Skip to main content
Microbial Biotechnology logoLink to Microbial Biotechnology
. 2019 Apr 23;13(1):274–284. doi: 10.1111/1751-7915.13418

Agar plate‐based screening methods for the identification of polyester hydrolysis by Pseudomonas species

Rebecka Molitor 1, Alexander Bollinger 1, Sonja Kubicki 1, Anita Loeschcke 1, Karl‐Erich Jaeger 1,2, Stephan Thies 1,
PMCID: PMC6922526  PMID: 31016871

Summary

Hydrolases acting on polyesters like cutin, polycaprolactone or polyethylene terephthalate (PET) are of interest for several biotechnological applications like waste treatment, biocatalysis and sustainable polymer modifications. Recent studies suggest that a large variety of such enzymes are still to be identified and explored in a variety of microorganisms, including bacteria of the genus Pseudomonas. For activity‐based screening, methods have been established using agar plates which contain nanoparticles of polycaprolactone or PET prepared by solvent precipitation and evaporation. In this protocol article, we describe a straightforward agar plate‐based method using emulsifiable artificial polyesters as substrates, namely Impranil® DLN and liquid polycaprolactone diol (PLD). Thereby, the currently quite narrow set of screening substrates is expanded. We also suggest optional pre‐screening with short‐chain and middle‐chain‐length triglycerides as substrates to identify enzymes with lipolytic activity to be further tested for polyesterase activity. We applied these assays to experimentally demonstrate polyesterase activity in bacteria from the P. pertucinogena lineage originating from contaminated soils and diverse marine habitats.


Hydrolases acting on polyesters like cutin, polycaprolactone or polyethylene terephthalate (PET) are of interest for several biotechnological applications like waste treatment, biocatalysis, and sustainable polymer modifications. In this protocol article, we describe a straightforward agar plate based method using emulsifiable artificial polyesters as substrates. We applied these assays to experimentally demonstrate polyesterase activity in bacteria from the Pseudomonas pertucinogena lineage originating from contaminated soils and diverse marine habitats.

graphic file with name MBT2-13-274-g003.jpg

Introduction

Recent attention of both the scientific community and the public was drawn to microorganisms with enzymatic capabilities to degrade the plastic polymer polyethylene terephthalate (PET) (Wei et al., 2016; Wierckx et al., 2018) that was assumed to be biologically inert for a long time (Moharir and Kumar, 2019). Probably the most prominent example is the β‐proteobacterium Ideonella sakaiensis isolated from a plastic‐polluted site (Yoshida et al., 2016) which produces an enzyme named IsPETase (Austin et al., 2018; Gong et al., 2018; Joo et al., 2018) that was shown to be responsible for the biodegradation of PET. Crystallographic studies revealed that this enzyme shows a cutinase‐like structure (Joo et al., 2018) which is in line with other studies on enzymatic degradation of PET by enzymes that were initially described as cutinases (Nikolaivits et al., 2018).

Cutinases are lipolytic enzymes and thus primarily active on carboxylic ester bonds (EC 3.1.1) but defined by activity on polyesters like the plant surface material cutin (Nikolaivits et al., 2018) and, as a consequence, were assigned to a distinct enzyme subclass (EC 3.1.1.74). Cutinases are now spotlighted in the development of new strategies to deal with man‐made plastic pollution: Most studies attempting to hydrolyze artificial polyesters are conducted applying such cutinase‐like enzymes (Korpecka et al., 2010; Austin et al., 2018; Nikolaivits et al., 2018). However, lipolytic enzymes clustering within other families (Arpigny and Jaeger, 1999), e.g. family VIII (β‐lactamase like), were likewise associated with polyesterase activity very recently (Biundo et al., 2017; Müller et al., 2017; Hajighasemi et al., 2018). Besides biodegradation of artificial polyesters like PET, cutinases/polyesterases are discussed for different biotechnological applications, e.g. sustainable polymerization and polymer modification processes or biocatalytic transesterification and ester synthesis reactions (Nikolaivits et al., 2018). Most polyesterases known today are secreted into the extracellular medium, potentially facilitating industrial production with either wild‐type or suitable recombinant host strains.

Currently, high‐throughput activity‐based screening assays are a frequently applied method to identify novel biocatalysts within environmental isolates or metagenomic libraries (Popovic et al., 2015; Martin et al., 2016; Peña‐García et al., 2016; Thies et al., 2016). These assays are of key importance for reducing the experimental workload to allow assigning of an activity of interest to an individual clone which can then be further characterized. To this end, agar plate‐based activity assays are typically applied. Here, clear or coloured zones which are formed around the bacterial colonies indicate the production of a catalytically active enzyme. Suchlike approaches to identify organisms or clones with polyesterase activity currently mostly rely on clearance of media containing polycaprolactone (PCL) or PET nanoparticles prepared by solvent precipitation and evaporation techniques (Jarrett et al., 1984; Nishida and Tokiwa, 1993; Wei et al., 2014). Notably, these assays imply safety hazards and the production of organic solvent waste. In this protocol article, we describe water‐emulsifiable polyesters (Fig. S1) as substrates for rapid and straightforward agar plate‐based screening assays as an alternative or at least complementary strategy to identify polyesterase activity in bacterial clones, here exemplified by the identification of such enzymatic activities exhibited by yet unexplored Pseudomonas species. These assays generally allow for high‐throughput identification of relevant clones, e.g. in metagenomic or genomic libraries (Fig. 1).

Figure 1.

Figure 1

Workflow for agar plate‐based screening for polyesterase active clones.

A. Steps of plate preparation and screening: 1. Prepare an emulsion/suspension with the respective substrate (if necessary). 2. Combine substrate emulsion/suspension and molten agar‐containing nutrient medium. 3. Pour the warm medium into suitable Petri dishes and let the agar solidify. Suitable supplements for induction of gene expression or selection may be included as well. 4. Plate bacteria either by transfer of single colonies using autoclaved toothpicks, 96 pin replicators or a robotic colony picker, or spread appropriate cell suspensions with glass beads or a Drigalski spatula. Incubate for at least 16 h at a temperature optimal for the applied organism. 5. Document the appearance of halos and/or fluorescence if applicable.

