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. 2022 Aug 22;7(5):e00311-22. doi: 10.1128/msphere.00311-22

Laboratory Plasticware Induces Expression of a Bacterial Virulence Factor

Philipp Hansen a, Kristine von Bargen a,*, Alexandra Jünger-Leif a, Albert Haas a,
Editor: Sarah E F D’Oraziob
PMCID: PMC9599451  PMID: 35993764

ABSTRACT

Pollution with microplastic has become a prime environmental concern. The various ways in which human-made polymers and microorganisms interact are little understood, and this is particularly true for microplastic and pathogenic microorganisms. Previous reports demonstrated that expression of central virulence-associated protein A (VapA) of the pathogenic bacterium Rhodococcus equi is shut off at 30°C, whereas it is strongly expressed at 37°C, a temperature which may serve as an intrahost cue. Here, we show that cultivation at 30°C in disposable plastic tubes increases mRNA levels of vapA 70-fold compared to growth in conventional glass tubes. Strong expression of vapA in plastic tubes does not seem to be caused by a compound leaching from plastic but rather by tube surface properties. Expression stimulation during growth in plastic is regulated by the R. equi transcription regulators VirR and VirS, indicating that plastic-induced vapA expression is (co)regulated through the canonical vapA expression pathway. Our observations have important implications for the future analysis and assessment of environmental microplastic contaminations in that they show that, in principle, contact of pathogens with environmental plastic can increase their virulence.

IMPORTANCE Millions of tons small plastic pieces (microplastic) find their way into the environment every year. They pose digestive and toxicity problems to various life forms in soil, freshwater, and seawater. Additionally, microplastic offers an opportunity for microorganisms to attach and to become an important part of a “plastisphere community.” The significance of our study lies in the documentation of a sharp increase in production of a central virulence factor by a bacterial pathogen when the bacterium is in touch with certain makes of plastic. Although this feature may not reflect an increased health risk in case of this particular soilborne pathogen, our data disclose a new facet of how microplastics can endanger life.

KEYWORDS: Rhodococcus, gene expression, microplastic, pathogen, pollution, virulence

INTRODUCTION

Gram-positive Rhodococcus equi (also referred to as Rhodococcus hoagii or Prescottella equi) (1, 2) thrives in many environments but is generally associated with soil. R. equi is a facultative intracellular bacterium that can cause severe bronchopneumonia, particularly in young foals and in immunocompromised humans such as AIDS patients (3). Its main target cell is the alveolar macrophage (2), which patrols the lung and ingests inhaled microorganisms. Instead of being killed by macrophages, virulent R. equi multiplies within a membrane-bound compartment, the Rhodococcus-containing vacuole (47). The key to intramacrophage multiplication is the abundant production of virulence-associated protein A (VapA), whose gene is localized to a virulence plasmid. VapA pH-neutralizes the endocytic and phagocytic continua in macrophages, which is a key requirement for intracellular multiplication (6). VapA is produced only at a pathogenetically meaningful, host-associated temperature, i.e., above 34°C, but not at all at environmental temperatures of 30°C or below (811), thus preventing the waste of resources during growth in soil.

R. equi is routinely cultivated in glass tubes. Here, we present evidence that cultivation in standard labware plastic tubes can strongly increase expression of vapA. One possible cause for this effect could be compounds leaching from plastic labware. For example, in a study in 1980, Mithen et al. reported that certain batches of polystyrene petri dishes used in tissue culture are toxic to neurons (12). A landmark paper from Holt’s laboratory (13) described that the leaking of the compounds di(2-hydroxyethyl)methyldodecylammonium and 9-octadecenamide from common laboratory plastic tubes and pipetting tips inhibited the activity of human monoamine oxidase B (hMAO-B) in the test tube. These two compounds are so-called slip agents that are often incorporated into plastic during the manufacture extrusion process. In the following years, additional well-documented cases of plastic-organism interaction were published (14). Considerable public interest in plastic “extractables and leachables” (15) arose when it was shown that the plastic-softening phthalates can reduce male fecundity (16).

Many of the biological effects of plastics are likely mediated by microplastics (<5 mm). They are currently being given wide attention, with billions of potentially biologically active microplastic pieces produced from an estimated 4 to 12 million tons of plastic entering the oceans every year (17). This plastic debris has detrimental effects on sea life such as turtles, fish larvae, marine mammals, mussels (17), and coral reefs, where the likelihood of coral disease is greatly increased in the presence of microplastic (18, 19). Plastic, in particular microplastic, provides a surface for the formation of biofilms. Escherichia coli pathotypes and strains of the human pathogen Vibrio cholerae and of the fish pathogen Vibrio salmonicida have been identified on marine plastic debris (2023), although it has not been investigated whether the bacteria in these particular samples were virulent. It has been speculated that horizontal gene transfer between pathogenic bacteria could occur within plastic-associated biofilms (18, 24), resulting in accelerated evolution of pathogenic traits (25). However, this hypothesis remains to be tested, and further investigation into microbial gene regulation by human-made plastics is needed, in particular as microplastic also exists in animal intestines, where it could influence transcription of virulence and multiple types of metabolic genes.

Here, we show that the tight temperature regulation of VapA production in broth culture is countermanded. Although this change in expression may not enhance the threat of this particular pathogen to humans or animals, it sets a precedent for a phenomenon which could be a serious microplastic-associated health problem for wildlife, particularly for aquatic animals.

RESULTS AND DISCUSSION

Growth of virulent R. equi in plastic tubes can induce vapA expression at 30°C.

During our studies on R. equi virulence, we observed that VapA was suddenly strongly produced not only at 37°C but also at 30°C, which was in contrast to our earlier observations and those of others (911, 26). This new phenomenon apparently coincided with a switch from reusable glass tubes to disposable polypropylene (PP) tubes for the incubation of broth cultures. Follow-up experiments confirmed that VapA was clearly not produced at 30°C in glass tubes but surprisingly was robustly produced in disposable plastic tubes (Fig. 1A). Further analysis of plastic tubes from several vendors and made from different polymers showed that most polypropylene tubes tested induced vapA expression at 30°C to some degree, with Falcon tubes being slightly effective and Sarstedt Snap Cap tubes very effective (Fig. 1A, lane SC). Induction was also observed with Techno Plastic Products (TPP) polystyrene and Corning polyethylene terephthalate tubes (Fig. 1A), in spite of their different polymer chemistries, indicating that a general rather than specific plastic property may have been responsible for the effect. However, not all synthetic nonwettable surfaces induce vapA expression at 30°C: when tetrafluoroethylene (Teflon) tubes were used for cultivation, VapA production was not detected at 30°C (Fig. 1B). Similarly, siliconized polypropylene tubes did not enhance vapA expression (Fig. 1C). For brevity, the observed induction of vapA expression at 30°C is referred to as “vapA induction” here.

