fe (II)). One of the most appealing features of TIE-1 is its ability to acquire electrons directly from a poised electrode, which enables us to use it in microbial electrosynthesis (MES) (
27,
32–35). MES is a system in which microorganisms are used to produce valuable compounds using their ability to obtain electrons from the bioelectrical reactor (
33,
35,
36). Using electrons from a poised electrode or a solar panel-powered MES system, TIE-1 produces biodegradable plastic and biofuel using CO
2 as a carbon source, N
2 as a nitrogen source, and light as an energy source (
27,
37). These represented the first steps toward a sustainable and carbon-neutral process for bioproduction using TIE-1 in MES. Besides its ability to utilize various substrates, TIE-1’s metabolic diversity also makes it an extraordinary model organism for pathway investigation (
38,
39). For example, the use of RuBisCO mutants allowed us to study the association between the Calvin–Benson–Bassham (CBB) cycle in carbon fixation and extracellular electron transport (
40). Similarly, a TIE-1 ∆
pioABC mutant was used to investigate the electron uptake mechanism during photoferrotrophic and electrotrophic growth conditions (
38). During these studies, mutants were first generated and grown under heterotrophic growth conditions in which the electron uptake machineries were not involved. These strains were then switched to autotrophic and electron uptake growth conditions to further understand their role in metabolism (
38,
40). Not only do these studies provide insights into TIE-1’s metabolism, but they also open doors for a deeper understanding of other closely related purple nonsulfur bacteria, such as
Rhodopseudomonas palustris CGA009, which has been studied extensively for biohydrogen production (
41,
42).
The available genetic tools for TIE-1 are limited compared to widely used model organisms, with most tools being based on homologous recombination (
34,
40). Fig. S1 illustrates the two-step homologous recombination process for achieving gene integration in TIE-1. Although this process results in markerless strains, it is time-consuming, with an efficiency lower than 50% (
34). To reduce processing time and enhance efficiency, we explored phage recombination techniques for gene integration. This technique has gained attention in various bacteria, including
Methanosarcina (
43) and
Mycobacterium smegmatis (
44), due to its simple design and high efficiency (
45,
46). The φC31 phage recombinase is commonly utilized due to its ability to function independently of a helper protein, and the recombination is unidirectional (
47). For example, in
Clostridium ljungdahlii, a whole butyric acid synthesis pathway was integrated into its genome by φC31 recombinase (
45). In
Methanosarcina spp., the φC31 recombinase achieved genome editing efficiency that is 30 times higher than that of homologous recombination (
43) .
Among many value-added chemical products obtained from advanced genome engineering tools, bioplastics from microorganisms have become an attractive product (reviewed in (
48)). This is particularly pertinent due to the detrimental environmental impact of excessive plastic usage in recent years. Bioplastics preserve the advantageous properties of petroleum-based plastics, such as high durability, moldability, water, and heat resistance, while also offering biocompatibility, emerge as a promising alternative (
49–51). Moreover, numerous microorganisms possess the natural ability to degrade bioplastics, including the polyhydroxyalkanoate (PHA) family, either aerobically or anerobically, typically within a span of 5 to 6 weeks (
50–52). However, the high feedstock cost remains an obstacle to the bioplastic’s competitiveness in the market (reviewed in (
53,
54)). This issue can be addressed by using photoautotrophic microbes that can use cheap alternatives and waste feedstock (such as CO
2) (
27).
PHA stands out as the most extensively studied bioplastic (
48,
54). The PHA pathway consists mainly of
phaA, phaB, phaC, and
phaZ genes.
phaA encodes a ß-keto thiolase, while
phaB encodes an acetoacetyl-CoA reductase (
27). PhaC catalyzes the polymerization of PHA, whereas PHA depolymerase, PhaZ, catalyzes its mobilization during carbon starvation (
27). Additional proteins, such as PhaP and PhaR, have also been reported to contribute to the maturation and regulation of PHA granules (
55,
56). In
Paracoccus denitrificans, PhaR is characterized as a repressor of PHA synthesis and acts by binding to the intergenic region of the
phaC-phaP and
phaP-phaR genes (
55). However, PhaR is proposed to be an activator for PHA synthesis in
Cupriavidus necator in a PhaP-dependent and -independent manner. Deletion of the
phaR gene decreased PHA production in this organism (
56). We have previously reported that TIE-1 possesses one
phaR gene (Rpal_0531) using bioinformatics (
27).