B. Overview on the described substrates (including the chain lengths of the dominant fatty acid for the triacylglycerides) and the enzymatic activities that can be identified with the respective screening plates.

Step‐by‐step protocols for agar plate preparation and polyesterase activity screening

Polyesterases are lipolytic enzymes and are thus detected by non‐specific esterase assays like an agar plate‐based screening with the substrate tributyrin. The use of this universal substrate with a short‐chain fatty acid triglyceride will also detect activities of esterases, true lipases, phospholipases or even peptidases and acyl transferases. The use of triglycerides with long‐chain fatty acids (FA) like olive oil instead is more selective for lipases because activity towards substrates with fatty acid chains > C10 is a characteristic of these enzymes (Kouker and Jaeger, 1987). However, cutinases have been categorized between esterases and true lipases because they are reported to have higher affinities for short‐chain to middle‐chain FA ester substrates with chain lengths up to C8 or C12 (Nikolaivits et al., 2018); as a result of this substrate specificity, established lipase‐specific screenings with long‐chain plant oils like olive oil (Kouker and Jaeger, 1987) may miss lipolytic enzymes with additional polyesterase activity. The application of coconut oil that contains, in contrast, a large portion of C6‐C14 FA esters (Sankararaman and Sferra, 2018), may bridge the gap between too universal and too lipase‐specific substrates used for screening (tributyrin and olive oil respectively). Here, we suggest using the substrates tributyrin and coconut oil for an optional pre‐screening to identify lipolytic activity because both substrates are inexpensive and easily available. As a second step, we describe the utilization of easy‐to‐emulsify polyesters which can serve as appropriate substrates, i.e. Impranil® DLN, an anionic aliphatic polyester polyurethane, and polycaprolactone diol PCDMn530 as a polycaprolactone derivative of lower molecular weight. Impranil® DLN emulsion was already described as a substrate in agar plates for polyurethanase screening (Howard et al., 2001). PCDMn530 constitutes a viscous liquid which can be emulsified in liquid media in contrast to amorphous or crystalline solids like the commonly applied polycaprolactone.

General remarks

Media preparation

For the plate assays, we used autoclaved (121°C, 20 min) LB medium (Carl Roth, Karlsruhe, Germany), consisting of 10 g l−1 tryptone (peptone from casein), 5 g l−1 yeast extract and 10 g l−1 NaCl solubilized in deionized water supplemented with 15 g l−1 agar–agar (Carl Roth) as the growth medium because it proved suitable for growth of the selected Pseudomonas strains despite their partial marine origin and Escherichia coli that was included as negative control. However, other growth media or agar plates supplemented with antibiotics or expression inductors may also be tested, if required. As examples, polyesterase screening plates supplemented with the here introduced polyesterase substrates polycaprolactone diol and Impranil® DLN based on MME minimal medium (Vogel and Bonner, 1956) as well as artificial seawater medium (Passeri et al., 1992) with regard to the sea‐born strains of the P. pertucinogena lineage (Fig. S2). The agar was melted just before plate preparation or, alternatively, applied immediately after autoclaving. An Ultra Turrax T25 basic (IKA Labortechnik, Staufen, Germany), previously rinsed with 70% (v/v) ethanol, was applied with 16 000 rpm for both the preparation of substrate emulsions in sterile deionized water (if applicable) and their homogeneous emulsification into molten LB agar (cooled to a temperature of about 60–70°C). Emulsification using an ultrasonic emulsifier according to manufacturer's instructions is also possible. Here, it was in particular applied for smaller volumes (≤ 1 ml). The emulsion of the substrates in hot agar is recommended to maintain sterility of the plates.

Bacterial clones

In the presented examples, single colonies of Pseudomonas sp. and E. coli BL21(DE3), respectively, are transferred from a master plate to the indicator plates using sterile toothpicks. In general, it should also be applicable to directly plate (meta‐)genomic libraries prepared in E. coli (Katzke et al., 2017) using commercially available kits for TopoTA‐cloning (Thermo Scientific, Waltham, MA, USA) or CopyControl™ Fosmid Library Production (epicentre, Madison, WI, USA), or mutagenesis libraries of specific genes in expression vectors prepared by standard molecular cloning methods. Agar plate‐based screening assays are typically suitable for that application. As an example, tributyrin plates are an established tool for metagenomic library screenings (Peña‐García et al., 2016). Plating of dilutions of environmental samples to isolate species of interest might also be tested. However, it has to be kept in mind that the applied growth medium and incubation conditions will in general select for a subpopulation of the plated microbial strains. Hence, a good part of the natural diversity may be lost.

In the here presented example, plates were incubated at the optimal growth temperature of the used bacterial strains to allow colony formation and afterwards incubated at 4°C. At low temperatures, halo formation proceeds, whereas bacterial growth is slowed down. Thereby, the perception of activity is often facilitated without the danger of overgrowing (see below, section ‘example’). Hence, prolonged incubation of screening plates at a lower temperature is a common strategy to detect poor activities in activity‐based metagenomic library screenings (Popovic et al., 2015, 2017; Thies et al., 2016). Incubation temperature, incubation time to establish growth and the necessity for prolonged incubation at 4°C depend of course on the investigated organisms and enzymes.

Universal screening for lipolytic enzymes

Tributyrin assay

  • i

    Prepare a 50% (v/v) tributyrin (Applichem, Darmstadt, Germany) emulsion in sterile distilled water and add 50 g l−1 gum arabic (Carl Roth) (Jaeger and Kovacic, 2014). Gum arabic powder is used as an emulsifying agent for the triglyceride. Homogenize the mixture for at least 1 min to yield a stable emulsion, e.g. using an Ultra Turrax (see general remarks).