FIG 1.

FIG 1

VapA expression in various plastic tubes at 30°C by different R. equi isolates. (A) An overnight culture of R. equi 33701 at 30°C was diluted into fresh BHI at an OD600 of 0.1 and further grown at 30°C or 37°C in glass or plastic tubes for 18 h, as indicated. Proteins from equal numbers of bacteria were analyzed by anti-VapA Western blotting. VapA typically runs as up to three separate proteins with molecular weights between 15 and 18 kDa (11, 49). (B and C) Strain ATCC 33701 was grown in Teflon tubes (B) or in untreated (mock) or siliconized (silic) Sarstedt 13-mL Snap Cap polypropylene tubes (C) at 30°C or 37°C and processed as described above. (D) Cultures of R. equi strains 103, ATCC 33701, and 85F were grown in glass (G) or Sarstedt 13-mL Snap Cap polypropylene tubes and processed as described above. The immunoblots are representative of three independent experiments each. Corn, Corning Inc.; Epp, Eppendorf AG; Falc, Falcon Corning Inc.; Grei, Greiner; PP, polypropylene SC; Sar, Sarstedt AG; SC, Sarstedt Snap Cap; TPP, Techno Plastic Products AG; VWR, VWR International.

It is important to note that not all tubes, even those from them same batch and from the same producer, showed the same results. For example, different packing units of 13-mL PP tubes from Sarstedt (catalog no. 62.515.028) yielded either consistent (batch 8032411_MHD 30.6.2021), occasional (batch 9034511_MHD 11.2022), or no (batch 1032821_MHD 31.07.2024) vapA induction. Manufacturer information retrieved via the vendor (Sarstedt) stated that they were not aware of any alterations in the production process between these batches. This indicated that apparently subtle changes in the product process may have strong effects on the interaction of the product with microorganisms.

In an effort to make sure that VapA induction was not an isolated feature of just one virulent R. equi strain (strain ATCC 33701, isolated in Canada), additional well-established R. equi strains isolated from pneumonic foals at different places and times, strains 103 (Canada) and 85F (Japan), were tested using a reliably inducing tube batch. These isolates also showed the induction phenomenon (Fig. 1D). Strain 33701, previously used to study vapA expression regulation (27, 28), was used in further experiments unless indicated otherwise.

The inducing plastic factor is unlikely to be a leachable or an extractable compound.

To identify the expression-inducing element, we chose to analyze plastic surface-associated slip agents which had previously been implicated in interference with different biological processes. Slip agents are often nature-identical substances that are added during plastic manufacture to reduce the frictional resistance of product surfaces. They form a lubricant layer at the polymer-liquid interface, and therefore, they were prime candidates for diffusible agonists (17). The following frequently used slip agents were tested. (i) The first is oleamide, which is also a signaling molecule in cerebrospinal fluid (29). At 100 μM, it inhibited hMAO-A and -B in vitro by 80 to 90% (13). Jug et al. (29) showed that oleamide is a major leachable from labware plastic. Here, oleamide did not induce vapA expression even at 100 μM (Fig. 2A). (ii) Similarly, a 100 μM concentration of the slip agent stearamide, which is produced by mushrooms and which also has antimicrobial activity, did not induce vapA expression (30) (Fig. 2A). (iii) Erucamide is routinely used in plastic manufacturing (13) and can also act as an angiogenic factor (31). Here, at 100 μM, it did not stimulate VapA induction (Fig. 2B). (iv) The slip agent di-HEMDA [di(2-hydroxyethyl)methyldodecylammonium] as used in the Holt lab study (13) also did not stimulate VapA induction. Addition of up to 10 μM did not promote VapA induction. For comparison, human hMAO-B was inhibited by 80% in 10 μM di-HEMDA, and concentrations higher than 10 μM inhibited R. equi growth. In summary, none of these prime candidate compounds induced vapA expression.

FIG 2.

FIG 2

VapA expression at 30°C is not induced by supplements commonly used in plastic manufacturing. (A and B) A 30°C overnight culture of R. equi 33701 was diluted into fresh BHI at an OD600 of 0.1 and grown for 18 h at 30°C or 37°C in glass tubes supplemented with (A) oleamide or stearamide or (B) erucamide or di-HEMDA at the indicated concentrations (micromolar units). Lanes labeled “0” contain the respective carrier controls. Sample buffer extracts of equal numbers of bacteria were analyzed as for Fig. 1. Top panels show an approximately 6-kDa loading control protein detected by R. equi antiserum. The protein was less strongly expressed in the presence of ethanol. (C) An overnight culture of R. equi 33701 at 30°C was diluted into fresh BHI broth at an OD600 of 0.1 and grown for 18 h in Sarstedt Snap Cap tubes that had been pretreated for 2 days at 21°C as indicated or in untreated glass tubes. Bacteria were grown at 30°C for 18 h (as for Fig. 1), and the bacteria were analyzed (Tube) or shaken in glass tubes supplemented with 5% (by volume) of the respective 2 day wash supernatant solution (Solvent). EtOH, ethanol; Isop, isopropanol; MeOH, methanol; DMSO, dimethyl sulfoxide. The immunoblots are representative of three independent experiments.