To improve PHA production, several gene manipulations have been undertaken directly on PHA pathway genes or genes from other pathways that may impact or compete with the PHA biosynthesis pathway (
57–59). For instance, a study revealed that the deletion of the
phaZ gene in
Sinorhizobium meliloti increased PHA production compared to wild-type when utilizing formate generated through electrochemical CO
2 reduction (
57). This suggests that prevention of PHA degradation results in intracellular accumulation of PHA. Metabolic pathways such as glycogen production and nitrogen fixation are also potential competitors for bacterial PHA production (
58). In
Synechocystis sp. PCC 6803, PHA accumulation is reported to be linked to glycogen production under prolonged nitrogen starvation conditions. Mutants lacking the glycogen phosphorylase genes showed impaired PHA accumulation, supporting the link between glycogen and PHA synthesis under nitrogen starvation (NaNO
3) conditions (
58). Nitrogen fixation, which is a pathway highly demanding of electrons, could also present another competition to PHA production (
60). Furthermore, PHA accumulation has also been reported to be induced by nitrogen deprivation ((N
2) or NH
4Cl) in many bacteria (
41,
61,
62).
In another study, increase in PHA production was achieved by enhancing carbon fixation through the Calvin–Benson–Bassham (CBB) cycle in
Ralstonia eutropha (now
C. necator) (
60). This enhancement involved the heterologous overexpression of the RuBisCO gene from
Synechococcus sp. PCC 7002 in
Ralstonia eutropha. Consequently, the overexpression resulted in a substantial increase in cell density, measured by optical density, by up to 89.2%. Additionally, there was a significant augmentation of the mass percent of PHA production, reaching up to 99.7% (
60).
In this study, we used the φC31 integration system to integrate additional copies of the RuBisCO form I and II genes driven by the
PaphII constitutive promoter into the TIE-1 genome. Additionally, to increase PHA accumulation in TIE-1, we created mutants that lack key genes in the PHA pathway, particularly focusing on the
phaZ and the
phaR genes. The behavior of the mutants lacking the
phaR helped us elucidate whether
phaR is an activator or repressor of the PHA pathway in TIE-1. In addition to exploring genes within the PHA pathway, we also examined the impact of deleting genes in pathways that might potentially compete with the PHA synthesis pathway. These include the mutants that have been previously studied in biobutanol production in the TIE-1: Δ
gly mutant lacking glycogen synthase and the mutant lacking the two NifA regulators
nifA, Rpal_1624 & Rpal_5113, of the nitrogen fixation pathway of TIE-1 (
37). We also hypothesize that like
R. eutropha, overexpressing RuBisCO genes (form I and II) in TIE-1 could increase intracellular carbon abundance and hence increase PHA accumulation. We tested PHA production in all six strains and wild-type under a variety of growth conditions, including non-nitrogen-fixing conditions with NH
4Cl (referred to as non-nitrogen-fixing conditions throughout) and nitrogen-fixing conditions with N
2 gas (referred to as nitrogen-fixing conditions throughout).
Our results show that the deletion of the phaR gene increased PHA production (dry cell weight % wt/wt) when TIE-1 was grown photoheterotrophically with butyrate under non-nitrogen-fixing conditions. We also observed an increase in PHA production (dry cell weight % wt/wt) from the Δgly and ΔnifA under photoautotrophic growth conditions with H2 and under non-nitrogen-fixing conditions. PHA production increased in TIE-1 strains overexpressing RuBisCO form I and form I & II genes under photoheterotrophy with butyrate irrespective of the nitrogen source used and photoautotrophy with H2 under non-nitrogen-fixing conditions as well as photoelectrotrophically under nitrogen fixing conditions. We show that both gene deletion and overexpression can enhance PHA production by TIE-1. This work advances TIE-1 as a model organism for potential commercialization for PHA production and provides valuable insights for future genetic engineering endeavors aimed at enhancing bioplastic production in other purple nonsulfur bacteria.
ACKNOWLEDGMENTS
We would like to thank Dr. Joshua Blodgett for facilitating PHA analysis using LC-MS. We would like to thank Jungwoo Lee for proofreading the manuscript.
This work was supported by the following grants to A.B.: The David and Lucile Packard Foundation Fellowship (201563111), the U.S. Department of Energy (grant number DESC0014613), and the U.S. Department of Defense, Army Research Office (grant number W911NF-18-1-0037), Gordon and Betty Moore Foundation, National Science Foundation (Grant Number 2021822, Grant Number 2124088, Grant Number 2117198, and Grant Number 2300081), the U.S. Department of Energy by Lawrence Livermore National Laboratory under Contract DEAC5207NA27344 (LLNL-JRNL-812309), NIGMS grant (NIHR01GM141344), and a DEPSCoR grant (FA9550-21-1-0211). A.B. was also funded by a Collaboration Initiation Grant, an Office of the Vice-Chancellor of Research Grant, an International Center for Energy, Environment, and Sustainability Grant, and a SPEED grant from Washington University in St. Louis.
T.O.R., W.B., M.S., J.O., H.S., and E.C. performed all the experiments. R.K. assisted with the bioelectrochemical experiments. BG assisted with the genome assembly. T.O.R., W.B., and A.B. wrote the manuscript with input from all authors.