Note: Add the gum arabic powder to the respective volume of water. Filling water into a tube or a bottle with a layer of the powder at the bottom should be avoided because it will result in a hard‐to‐dissolve clot of gum.

  • ii

    Add 30 ml of tributyrin emulsion per 1 l of molten LB agar (see general remarks) and mix thoroughly, e.g. using an Ultra Turrax (see general remarks).

  • iii

    Pour 25 ml medium portions into appropriate Petri dishes and allow the agar to solidify for at least 15 min.

  • iv

    Plate bacterial clones (see general remarks) and incubate at optimal growth temperature for the specific organism for at least 16 h.

  • v

    Positive clones are identified by a clearing halo after overnight growth or after prolonged (2–7 days) incubation at 4°C for clones expressing low amounts or less active enzymes. Photodocument agar plates (e.g. with a digital camera) and further proceed with selected clones, which were identified as lipolytically active, as appropriate.

Coconut oil assay

  • i

    Melt coconut oil (Biozentrale Naturprodukte, Wittibreut – Ulbering, Germany) by incubation at 30–37°C. Pre‐heat sterile distilled water to 60°C. Heating the water in advance should avoid a drop of temperature below 30°C during the preparation of the emulsion in the next step and therefore prevent a partial hardening of the coconut oil which will hamper successful emulsification.

  • ii

    Prepare a 50% (v/v) coconut oil emulsion in the pre‐heated water containing 50 g l−1 gum arabic (Carl Roth) and 0.35 g l−1 rhodamine B (Sigma‐Aldrich/Merck, Darmstadt, Germany). Homogenize the mixture for at least 1 min to yield a stable emulsion.

Note: Add the gum arabic powder to the respective volume of water. Filling water into a tube or a bottle with a layer of the powder at the bottom should be avoided because it will result in a hard‐to‐dissolve clot of gum.

  • iii

    Add 20 ml of coconut oil emulsion per 1 l of molten LB agar (see general remarks) and mix thoroughly, e.g. using an Ultra Turrax (see general remarks).

  • iv

    Pour 25 ml medium portions into appropriate Petri dishes and allow the agar to solidify for at least 15 min.

  • v

    Plate bacterial clones (see general remarks) and incubate at optimal growth temperature for the specific organism for at least 16 h.

  • vi

    Positive clones are identified by a fluorescent halo after overnight growth or after prolonged (2–7 days) incubation at 4°C for clones expressing low amounts or less active enzymes. Because of the low solubility of middle‐ and long‐chain fatty acids in aqueous media, clearing halos are barely formed. Hence, esterase/lipase activity is detected by fluorescent complexes that are formed between the cationic rhodamine B and free fatty acids released from the substrate lead to yellow fluorescing colonies and/or halos around active colonies. These can be visualized by irradiation of the plate with UV light, e.g. at 254 nm, for example on a UV table for visualization of ethidium bromide‐labelled DNA after gel electrophoresis. Photodocument agar plates (e.g. with a digital camera) and further proceed with selected clones, which were identified as lipolytically active, as appropriate.

Note: If the propagation of the colonies in further experiments is planned, apply UV radiation only for a short period of time (a few seconds) to prevent damaging effects of the UV light. Alternatively, blue light can be used for excitation, e.g. by NGFG15‐FastGene Blue/Green LED Gel TransIlluminator XL (460–530 nm). However, background fluorescence of rhodamine B (excitation maximum 580 nm) increases (Fig. S3).

Note: Agar plates containing oils and rhodamine B constitute a frequently applied robust assay to detect lipase activities in different bacteria (Kouker and Jaeger, 1987; Jaeger and Kovacic, 2014). However, the production of fluorescent pigments may interfere with the rhodamine B fluorescence. The fluorescent siderophore pyoverdine leads to a bright fluorescence of many Pseudomonas strains under UV light exposure. Production of fluorescent siderophores should not be an issue for libraries within E. coli or the strains of the P. pertucinogena lineage investigated here because of the absence of respective gene clusters (Bollinger et al., 2018). However, if pyoverdine producers are the strains of interest, supplementing additional iron to the medium decreases the siderophore production and therefore the autofluorescence (Fig. S4). The necessary amount is probably dependent on the physiology of the investigated strain and the applied growth medium. Concentrations described in protocols for appropriate mineral media for the respective strain may offer a suitable starting point.

Polyesterase screenings

Impranil® DLN assay

  1. Add 4 ml of Impranil® DLN‐SD emulsion (COVESTRO, Leverkusen, Germany) per 1 l of sterile molten LB agar (see general remarks) and mix thoroughly, e.g. using an Ultra Turrax (see general remarks).

  2. Pour 25 ml medium portions into appropriate Petri dishes and allow the agar to solidify for at least 15 min.

  3. Plate bacterial clones (see general remarks) and incubate at optimal growth temperature for the specific organism for at least 16 h.

  4. Positive clones are identified by a clearing halo after overnight growth or after prolonged (2–7 days) incubation at 4°C for clones expressing low amounts or less active enzymes. Photodocument agar plates (e.g. with a digital camera) and further proceed with selected clones, which were identified as active, as appropriate.

Note: Impranil® DLN‐SD emulsion contains isothiazolones as biocidal supplements to prevent spoilage. In the concentrations used here, we observed no impaired growth of the investigated bacteria.

Note: The anionic Impranil® DLN‐SD may become difficult to emulsify into the agar in our experience when a salt‐rich growth medium is applied.

Note: Impranil® DLN is also described as a useful substrate to uncover polyurethanase activities. Although this activity, like polyester hydrolysis, is not widespread, the verification of hits from an Impranil® DLN‐based screening by determination of sequence homology or additional esterase activity assays is suggested (not described in this article).

Polycaprolactone diol (PCDMn530) assay

  • i

    Prepare a 50% (v/v) PCD (average Mn 530 Da) emulsion: Mix the PCDMn530 (Sigma‐Aldrich/Merck) and 50 g l−1 gum arabic with sterile distilled water. Homogenize the mixture for at least 1 min to yield a stable emulsion, e.g. using an Ultra Turrax (see general remarks).