To further test whether substances leaching from plastic would induce vapA expression, we washed a presumably present leaching compound from plastic tubes and transferred it to glass tubes, as described in reference 13. In detail, sterile broth media which had been shaken overnight at 30°C in plastic tubes were used for subsequent bacterial culture in glass tubes. These conditioned media did not induce vapA expression at 30°C during the next 24 h (data not shown). To further force the release of potentially relevant leachates or extractables, we preincubated unused plastic tubes for 2 days with water or sterile broth or any of the organic solvents ethanol, methanol, isopropanol, acetone, and dimethyl sulfoxide (DMSO). Previous studies recommended this treatment for efficient release and collection of transferable, more hydrophobic compounds (13, 29). However, these pretreatments did not reliably reduce the ability of plastic to induce VapA expression in subsequent R. equi cultivation at 30°C; i.e., the reduced expression seen in this experiment after acetone pretreatment (Fig. 2C) was not reproduced in other experiments. In a converse approach, the organic eluates were added to fresh brain heart infusion (BHI) broth at 5% (by volume) in glass tubes for growth experiments at 30°C, which never led to any vapA induction (Fig. 2C). Therefore, extraction of a putative inducer did not reduce the expression effect, nor was a putative inducer transferred into fresh (glass) tubes.

In summary, induction could occur with different types of tubes representing entirely different compositions and modes of production (polypropylene, polystyrene, polyethylene terephthalate) and was not influenced by prewashing the tubes with organic compounds. No inducing leachate could be transferred from one tube to another, and purified slip agents that had previously been identified to interfere with biological reactions did not induce vapA expression either. These data indicated that leachates are not the sought-after inducers but that some nonmobilizable property of the system induced vapA expression.

Induction ability of Sarstedt polypropylene is lost upon heating.

Hypothesizing that the structure of plastic rather than its compounds had an effect on R. equi gene expression, we heated the tubes, altering the structure of polypropylene to a more crystalline state and causing an increase in haze and stickiness (32) (Fig. 3A). Heating of Sarstedt Snap Cap tubes in dry heat at 121°C for 120 min (Fig. 3B) or in an autoclave (Fig. 3C) led to a complete loss of their capability to stimulate VapA production, and transferring BHI broth that had been autoclaved within the PP tube to a glass tube to serve as fresh growth medium for R. equi did not result in vapA induction (Fig. 3A). These data are best interpreted as showing that the inducing factor is not some leachable substance from the plastic ware but a physical tube property. They also agree well with the observed loss of induction after altering the tube surface by siliconization (Fig. 1C) and with the concurrent inability to remove or transfer an active component by incubation of tubes with solvents (Fig. 2C).

FIG 3.

FIG 3

Sarstedt Snap Cap culture tubes lose the ability to induce VapA expression during heating at 121°C. (A) Sarstedt Snap Cap tubes left for 2 h at ambient temperature (mock) or 121°C dry heat are shown. Note the increased turbidity of the heated tube. (B) Autoclaving. An overnight culture of R. equi 33701 at 30°C was diluted into fresh BHI broth at an OD600 of 0.1 and grown for 18 h in glass tubes or Snap Cap tubes that had been untreated (mock) or autoclaved (autocl) at 121°C. “BHI transfer” represents a sample in which the BHI broth from an autoclaved Snap Cap tube was transferred into a glass tube and vapA expression during growth at 30°C was assessed. In all cases, vapA expression was quantified by VapA Western blotting and blot scanning, and the blot signal for the glass/37°C sample was set as 100% in each experiment. Three independent experiments were performed, and the means and standard deviations (SD) are shown. (C) Dry heat. A Western blot representative of three experiments developed with anti-VapA shows samples as generated for panel B but in regular glass tubes or in Snap Cap tubes pretreated (121°C) or not (mock) in a dry heat cabinet for 120 min. Growth temperature was 30°C or 37°C, as indicated. As a loading control, we used rabbit antiserum to R. equi as for Fig. 2A and B.

Stimulation of VapA expression by plastic is regulated through the VirR/VirS pathway.

Even though the precise signaling mode for vapA induction was unclear, we wondered whether induction was dependent on the proteins which regulate vapA transcription in the physiological setting. Normally, vapA expression is increased by raising the growth temperature to about 37°C and, to some degree, by lowering the pH (10, 11, 28, 33). It is noteworthy that the culture medium pH did not decrease in any tube throughout the experiments. Temperature and pH are relayed in an unknown fashion to the LysR-type transcription factor VirR, whose gene is also localized to the virulence plasmid (9, 10, 27, 28). VirR is constitutively expressed, most likely through the principal sigma factor (26), and cooperates with the orphan two-component response regulator VirS in vapA regulation (34) (Fig. 4). VirS expression is induced when VirR is activated directly or indirectly by signals such as high environmental temperature (9). VirS then promotes transcription of vapA (Fig. 4). Activation of VirS may uncanonically occur without phosphorylation by a histidine kinase (10). In summary, the transcription of virR is largely temperature independent, whereas expression of virS is dependent on high temperature.

FIG 4.

FIG 4

Induction of VapA expression at 30°C depends on the virR/virS regulatory system. Overnight cultures of R. equi 103 and its isogenic deletion mutants 103/ΔvirR, 103/ΔvirS, and 103/ΔvcgB, grown at 30°C, were diluted into fresh BHI broth at an OD600 of 0.1 and grown for 18 h in glass tubes (G) or Sarstedt Snap Cap tubes (PP) at the indicated temperatures. Extracts of equal numbers of bacteria were analyzed for vapA expression by Western blotting. A representative blot from three independent experiments is shown.

We used virR or virS deletion mutants of the virulent strain 103 (35) and tested if plastic-driven vapA induction occurred in the absence of either gene, i.e., whether there is an alternative route of expression stimulation. vapA expression was strongly induced in wild-type bacteria grown at 37°C in glass tubes, and expression was strongly reduced in a ΔvirR and virtually absent in a ΔvirS background (Fig. 5). The very weak vapA expression in the ΔvirR background was similar at 30°C and 37°C, hinting once more that VirR is the constitutively expressed integrator of environmental signals. A vcgB (vapA-coexpressed gene B) deletion mutant (36), constructed in strain 103 using the same strategy as for the ΔvirR and ΔvirS strains (35), was used as a control strain for possible genetic manipulation side effects and behaved like wild-type bacteria (Fig. 5). Clearly, the expression patterns of plastic-grown R. equi were as strongly influenced by the mutations as expression at 37°C in glass-grown cells. In summary, plastic-mediated vapA induction at 30°C followed, at least in central parts, the same pathway as high-temperature induction in glass.

FIG 5.