Note: Add the gum arabic powder to the respective volume of water. Filling water into a tube or a bottle with a layer of the powder at the bottom should be avoided because it will result in a hard‐to‐dissolve clot of gum.

  • ii

    Add 30 ml of PCDMn530 emulsion per 1 l of LB agar and mix thoroughly, e.g. using an Ultra Turrax (see general remarks).

  • iii

    Pour 25 ml medium portions into appropriate Petri dishes and allow the agar to solidify for at least 15 min.

  • iv

    Plate bacterial clones (see general remarks) and incubate at optimal growth temperature for the specific organism for at least 16 h.

  • v

    Positive clones are identified by a distinct halo after overnight growth or after prolonged (2–7 days) incubation at 4°C for clones expressing low amounts or less active enzymes. Notably, the formation of clearing halos by enzymatic activity on PCD agar plates is often accompanied by a grainy accumulation of apparent hydrolysis or transesterification products at the edges of the halo, which is not observed on plates supplemented with tributyrin or Impranil® DLN. However, this even enhances the perceptibility of the halo (Fig. S4). Photodocument agar plates (e.g. with a digital camera) and further proceed with selected clones, which were identified as active on polyesters, as appropriate.

Assay with polycaprolactone (PCL) nanoparticle plates (common polyesterase assay, protocol derived from Jarrett et al. (1984))

  • i

    Prepare a 5 g l−1 PCL solution by completely solving PCL (average Mn ˜10 000 by GPC, density 1.146 g ml−1, Sigma‐Aldrich/Merck) in pre‐heated acetone at 50°C under continuous stirring. Pre‐heat an appropriate volume of sterile water likewise to 50°C for the next step.

  • ii

    Prepare a PCL particle suspension by slowly pouring the PCL solution drop by drop under continuous stirring into the water until a final acetone percentage of ca. 10–15% is reached.

Note: A turbid dispersion should be formed. Pour carefully, because too fast supplementation of PCL solution easily leads to the formation of tiny globular plastic particles instead of a homogenous suspension.

  • iii

    Add 100 ml of the warm PCL suspension per 1 l of LB agar (see general remarks) and mix thoroughly, e.g. using an Ultra Turrax (see general remarks).

  • iv

    Pour 25 ml medium into appropriate Petri dishes and allow the agar to solidify for at least 15 min.

  • v

    Plate bacterial clones (see general remarks) and incubate at optimal growth temperature for the specific organism for at least 16 h.

  • vi

    Positive clones are identified by a clearing halo on slightly turbid plates after overnight growth or after prolonged (2–7 days) incubation at 4°C for clones expressing low amounts or less active enzymes. Photodocument agar plates (e.g. with a digital camera) and further proceed with selected clones, which were identified as active on polyesters, as appropriate.

Example: Identification of polyesterase activity among members of the P. pertucinogena group

The recently established Pseudomonas pertucinogena lineage (Peix et al., 2018) consists of several species barely explored until today. The group appears especially interesting for its distinct characteristics with respect to metabolism, genome size and, not least, habitats with very specific conditions including cold, high‐salt and chemically contaminated environments (Bollinger et al., 2018). Remarkably for the predominantly terrestrial genus Pseudomonas, most of the species within this lineage were isolated from marine or saline habitats. Unlike other Pseudomonas species, which are well known for their versatile metabolism, bacteria of the P. pertucinogena lineage seem to have a more niche‐adapted metabolism in common (Bollinger et al., 2018). This is indicated by a comparably small genome and a limited spectrum of utilizable carbon sources. However, the current knowledge about the specific ecological and physiological properties of these species is very limited. An in silico search for cutinase homologous proteins uncovered a lipase of Pseudomonas pelagia (PpelaLip) which was recombinantly expressed in E. coli and proven to hydrolyze different artificial aromatic polyesters, among them poly(oxyethylene terephthalate) (Haernvall et al., 2017a; Haernvall et al., 2018). The strain itself exhibited likewise activity on the polyesters (Haernvall et al., 2017a). The occurrence of genes encoding closely related proteins to PpelaLip appeared to be a common feature of this lineage of Pseudomonas sp. (Bollinger et al., 2018). Therefore, we investigated one terrestrial and four species from different marine habitats differing in temperature, type of contamination and water depth for polyester hydrolyzing properties (Table 1). All strains were purchased from DSMZ (Deutsche Sammlung von Mikroorganismen und Zellkulturen, Braunschweig) and included P. pelagia CL‐AP6T as described producer of PpelaLip as a positive control. We further included P. bauzanensis BZ93T isolated from contaminated soil and the marine species P. litoralis 2SM5T , P. aestusnigri VGXO14T and P. oceani KX 20T. P. putida KT2440 (Belda et al., 2016) was also included as a well‐established and frequently applied member of the fluorescent Pseudomonads (Loeschcke and Thies, 2015) with a versatile metabolism, but without previously described polyesterase activity. In addition, we comprised E. coli BL21(DE3) (Studier and Moffatt, 1986) as a negative control because E. coli is applied as a standard host for metagenomic library screenings and recombinant esterase production, respectively, with negligible background activity.

Table 1.

Pseudomonas strains analysed for polyesterase activity

Species DSMZ No. Habitata Origina Referencesb
P. aestusnigri VGXO14T 103 065 Crude oil‐contaminated intertidal sand samples

Spain

42°46′ 29.27″ N 9°7′27.08″ W

Sánchez et al. (2014); Gomila et al. (2017)
P. bauzanensis BZ93T 22 558 Soil from an industrial site Bozen, South Tyrol, Italy Zhang et al. (2011)
P. litoralis 2SM5T 26 168 Seawater of the Mediterranean coast

Spain

40° 27′ 24″ N 0° 31′ 36″ E

Pascual et al. (2012)
P. oceani KX 20T 100 277 Deep‐sea (1350 m) Okinawa Trough, Pacific Ocean Wang and Sun (2016); García‐Valdés et al. (2018)
P. pelagia CL‐AP6T 25 163 Antarctic green algae co‐culture Antarctic Ocean Hwang et al. (2009); Koh et al. (2013)
P. putida KT2440c 6125 Plasmid free derivative of P. putida mt‐2, isolated from soil in Japan Nakazawa (2002); Belda et al. (2016)

a. Environment from which the species was isolated (habitat) and geographical origin of the sample (origin) as stated in the type strain description.

b. References for original descriptions and, if applicable, genome announcements.

c. P. putida was included as an established representative of the fluorescent Pseudomonads.

All strains were streaked on LB agar plates and incubated at 30°C for 24 h. Distinct colonies of each strain were transferred to the indicator plates using sterile toothpicks and grown for 24 h at 30°C. Plates were photodocumented (Fig. 2), incubated further 24 h at 30°C and afterwards stored at 4°C for 4 days before the final photodocumentation (Fig. S5). All strains showed activity on the indicator plates, except E. coli BL21(DE3) and P. putida KT2440 which appeared as polyesterase‐negative. The production of the fluorescent siderophore pyoverdine leads to bright fluorescence of the latter strain under UV light exposure. As halos were formed not only on Impranil® DLN, which may also result from other enzymatic activities (Fig. 1), but also on the two other polyester substrates, the tested strains of the P. pertucinogena lineage can be assumed to produce lipolytic and/or polyester hydrolyzing enzymes. Hydrolysis of the applied substrates by polyesterases was furthermore confirmed by clearing halos exhibited by E. coli with pEBP18_Cut (Troeschel et al., 2012). This strain is able to express the cutinase gene from Fusarium solani f.sp. pisi which constitutes a well‐characterized enzyme known for its polyesterase activity (Wei et al., 2016; Wierckx et al., 2018), from a shuttle vector applicable to metagenomic library screenings (Thies et al., 2016) (Fig. S6).

Figure 2.

Figure 2

Polyesterase activities exhibited by Pseudomonas species. The colonies were grown for 24 h at 30°C on LB agar plates supplemented with different substrates: Tributyrin (esterase activity); coconut oil + rhodamine B (mid‐chain‐length hydrolyzing esterase); Impranil® DLN (synthetic polyester polyurethane, polyesterase activity); PCDM n530, polycaprolactone diol (synthetic polyester, polyesterase activity); and polycaprolactone nanoparticles (current standard for polyesterase screens, polyesterase activity). P. putida as an example for a fluorescent Pseudomonad and E. coli as a negative control are indicated by grey letters. The white halo around P. putida relies on the fluorescence of the siderophore pyoverdine and does not indicate clearance of the substrate. All plates were photodocumented under white light, except coconut oil + rhodamine B‐supplemented plates which were exposed to UV light (λ = 254 nm). Shown are exemplary colonies of a set of at least three colonies for each combination on independent plates. Halo formation of the depicted colony is representative for all replicates.

In conclusion, polyesterase activity that was suggested by the previous identification of respective genes by sequence homology searches (Bollinger et al., 2018) could be experimentally confirmed for these strains. The comparison of the halo sizes as an indicator for the enzymatic activity revealed remarkable differences: (i) Closely related species exhibited very different strengths of activity. P. litoralis and P. oceani showed large hydrolysis halos already after one night of incubation, whereas the activity of P. pelagia became clearly visible only after growth for 48 h and several further days at 4°C (Fig. S5). (ii) The activity on polyester substrates appeared more prominent than on tributyrin and coconut oil while a polyesterase itself should be able to hydrolyze the triglyceride substrates likewise very well (A. Bollinger, unpublished). Both observations may be caused by variances in the specific activities of the different enzymes or attributable to differentially regulated polyesterase production and secretion by the different bacteria in reaction to the substrates. Further studies are necessary to assess whether the enzyme biochemistry or the bacterial physiology is the dominant factor behind the apparently massive differences in polyesterase activity.

Discussion

Lipolytic enzymes with activities on polyesters are already highly interesting for a variety of industrial applications and may become even more important in the future for plastic waste and microplastic removal (Wei and Zimmermann, 2017; Urbanek et al., 2018). Currently, many scientific studies on the detection of bacterial polyesterase enzyme production rely on a first screening step utilizing the clearance of media from polymer nanoparticles, often polycaprolactone as a simple aliphatic polyester or PET as prominent industrially applied polyester (Jarrett et al., 1984; Nishida and Tokiwa, 1993; Wei et al., 2014). These procedures are associated with certain disadvantages as they imply solving of the solid polymer in hazardous organic solvents like acetone, dichloromethane or 1,1,1,3,3,3‐hexafluoro‐2‐propanol and subsequent precipitation by careful addition to heated water or immediately to molten agar. In both cases, a temperature just below the boiling point of the applied solvents is necessary. Hence, the boiling temperature may easily be exceeded and the risk of a sudden evaporation of hot solvents is immanent. Connected to this is the reassembly of larger globular polymer particles because of the sudden exposition of the insoluble polymer to water. Finally, the solvent has to be evaporated by heat or ultrasonication to avoid detrimental effects to the cells which are to be investigated. In addition, this step is necessary for the exchange of solvent shells around the plastic nanoparticles against water which makes them accessible for hydrolases. In our experience, the named procedures not only bear safety hazards but also require considerable handling practice to obtain reproducible results. The application of emulsifiable polyesters like Impranil® DLN or lower molecular weight polycaprolactone derivatives instead appeared in our hands to be a more rapid and straightforward procedure. While PCD–agar was to our knowledge not described to prepare screening plates before, Impranil® DLN‐supplemented agar has previously been described and applied to identify and characterize polyurethanases, e.g. in biofilms that degrade coatings in military aircrafts (Howard et al., 2001; Biffinger et al., 2015, 2018; Hung et al., 2016). In our experiences, this substrate is also perfectly suited to identify polyesterases. This observation is in line with studies using this substrate to assess cutinase activities in turbidometric experiments (Schmidt et al., 2017). It is further supported by the fact that F. solani f.sp. pisi cutinase producing recombinant E. coli that are able to hydrolyze the polyester polyurethane (Fig. S6). However, Impranil® DLN screening may yield false positive hits constituting protease‐ or amidase‐like enzymes rather than esterases. Hence, hits from these screenings should be verified using esterase activity assays based on the hydrolysis of, e.g., triglycerides or p‐nitrophenol esters (Jaeger and Kovacic, 2014). Generally, application of inexpensive and easily available triglyceride substrates like tributyrin and coconut oil for screening may be highly useful to pre‐select esterolytic organisms or clones in a library in advance to specific polyesterase assays (Fig. S7). PCDMn530 is near twice as expensive as the applied polycaprolactone (source: Sigma‐Aldrich); however, the small amounts necessary to prepare one litre medium for screening approaches render this substrate also affordable according to our experience. Impranil® DLN‐SD emulsion is conventionally purchased as a bulk product for industrial coating applications. Hence, conditions to obtain small scaled product samples for the laboratory application have to be enquired on an individual basis. The applicability of a two‐step strategy combining pre‐selection and subsequent polyesterase activity assay was shown by the identification of novel types of polyesterases within a set of hydrolases from metagenomic libraries that were identified by their lipolytic activity in previous studies (Hajighasemi et al., 2018).