FIG 5

Quantitative real-time PCR of genes involved in vapA expression. Total RNA of R. equi 33701 was isolated from cultures grown for 18 h in glass tubes at 30°C or 37°C, as indicated, or in Sarstedt Snap Cap polypropylene (PP) tubes at 30°C and further analyzed by quantitative real-time PCR. Values shown indicate the fold change in vapA mRNA abundance (log10) between bacteria from 30°C/glass cultures and from the respective test sample. alkB denotes the transcripts from an alkane monooxygenase gene. The dotted line marks the “no change” horizon. Data are means and standard deviations from three independent experiments.

To analyze gene regulation with a technology independent of immunoblotting, we quantified vapA transcription during cultivation at 30°C or 37°C in glass or in Sarstedt Snap Cap tubes using quantitative PCR (qPCR). vapA transcription in R. equi grown in glass at 37°C was induced 233-fold compared to expression at 30°C, similar to reports by others (36). The transcription increase of virR at 37°C in glass was a more moderate 7-fold, and that of virS expression was 93-fold, all in good agreement with previous observations (26). The chromosomal alkB gene, coding for an alkane monooxygenase, was included as a negative control (Fig. 6).

FIG 6.

FIG 6

Working model of VapA transcriptional regulation modified from reference 10. Increased temperature and moderately low pH act on the constitutively expressed LysR-type transcription regulator VirR in an unknown way. VirR then stimulates transcription of the icgA operon, including the virS gene. The newly produced VirS protein, an orphan two-component signal transduction response regulator, and then strongly upregulates vapA transcription. We show in this study that plastic-mediated induction of vapA expression at 30°C uses at least part of the same pathway through VirR, although the high-temperature requirement is circumvented. P, promoter.

In comparison, during growth in reliably “bioactive” Sarstedt polypropylene tubes, there was no increase in the virR mRNA level, whereas the virS mRNA level increased 25-fold and vapA mRNA increased a substantial 68-fold (Fig. 6). Therefore, the vapA transcription patterns during growth in glass at 37°C paralleled those of growth in plastic at 30°C, even though the induction levels upon plastic contact were lower than those in glass. In summary, this indicated that the same regulatory proteins participate in regulation of vapA expression during growth in plastic at 30°C as at elevated temperatures in glass (Fig. 4).

Conclusion.

We present here the first evidence that contact with human-made plastic can dramatically change the regulation of a central virulence gene in a pathogenic bacterium. Occurrence of potentially pathogenic bacteria on environmental plastic has been described (2023), and the possibility of plastic-driven pathogen gene regulation has been discussed (19, 37) but remained speculative. Although we did not identify a hypothetical “plastic sensor” in this study, our data show that expression induction at 30°C occurred through transcriptional regulation by the virulence plasmid-encoded VirR and VirS proteins, which also participate in the high-temperature-and-low-pH mode of expression induction (10). We have further shown that induction was not attributable to any of several plastic slip agents which can interfere with biological reactions. We present evidence that there was no leakage of a bioactive plastic substance from within plastic into the growth medium and neither was a potential soluble expression-stimulating factor extracted with either of several organic solvents. Heating of the tubes destroyed their capability to induce vapA expression and also caused an increase in surface polarity (38), microscopic changes in surface structure, and changes in crystallinity (39), yet the precise cause of loss of vapA induction remains enigmatic. However, together with the Teflon and silicone tube experiments, our data point to a role of tube surface characteristics in vapA induction.

It is not clear whether the induction phenomenon described here bears any relevance to R. equi-caused disease, yet it is interesting that R. equi growing on plastic catheters can cause bacteremia in cancer patients (40). Additionally, reports by others show that rhodococci, as ubiquitous environmental degraders, can be closely associated with environmental plastic (4143). Collectively, our data allow at least four relevant conclusions: (i) contact with plastic can strongly influence the expression of bacterial virulence genes, (ii) several kinds of plastic can regulate expression of the same gene, (iii) induction is dependent on surface characteristics of plastic, and (iv) phenomena like this could further increase the danger when plastic microparticles with “artificially” induced virulence or metabolic genes are ingested. Taken together with the recent observations that ingested microplastics can change the integrity of intestines and the composition of intestine-associated microbiotas and increase the carriers’ inflammatory status (44, 45), our results show that all these factors can cooperatively compromise the health of wildlife.

MATERIALS AND METHODS

Chemicals and antibodies.

All standard chemicals were of analysis grade and purchased form Sigma-Aldrich, Carl Roth, or Fisher Scientific. Oleamide (Sigma-Aldrich, catalog no. O2136) was dissolved at 100 mM in DMSO, erucamide (Sigma-Aldrich; catalog no. 90082) at 50 mM in isopropyl alcohol, and stearamide (Cayman Chemical, catalog no. 21087) at 50 mM in ethanol. di(2-hydroxyethyl)methyldodecylammonium (di-HEMDA) was purchased from Watson International, Ltd. (Kunshan City, Jiangsu, China), and dissolved at 100 mM in Milli-Q water. Peroxidase-coupled goat anti-mouse secondary antibody (catalog no. 115-035-062, batch 134308) was from Jackson ImmunoResearch. The manufacturers of plastic tubes, catalog numbers, and batch numbers are listed in Table 1.

TABLE 1.

Tubes used for cultivation of R. equi

Type Material Manufacturer Catalog no. Batch no.
Tube,a 13 mL PP Sarstedt 62.515.028 8032411
Tube, 15 mL PP Sarstedt 62.554.502 0040821
Tube, 13 mL PTFEb Fisher Scientific 16255971
Centrifuge tube, 11 mL PC Nunc 347708 167259
Centrifuge tube, 15 mL PET Corning 430053 09118003
Conical tube, 15 mL PP Eppendorf 0030.122.151 H176351H
Conical tube, 15 mL PP Falcon 3552096 15418105
Centrifuge tube, 15 mL PP VWR 5250604 180606058
Tube, 14 mL PP Greiner Bio One 187261 E1511359
Tube, 15 mL PP Greiner Bio One 188271 E161239J
Centrifuge tube, 15 mL PS TPP 91115 20120447
Glass tubes, 16 by 160 mm Glass DKW Life-Sciences 26131210
Glass tube lids Aluminum Schütt Labortechnik 3.620.713
a

Referred to as “Snap Cap.”

b

Polytetrafluoroethylene (Teflon).