The halo formation on the opaque white or yellowish Impranil® DLN agar (in dependence of the used medium) and the dark framed halos on PCD plates appeared to facilitate visual recognition of poor activities in comparison with semi‐transparent nanoparticle plates. This straightforward readout might also be useful in applications using cutinases as reporter proteins in high‐throughput approaches. Examples include transcriptional fusions confirming the successful transcription of target operons to identify promising expression strains (Domröse et al., 2017), or as a model protein for studies on protein secretion, e.g. using signal peptide libraries (Knapp et al., 2017). In addition, both substrates generally expand the set of polymers applicable to screenings. They may be used in combination with nanoparticle‐based screenings to increase hit rates and to detect a broad variety of enzymatic activities in mixed samples as it can be assumed that different enzymes are differentially active on diverse unnatural substrates. Certainly, the aim of the screening was an important determinant for the selection of the substrate. Both assays described here apply aliphatic polyesters (Fig. S1), whereas many of the widely used polyesters like PET contain aromatic building blocks. However, previous studies showed that a large portion of enzymes is active on both types of substrates (Wei et al., 2014; Danso et al., 2018). This suggests that aliphatic polyesters might still serve as a useful substrate to pre‐select candidates for further investigation even if aromatic polyester hydrolysis is the activity of interest. However, evolutive development of respective specificities towards a separation of both activities is discussed (Austin et al., 2018); the presented assays are probably not suitable to indicate activity of such enzymes that are selective for aromatic polyesters.

In conclusion, the presented assays are suitable for high‐throughput screening applications and may not completely replace but functionally complement the existing nanoparticle‐based activity assays to exploit novel organisms and biocatalysts with polyesterase activity. For optimal results, these methods need to be interlinked with appropriate in silico strategies to exploit the available DNA sequence information. By using a hidden Markov Model‐based search strategy to screen sequence data sets, Danso and co‐authors showed that a surprisingly large variety of potential polyesterases is still to be discovered, in particular in bacteria which are currently not considered as a prime source for cutinases (Danso et al., 2018). Pseudomonas species may constitute an example; in the context of polymer hydrolysis, they appeared as a source for enzymes hydrolyzing polyurethane (Wilkes and Aristilde, 2017) for a long time, but some very recent reports by the Guebitz group indicated also polyesterase activity in Pseudomonads (Haernvall et al., 2017a,2017b; Wallace et al., 2017). The here reported confirmation of polyesterase activity of bacteria from the P. pertucinogena lineage, that was already suggested by sequence homology searches (Bollinger et al., 2018), underlines the biotechnological potential of this group of bacteria. The predominantly marine Pseudomonas lineage, which includes psychrophilic, halophilic, as well as hydrocarbonoclastic, and heavy metal‐tolerant species, may harbour many more intriguing biocatalysts with extraordinary properties.

Agar plate‐based assays are a frequently applied tool for the activity‐based screenings of metagenomic libraries, in particular for lipolytic enzymes (Popovic et al., 2015, 2017; Peña‐García et al., 2016; Thies et al., 2016), also with special emphasis on pollutant degrading enzymes (Ufarté et al., 2015). The functionality of this assay with the typical host for metagenomic libraries, E. coli, expressing a cutinase encoding gene was indicated here (Fig. S6). In this light, the here presented assays may also prove useful to identify polyester‐hydrolytic biocatalysts within metagenomic libraries containing DNA, e.g. from microplastic‐polluted habitats. In the future, this may contribute to the exploitation of novel biocatalysts for biotechnological and environmental applications and shed light on natural plastic degradation processes in microbial communities.

Conflict of interest

None declared.

Supporting information

Fig. S1. Molecular structures of the discussed substrates.

Fig. S2. Growth and polyesterase activities exhibited by Pseudomonas species on agar plates based on artificial sea medium and MME minimal medium.

Fig. S3. Coconut oil/rhodamine B agar plates exposed to different light conditions.

Fig. S4. Effect of the additional supplementation of Fe2+ on the autofluorescence of P. putida on coconut oil +rhodamine B agar plates.

Fig. S5. Polyesterase activities exhibited by Pseudomonas species after prolonged incubation at 4°C.

Fig. S6. Polyesterase exhibited by E. coli BL21(DE3) expressing the F. solani f.sp pisi cutinase gene.

Fig. S7. Schematic workflow for agar plate‐based screening for polyesterase active clones within a (meta‐)genomic library.