Bacteria and cultivation.

R. equi strains 103, 103/ΔvirR, 103/ΔvirS, and 103/ΔvcgB (35) were kindly provided by John F. Prescott (University of Guelph, ON, Canada) and R. equi 85F (46) by Axel Hartke (University of Caen Normandy, Caen, France). R. equi ATCC 33701 was from the American Type Culture Collection (Manassas, VA, USA). Bacteria were maintained on BBL brain heart infusion (BHI; Becton Dickinson, catalog no. 90000-060) agar plates at 30°C. For experiments, bacteria were grown overnight in glass tubes in a 10-mL BHI starter culture under noninducing conditions (pH 7, 30°C). This pH did not decrease (and, therefore, possibly induce vapA expression) throughout the cultivation. The starter culture was diluted into 3 mL of fresh BHI at an optical density at 600 nm (OD600) of 0.1 and grown further at 30°C or 37°C for 18 h at 200 rpm in glass or plastic tubes, as indicated. Polytetrafluoroethylene tubes did not come with a serial cap and were covered with sterile aluminum foil during cultivation. Where indicated, glass tubes and Snap Cap tubes were covered with a silicone layer by using 5 mL organopolysiloxane in heptane (Sigmacote; Sigma-Aldrich-Merck, catalog no. SL2) to fill the tubes, and the tube was swirled to cover the whole inner surface. The formation of a silicone layer was almost instantaneous. Tubes were dried overnight to evaporate the heptane solvent. Before use, tubes were rinsed repeatedly with Milli-Q water. Where indicated, Sarstedt 13-mL tubes were autoclaved with aluminum foil instead of their plastic caps because these were heat sensitive. The sterile caps were placed back on the tubes after autoclaving.

Analysis of VapA expression.

Bacterial suspensions, cultivated as described above, were carefully removed from the culture tubes, transferred into fresh tubes, harvested by centrifugation for 3 min at 7,000 × g in a microcentrifuge, washed once with phosphate-buffered saline (PBS), and resuspended in PBS. Bacteria equivalent to OD600 of 0.1 (1.5 × 107 bacteria) for Western blotting or 0.01 (1.5 × 106 bacteria) for dot blot analysis were heated in SDS sample buffer for 10 min at 95°C and centrifuged for 3 min at 7,000 × g, and the supernatants were separated by SDS-gel electrophoresis and transferred onto nitrocellulose membranes (immunoblotting; Carl Roth [Karlsruhe, Germany], catalog no. HP40.1) or directly spotted onto nitrocellulose membrane in equal volumes (immuno-dot blotting). Membranes were incubated with murine anti-VapA primary monoclonal antibody (Santa Cruz Biotechnology; clone E-6, sc-390576, batch B0216) at a dilution of 1:1,000 for 1 h at ambient temperature (dot blotting) or 18 h at 4°C (Western blotting) and developed with horseradish peroxidase (HRP)-coupled secondary antibody (Dianova, catalog no. 115-035-062) at 1:10,000 for 1 h at ambient temperature followed by enhanced chemiluminescence (SuperSignal West Pico Plus; Thermo Scientific) and exposure to X-ray film (Super RX-N; Fujifilm, Japan). This VapA monoclonal antibody recognizes exclusively VapA, as validated by the complete absence of signal in vapA deletion strain samples (6). Where indicated, blots were probed with a custom-made polyclonal mouse antibody raised against formaldehyde-fixed R. equi 103- (strain isogenic to strain 103 but cured of the virulence plasmid). For solvent treatment of plastic tubes before cultivation of bacteria, 6 mL of the indicated solvents was used to fill the closed tubes, and the tubes were shaken at 21°C for 48 h in a rotary shaker at 60 rpm. Solvents were collected in glass tubes, and the treated tubes were washed three times with distilled Milli-Q water before 3 mL fresh BHI broth was added and inoculated with bacteria as indicated. In parallel, glass tubes were filled with 3 mL BHI broth plus 150 μL of one of the “solvent eluates” and used for inoculation with bacteria to determine whether the eluates would have any effect on VapA induction. At this concentration of solvents, growth of the bacteria was not affected.

RNA isolation and cDNA synthesis.

R. equi total RNA was isolated from cultures grown for 18 h in glass tubes at 200 rpm and 30°C or 37°C, as indicated, or from cultures grown in Sarstedt Snap Cap tubes at 30°C. Of this, 1 × 109 cells were harvested by centrifugation for 5 min at 17,000 × g, resuspended in 1 mL of RNAlater solution (Thermo Scientific, catalog no. AM2070) to stabilize RNA, and stored at 4°C. Total RNA was isolated using a RiboPure-Bacteria kit (Invitrogen, catalog no. AM1925) according to the manufacturer’s instructions, except for the disruption step, which was performed in a precooled TissueLyser LT instrument (Qiagen, catalog no. 85600) for 20 min at 50 Hz. To eliminate DNA, the DNase I treatment step was performed. RNA yield and purity were determined by UV absorbance in a spectrophotometer at 260 nm and 280 nm. An A260/A280 ratio between 1.8 and 2.0 was considered indicative of pure RNA. cDNA was synthesized from 1 μg of total RNA using the iScript cDNA synthesis kit (Bio-Rad, catalog no. 1708891) according to the manufacturer’s instructions in a Mastercycler personal thermal cycler (Eppendorf) applying the following Bio-Rad standard protocol: priming for 5 min at 25°C, reverse transcription for 20 min at 46°C, reverse transcriptase inactivation for 1 min at 95°C, and a hold at 4°C.

Real-time quantitative PCR (RT-qPCR).

Before the gene expression assays, primer pairs were validated by preparing a 5-point standard curve (10-fold dilution series) of the positive control (37°C glass). Reaction efficiency (E) was calculated for each pair as 101−s, where s is the slope of the standard curve. Assay specificity was verified by running a melt curve (47). The oligonucleotides and the E values are listed in Table 2. The quantitative real-time PCR was performed using SsoFast EvaGreen Supermix (Bio-Rad, catalog no. 172-5200) in a 10-μL reaction volume. The cycling conditions for amplification in a Bio-Rad CFX96 real-time PCR system controlled by the CFX 3.1 software are listed in Table 3. gapdh and gyrB were used as reference genes for normalization. Relative gene expression was calculated as described in reference 48.

TABLE 2.

Oligonucleotides used in this study and their reaction efficiencies

Oligonucleotide Sequence (5′-3′) Efficiency (%)a
alkB-FW AAGTGGCCGTAGAACGACTG 105.1
alkB-RV AACTCGGCCACAAGAAGGAC
GAPDH-FW TCACCGTCAACCTGTCGAAG 107.6
GAPDH-RV ACTTCAGGATGCCCTTCAGC
gyrB-FW GATCTACATCGTGGAGGGCG 99.2
gyrB-RV GACGTTGATGATCTTGCCGC
icgA-FW GATCTAGGTCTCAAGCCCGC 98.1
icgA-RV CAAAAACCCAGGGCAAGACG
orf3-FW ACCAAGCCAGCCTTATCGTC 105.5
orf3-RV GAGGATGGGGTGTTCTTCGG
sig70-FW CCACCAACCTCTTCCTGGAC 107.7
sig70-RV GTCGTGGTAGATCTGCTCGG
vapA-FW AGAGCAGCAGTACGACGTTC 109.3
vapA-RV TCGCCATCGAAGACCTTTCC
vapH-FW ACACACGACCTGCCTACTTG 95.3
vapH-RV TGTCACTGTGAGTCGATGGC
virR-FW GAGACCCACCAAAGAGACCG 105.8
virR-RV CGGTTTGCTAGAAACGCGAG
virS-FW TCGACCTGCTCGCATACTTC 108.4
virS-RV TGACGTGTACAGTGACCGTG
a

Reaction efficiency was determined as stated in Materials and Methods.

TABLE 3.

Cycling conditions for real-time PCR

Cycling step Temp (°C) Time (s) No. of cycles
Enzyme activation 95 30 1
Denaturation 95 5 40
Annealing/extension 60 5 40
Melt curve 65–95a 5 (per step) 1
a

In 0.5°C increments.

ACKNOWLEDGMENTS

We thank Jens Wohlmann for technical support, John Prescott (University of Guelph, Canada) and Axel Hartke (University of Caen Normandy, France) for bacterial strains.

Financial support was through a grant of the Volkswagen Foundation (VW_A127424_Haas) in their Experiment! program and through the Deutsche Forschungsgemeinschaft (HA1929/14-1).

Contributor Information

Albert Haas, Email: ahaas@uni-bonn.de.