Acknowledgements

The authors received funding from the European Union's Horizon 2020 research and innovation programme (Blue Growth: Unlocking the potential of Seas and Oceans) through the Project ‘INMARE’ under grant agreement No. 634486. ST, SK and AL are financially supported by the ministry of Culture and Science of the German State of North Rhine‐Westphalia within in the framework of the NRW Strategieprojekt BioSC (No. 313/323‐400‐00213).

Microbial Biotechnology (2020) 13(1), 274–284

Funding Information

The authors received funding from the European Union's Horizon 2020 research and innovation programme (Blue Growth: Unlocking the potential of Seas and Oceans) through the Project ‘INMARE’ under grant agreement No. 634486. ST, SK and AL are financially supported by the ministry of Culture and Science of the German State of North Rhine‐Westphalia within in the framework of the NRW Strategieprojekt BioSC (No. 313/323‐400‐00213).

References

  1. Arpigny, J.L. , and Jaeger, K.‐E. (1999) Bacterial lipolytic enzymes: classification and properties. Biochem J 343(Pt 1): 177–183. [PMC free article] [PubMed] [Google Scholar]
  2. Austin, H.P. , Allen, M.D. , Donohoe, B.S. , Rorrer, N.A. , Kearns, F.L. , Silveira, R.L. , et al (2018) Characterization and engineering of a plastic‐degrading aromatic polyesterase. Proc Natl Acad Sci USA 115: E4350–E4357. [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Belda, E. , van Heck, R.G.A. , José Lopez‐Sanchez, M. , Cruveiller, S. , Barbe, V. , Fraser, C. , et al (2016) The revisited genome of Pseudomonas putida KT2440 enlightens its value as a robust metabolic chassis. Environ Microbiol 18: 3403–3424. [DOI] [PubMed] [Google Scholar]
  4. Biffinger, J.C. , Barlow, D.E. , Cockrell, A.L. , Cusick, K.D. , Hervey, W.J. , Fitzgerald, L.A. , et al (2015) The applicability of Impranil®DLN for gauging the biodegradation of polyurethanes. Polym Degrad Stab 120: 178–185. [Google Scholar]
  5. Biffinger, J.C. , Crookes‐Goodson, W.J. and Barlow, D.E. (2018) Assignment of direct vs. indirect mechanisms used by fungi for polyurethane coating degradation. SERDP Final Report for SEED WP‐2745. [WWW document] URL: https://www.serdp-estcp.org/content/download/47939/456696/file/WP-2745%20Final%20Report.pdf.
  6. Biundo, A. , Ribitsch, D. , Steinkellner, G. , Gruber, K. , and Guebitz, G.M. (2017) Polyester hydrolysis is enhanced by a truncated esterase: less is more. Biotechnol J 12: 8. [DOI] [PubMed] [Google Scholar]
  7. Bollinger, A. , Thies, S. , Katzke, N. and Jaeger, K.‐E. (2018) The biotechnological potential of marine bacteria in the novel lineage of Pseudomonas pertucinogena . Microb Biotechnol. 10.1111/1751-7915.13288. [Epub ahead of print]. [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Danso, D. , Schmeisser, C. , Chow, J. , Zimmermann, W. , Wei, R. , Leggewie, C. , et al (2018) New insights into the function and global distribution of polyethylene terephthalate (PET)‐degrading bacteria and enzymes in marine and terrestrial metagenomes. Appl Environ Microbiol 84: AEM.02773‐17. [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Domröse, A. , Weihmann, R. , Thies, S. , Jaeger, K.‐E. , Drepper, T. , and Loeschcke, A. (2017) Rapid generation of recombinant Pseudomonas putida secondary metabolite producers using yTREX. Synth Syst Biotechnol 2: 310–319. [DOI] [PMC free article] [PubMed] [Google Scholar]
  10. García‐Valdés, E. , Gomila, M. , Mulet, M. , and Lalucat, J. (2018) Draft genome sequence of Pseudomonas oceani dsm 100277T, a Deep‐sea bacterium. Genome Announc 6: e00254‐18. [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Gomila, M. , Mulet, M. , Lalucat, J. , and García‐Valdés, E. (2017) Draft genome sequence of the marine bacterium Pseudomonas aestusnigri VGXO14T . Genome Announc 5: e00765‐17. [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. Gong, J. , Kong, T. , Li, Y. , Li, Q. , Li, Z. , Zhang, J. , et al (2018) Biodegradation of microplastic derived from poly(ethylene terephthalate) with bacterial whole‐cell biocatalysts. Polymers (Basel) 10: 1326. [DOI] [PMC free article] [PubMed] [Google Scholar]
  13. Haernvall, K. , Zitzenbacher, S. , Wallig, K. , Yamamoto, M. , Schick, M.B. , Ribitsch, D. , and Guebitz, G.M. (2017a) Hydrolysis of ionic phthalic acid based polyesters by wastewater microorganisms and their enzymes. Environ Sci Technol 51: 4596–4605. [DOI] [PubMed] [Google Scholar]
  14. Haernvall, K. , Zitzenbacher, S. , Yamamoto, M. , Schick, M.B. , Ribitsch, D. , and Guebitz, G.M. (2017b) A new arylesterase from Pseudomonas pseudoalcaligenes can hydrolyze ionic phthalic polyesters. J Biotechnol 257: 70–77. [DOI] [PubMed] [Google Scholar]
  15. Haernvall, K. , Zitzenbacher, S. , Biundo, A. , Yamamoto, M. , Schick, M.B. , Ribitsch, D. , and Guebitz, G.M. (2018) Enzymes as enhancers for the biodegradation of synthetic polymers in wastewater. ChemBioChem 19: 317–325. [DOI] [PubMed] [Google Scholar]