Sarah E. F. D’Orazio, University of Kentucky

REFERENCES

  • 1.Vázquez-Boland JA, Meijer WG. 2019. The pathogenic actinobacterium Rhodococcus equi: what’s in a name? Mol Microbiol 112:1–15. doi: 10.1111/mmi.14267. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Prescott JF. 1991. Rhodococcus equi: an animal and human pathogen. Clin Microbiol Rev 4:20–34. doi: 10.1128/CMR.4.1.20. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Gundelly P, Suzuki Y, Ribes JA, Thornton A. 2016. Differences in Rhodococcus equi infections based on immune status and antibiotic susceptibility of clinical isolates in a case series of 12 patients and cases in the literature. Biomed Res Int 2016:2737295. doi: 10.1155/2016/2737295. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Hondalus MK, Mosser DM. 1994. Survival and replication of Rhodococcus equi in macrophages. Infect Immun 62:4167–4175. doi: 10.1128/iai.62.10.4167-4175.1994. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.Willingham-Lane JM, Berghaus LJ, Giguère S, Hondalus MK. 2016. Influence of plasmid type on the replication of Rhodococcus equi in host macrophages. mSphere 1:e00186-16. doi: 10.1128/mSphere.00186-16. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.von Bargen K, Scraba M, Krämer I, Ketterer M, Nehls C, Krokowski S, Repnik U, Wittlich M, Maaser A, Zapka P, Bunge M, Schlesinger M, Huth G, Klees A, Hansen P, Jeschke A, Bendas G, Utermöhlen O, Griffiths G, Gutsmann T, Wohlmann J, Haas A. 2019. Virulence-associated protein A from Rhodococcus equi is an intercompartmental pH-neutralising virulence factor. Cell Microbiol 21:e12958. doi: 10.1111/cmi.12958. [DOI] [PubMed] [Google Scholar]
  • 7.Zink MC, Yager JA, Prescott JF, Fernando MA. 1987. Electron microscopic investigation of intracellular events after ingestion of Rhodococcus equi by foal alveolar macrophages. Vet Microbiol 14:295–305. doi: 10.1016/0378-1135(87)90117-9. [DOI] [PubMed] [Google Scholar]
  • 8.Byrne BA, Prescott JF, Palmer GH, Takai S, Nicholson VM, Alperin DC, Hines SA. 2001. Virulence plasmid of Rhodococcus equi contains inducible gene family encoding secreted proteins. Infect Immun 69:650–656. doi: 10.1128/IAI.69.2.650-656.2001. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Kakuda T, Miyazaki S, Hagiuda H, Takai S. 2015. Transcriptional regulation by VirR and VirS of members of the Rhodococcus equi virulence-associated protein multigene family. Microbiol Immunol 59:495–499. doi: 10.1111/1348-0421.12277. [DOI] [PubMed] [Google Scholar]
  • 10.Kakuda T, Hirota T, Takeuchi T, Hagiuda H, Miyazaki S, Takai S. 2014. VirS, an OmpR/PhoB subfamily response regulator, is required for activation of vapA gene expression in Rhodococcus equi. BMC Microbiol 14:243. doi: 10.1186/s12866-014-0243-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Takai S, Iie M, Watanabe Y, Tsubaki S, Sekizaki T. 1992. Virulence-associated 15- to 17-kilodalton antigens in Rhodococcus equi: temperature-dependent expression and location of the antigens. Infect Immun 60:2995–2997. doi: 10.1128/iai.60.7.2995-2997.1992. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Mithen FA, Cochran M, Johnson MI, Bunge RP. 1980. Neurotoxicity of polystyrene containers detected in a closed tissue culture system. Neurosci Lett 17:107–111. doi: 10.1016/0304-3940(80)90070-1. [DOI] [PubMed] [Google Scholar]
  • 13.McDonald GR, Hudson AL, Dunn SMJ, You H, Baker GB, Whittal RM, Martin JW, Jha A, Edmondson DE, Holt A. 2008. Bioactive contaminants leach from disposable laboratory plasticware. Science 322:917. doi: 10.1126/science.1162395. [DOI] [PubMed] [Google Scholar]
  • 14.Olivieri A, Degenhardt OS, McDonald GR, Narang D, Paulsen IM, Kozuska JL, Holt A. 2012. On the disruption of biochemical and biological assays by chemicals leaching from disposable laboratory plasticware. Can J Physiol Pharmacol 90:697–703. doi: 10.1139/y2012-049. [DOI] [PubMed] [Google Scholar]
  • 15.Dorival-García N, Carillo S, Ta C, Roberts D, Comstock K, Lofthouse S, Ciceri E, D’Silva K, Kierans G, Kaisermayer C, Lindeberg A, Bones J. 2018. Large-scale assessment of extractables and leachables in single-use bags for biomanufacturing. Anal Chem 90:9006–9015. doi: 10.1021/acs.analchem.8b01208. [DOI] [PubMed] [Google Scholar]
  • 16.Fiandanese N, Borromeo V, Berrini A, Fischer B, Schaedlich K, Schmidt J-S, Secchi C, Pocar P. 2016. Maternal exposure to a mixture of di(2-ethylhexyl) phthalate (DEHP) and polychlorinated biphenyls (PCBs) causes reproductive dysfunction in adult male mouse offspring. Reprod Toxicol 65:123–132. doi: 10.1016/j.reprotox.2016.07.004. [DOI] [PubMed] [Google Scholar]
  • 17.Hahladakis JN, Velis CA, Weber R, Iacovidou E, Purnell P. 2018. An overview of chemical additives present in plastics: migration, release, fate and environmental impact during their use, disposal and recycling. J Hazard Mater 344:179–199. doi: 10.1016/j.jhazmat.2017.10.014. [DOI] [PubMed] [Google Scholar]
  • 18.Lamb JB, Willis BL, Fiorenza EA, Couch CS, Howard R, Rader DN, True JD, Kelly LA, Ahmad A, Jompa J, Harvell CD. 2018. Plastic waste associated with disease on coral reefs. Science 359:460–462. doi: 10.1126/science.aar3320. [DOI] [PubMed] [Google Scholar]
  • 19.Loiseau C, Sorci G. 2022. Can microplastics facilitate the emergence of infectious diseases? Sci Total Environ 823:153694. doi: 10.1016/j.scitotenv.2022.153694. [DOI] [PubMed] [Google Scholar]
  • 20.Silva MM, Maldonado GC, Castro RO, de Sá Felizardo J, Cardoso RP, Anjos RMD, de Araújo FV. 2019. Dispersal of potentially pathogenic bacteria by plastic debris in Guanabara Bay, RJ, Brazil. Mar Pollut Bull 141:561–568. doi: 10.1016/j.marpolbul.2019.02.064. [DOI] [PubMed] [Google Scholar]
  • 21.Kirstein IV, Kirmizi S, Wichels A, Garin-Fernandez A, Erler R, Löder M, Gerdts G. 2016. Dangerous hitchhikers? Evidence for potentially pathogenic Vibrio spp. on microplastic particles. Mar Environ Res 120:1–8. doi: 10.1016/j.marenvres.2016.07.004. [DOI] [PubMed] [Google Scholar]
  • 22.Amaral-Zettler LA, Zettler ER, Mincer TJ. 2020. Ecology of the plastisphere. Nat Rev Microbiol 18:139–151. doi: 10.1038/s41579-019-0308-0. [DOI] [PubMed] [Google Scholar]
  • 23.Viršek MK, Lovšin MN, Koren Š, Kržan A, Peterlin M. 2017. Microplastics as a vector for the transport of the bacterial fish pathogen species Aeromonas salmonicida. Mar Pollut Bull 125:301–309. doi: 10.1016/j.marpolbul.2017.08.024. [DOI] [PubMed] [Google Scholar]
  • 24.Wright RJ, Erni-Cassola G, Zadjelovic V, Latva M, Christie-Oleza JA. 2020. Marine plastic debris: a new surface for microbial colonization. Environ Sci Technol 54:11657–11672. doi: 10.1021/acs.est.0c02305. [DOI] [PubMed] [Google Scholar]
  • 25.Vos M. 2020. The evolution of bacterial pathogens in the Anthropocene. Infect Genet Evol 86:104611. doi: 10.1016/j.meegid.2020.104611. [DOI] [PubMed] [Google Scholar]
  • 26.Byrne GA, Russell DA, Chen X, Meijer WG. 2007. Transcriptional regulation of the virR operon of the intracellular pathogen Rhodococcus equi. J Bacteriol 189:5082–5089. doi: 10.1128/JB.00431-07. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Ren J, Prescott JF. 2003. Analysis of virulence plasmid gene expression of intra-macrophage and in vitro grown Rhodococcus equi ATCC 33701. Vet Microbiol 94:167–182. doi: 10.1016/s0378-1135(03)00099-3. [DOI] [PubMed] [Google Scholar]
  • 28.Russell DA, Byrne GA, O’Connell EP, Boland CA, Meijer WG. 2004. The LysR-type transcriptional regulator VirR is required for expression of the virulence gene vapA of Rhodococcus equi ATCC 33701. J Bacteriol 186:5576–5584. doi: 10.1128/JB.186.17.5576-5584.2004. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 29.Jug U, Naumoska K, Metličar V, Schink A, Makuc D, Vovk I, Plavec J, Lucas K. 2020. Interference of oleamide with analytical and bioassay results. Sci Rep 10:2163. doi: 10.1038/s41598-020-59093-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Reid T, Kashangura C, Chidewe C, Benhura MA, Stray-Pedersen B, Mduluza T. 2019. Characterization of anti-Salmonella typhi compounds from medicinal mushroom extracts from Zimbabwe. Int J Med Mushrooms 21:713–724. doi: 10.1615/IntJMedMushrooms.v21.i7.80. [DOI] [PubMed] [Google Scholar]
  • 31.Hamberger A, Stenhagen G. 2003. Erucamide as a modulator of water balance: new function of a fatty acid amide. Neurochem Res 28:177–185. doi: 10.1023/a:1022364830421. [DOI] [PubMed] [Google Scholar]
  • 32.Gahleitner M, Grein C, Blell R, Wolfschwenger J, Koch T, Ingolic E. 2011. Sterilization of propylene/ethylene random copolymers: annealing effects on crystalline structure and transparency as influenced by polymer structure and nucleation. Express Polym Lett 5:788–798. doi: 10.3144/expresspolymlett.2011.77. [DOI] [Google Scholar]
  • 33.Takai S, Fukunaga N, Kamisawa K, Imai Y, Sasaki Y, Tsubaki S. 1996. Expression of virulence-associated antigens of Rhodococcus equi is regulated by temperature and pH. Microbiol Immunol 40:591–594. doi: 10.1111/j.1348-0421.1996.tb01113.x. [DOI] [PubMed] [Google Scholar]
  • 34.MacArthur I, Parreira VR, Lepp D, Mutharia LM, Vazquez-Boland JA, Prescott JF. 2011. The sensor kinase MprB is required for Rhodococcus equi virulence. Vet Microbiol 147:133–141. doi: 10.1016/j.vetmic.2010.06.018. [DOI] [PubMed] [Google Scholar]
  • 35.Ren J, Prescott JF. 2004. The effect of mutation on Rhodococcus equi virulence plasmid gene expression and mouse virulence. Vet Microbiol 103:219–230. doi: 10.1016/j.vetmic.2004.08.005. [DOI] [PubMed] [Google Scholar]
  • 36.Miranda-CasoLuengo R, Miranda-CasoLuengo AA, O’Connell EP, Fahey RJ, Boland CA, Vázquez-Boland JA, Meijer WG. 2011. The vapA co-expressed virulence plasmid gene vcgB (orf10) of the intracellular actinomycete Rhodococcus equi. Microbiology (Reading) 157:2357–2368. doi: 10.1099/mic.0.049759-0. [DOI] [PubMed] [Google Scholar]
  • 37.Bowley J, Baker-Austin C, Porter A, Hartnell R, Lewis C. 2021. Oceanic hitchhikers - assessing pathogen risks from marine microplastic. Trends Microbiol 29:107–116. doi: 10.1016/j.tim.2020.06.011. [DOI] [PubMed] [Google Scholar]
  • 38.Caudill VE, Halek GW. 1992. Polypropylene surface characteristics after exposure to hydrogen peroxide and heat processing. J Plastic Film Sheeting 8:140–154. doi: 10.1177/875608799200800206. [DOI] [Google Scholar]
  • 39.Alberto Lopes J, Tsochatzis ED, Robouch P, Hoekstra E. 2019. Influence of pre-heating of food contact polypropylene cups on its physical structure and on the migration of additives. Food Packag Shelf Life 20:100305. doi: 10.1016/j.fpsl.2019.100305. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.Al Akhrass F, Al Wohoush I, Chaftari A-M, Reitzel R, Jiang Y, Ghannoum M, Tarrand J, Hachem R, Raad I. 2012. Rhodococcus bacteremia in cancer patients is mostly catheter related and associated with biofilm formation. PLoS One 7:e32945. doi: 10.1371/journal.pone.0032945. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 41.Auta HS, Emenike CU, Jayanthi B, Fauziah SH. 2018. Growth kinetics and biodeterioration of polypropylene microplastics by Bacillus sp. and Rhodococcus sp. isolated from mangrove sediment. Mar Pollut Bull 127:15–21. doi: 10.1016/j.marpolbul.2017.11.036. [DOI] [PubMed] [Google Scholar]
  • 42.Yin W, Zhang B, Shi J, Liu Z. 2022. Microbial adaptation to co-occurring vanadium and microplastics in marine and riverine environments. J Hazard Mater 424:127646. doi: 10.1016/j.jhazmat.2021.127646. [DOI] [PubMed] [Google Scholar]
  • 43.Martínez-Campos S, Pissaridou P, Drakou K, Shammas C, Andreou K, González-Pleiter M, Fernández-Piñas F, Leganes F, Rosal R, Koutinas M, Kapnisis K, Vasquez MI. 2022. Evolution of prokaryotic colonisation of greenhouse plastics discarded into the environment. Ecotoxicol Environ Saf 232:113213. doi: 10.1016/j.ecoenv.2022.113213. [DOI] [PubMed] [Google Scholar]
  • 44.Zolotova N, Kosyreva A, Dzhalilova D, Fokichev N, Makarova O. 2022. Harmful effects of the microplastic pollution on animal health: a literature review. PeerJ 10:e13503. doi: 10.7717/peerj.13503. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.de Souza-Silva TG, Oliveira IA, da Silva GG, Giusti FCV, Novaes RD, Paula H. 2022. Impact of microplastics on the intestinal microbiota: a systematic review of preclinical evidence. Life Sci 294:120366. doi: 10.1016/j.lfs.2022.120366. [DOI] [PubMed] [Google Scholar]
  • 46.Benoit S, Taouji S, Benachour A, Hartke A. 2000. Resistance of Rhodococcus equi to acid pH. Int J Food Microbiol 55:295–298. doi: 10.1016/s0168-1605(00)00172-0. [DOI] [PubMed] [Google Scholar]
  • 47.Bustin SA, Benes V, Garson JA, Hellemans J, Huggett J, Kubista M, Mueller R, Nolan T, Pfaffl MW, Shipley GL, Vandesompele J, Wittwer CT. 2009. The MIQE guidelines: minimum information for publication of quantitative real-time PCR experiments. Clin Chem 55:611–622. doi: 10.1373/clinchem.2008.112797. [DOI] [PubMed] [Google Scholar]
  • 48.Vandesompele J, de Preter K, Pattyn F, Poppe B, van Roy N, de Paepe A, Speleman F. 2002. Accurate normalization of real-time quantitative RT-PCR data by geometric averaging of multiple internal control genes. Genome Biol 3:RESEARCH0034. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 49.Tan C, Prescott JF, Patterson MC, Nicholson VM. 1995. Molecular characterization of a lipid-modified virulence-associated protein of Rhodococcus equi and its potential in protective immunity. Can J Vet Res 59:51–59. [PMC free article] [PubMed] [Google Scholar]

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