  16. Hajighasemi, M. , Tchigvintsev, A. , Nocek, B. , Flick, R. , Popovic, A. , Hai, T. , et al (2018) Screening and characterization of novel polyesterases from environmental metagenomes with high hydrolytic activity against synthetic polyesters. Environ Sci Technol 52: 12388–12401. [DOI] [PubMed] [Google Scholar]
  17. Howard, G.T. , Vicknair, J. , and MacKie, R.I. (2001) Sensitive plate assay for screening and detection of bacterial polyurethanase activity. Lett Appl Microbiol 32: 211–214. [DOI] [PubMed] [Google Scholar]
  18. Hung, C.‐S. , Zingarelli, S. , Nadeau, L.J. , Biffinger, J.C. , Drake, C.A. , Crouch, A.L. , et al (2016) Carbon catabolite repression and impranil polyurethane degradation in Pseudomonas protegens strain Pf‐5. Appl Environ Microbiol 82: 6080–6090. [DOI] [PMC free article] [PubMed] [Google Scholar]
  19. Hwang, C.Y. , Zhang, G.I. , Kang, S.‐H. , Kim, H.J. , and Cho, B.C. (2009) Pseudomonas pelagia sp. nov., isolated from a culture of the Antarctic green alga Pyramimonas gelidicola . Int J Syst Evol Microbiol 59: 3019–3024. [DOI] [PubMed] [Google Scholar]
  20. Jaeger, K.‐E. , and Kovacic, F. (2014) Determination of lipolytic enzyme activities. Methods Mol Biol 1149: 111–134. [DOI] [PubMed] [Google Scholar]
  21. Jarrett, P. , Benedict, C.V. , Bell, J.P. , Cameron, J.A. , and Huang, S.J. (1984) Mechanism of the Biodegradation of polycaprolactone In Polymers as Biomaterials. Boston, MA: Springer US, pp. 181–192. [Google Scholar]
  22. Joo, S. , Cho, I.J. , Seo, H. , Son, H.F. , Sagong, H.‐Y. , Shin, T.J. , et al (2018) Structural insight into molecular mechanism of poly(ethylene terephthalate) degradation. Nat Commun 9: 382. [DOI] [PMC free article] [PubMed] [Google Scholar]
  23. Katzke, N. , Knapp, A. , Loeschcke, A. , Drepper, T. , and Jaeger, K.‐E. (2017) Novel tools for the functional expression of metagenomic DNA In Metagenomics‐Methods and Protocols. Streit W.R., and Daniel R. (eds). New York: Springer, New York, pp. 159–196. [DOI] [PubMed] [Google Scholar]
  24. Knapp, A. , Ripphahn, M. , Volkenborn, K. , Skoczinski, P. , and Jaeger, K.‐E. (2017) Activity‐independent screening of secreted proteins using split GFP. J Biotechnol 258: 110–116. [DOI] [PubMed] [Google Scholar]
  25. Koh, H.Y. , Jung, W. , Do, H. , Lee, S.G. , Lee, J.H. , and Kim, H.J. (2013) Draft genome sequence of Pseudomonas pelagia CL‐AP6, a psychrotolerant bacterium isolated from culture of Antarctic green alga Pyramimonas gelidicola . Genome Announc 1: e00699‐13. [DOI] [PMC free article] [PubMed] [Google Scholar]
  26. Korpecka, J. , Heumann, S. , Billig, S. , Zimmermann, W. , Zinn, M. , Ihssen, J. , et al (2010) Hydrolysis of cutin by PET‐hydrolases. Macromol Symp 296: 342–346. [Google Scholar]
  27. Kouker, G. , and Jaeger, K.‐E. (1987) Specific and sensitive plate assay for bacterial lipases. Appl Env Microbiol 53: 211–213. [DOI] [PMC free article] [PubMed] [Google Scholar]
  28. Loeschcke, A. , and Thies, S. (2015) Pseudomonas putida‐a versatile host for the production of natural products. Appl Microbiol Biotechnol 99: 6197–6214. [DOI] [PMC free article] [PubMed] [Google Scholar]
  29. Martin, M. , Vandermies, M. , Joyeux, C. , Martin, R. , Barbeyron, T. , Michel, G. , and Vandenbol, M. (2016) Discovering novel enzymes by functional screening of plurigenomic libraries from alga‐associated Flavobacteriia and Gammaproteobacteria. Microbiol Res 186–187: 52–61. [DOI] [PubMed] [Google Scholar]
  30. Moharir, R.V. , and Kumar, S. (2019) Challenges associated with plastic waste disposal and allied microbial routes for its effective degradation: a comprehensive review. J Clean Prod 208: 65–76. [Google Scholar]
  31. Müller, C.A. , Perz, V. , Provasnek, C. , Quartinello, F. , Guebitz, G.M. , and Berg, G. (2017) Discovery of polyesterases from moss‐associated microorganisms. Appl Environ Microbiol 83: e02641‐16. [DOI] [PMC free article] [PubMed] [Google Scholar]
  32. Nakazawa, T. (2002) Travels of a Pseudomonas, from Japan around the world. Environ Microbiol 4: 782–786. [DOI] [PubMed] [Google Scholar]
  33. Nikolaivits, E. , Kanelli, M. , Dimarogona, M. , Topakas, E. , Nikolaivits, E. , Kanelli, M. , et al (2018) A middle‐aged enzyme still in its prime: recent advances in the field of cutinases. Catalysts 8: 612. [Google Scholar]
  34. Nishida, H. , and Tokiwa, Y. (1993) Distribution of poly(β‐hydroxybutyrate) and poly(ε‐caprolactone) aerobic degrading microorganisms in different environments. J Environ Polym Degrad 1: 227–233. [Google Scholar]
  35. Pascual, J. , Lucena, T. , Ruvira, M.A. , Giordano, A. , Gambacorta, A. , Garay, E. , et al (2012) Pseudomonas litoralis sp. nov., isolated from Mediterranean seawater. Int J Syst Evol Microbiol 62: 438–444. [DOI] [PubMed] [Google Scholar]
  36. Passeri, A. , Schmidt, M. , Haffner, T. , Wray, V. , Lang, S. , and Wagner, F. (1992) Marine biosurfactants. IV. Production, characterization and biosynthesis of an anionic glucose lipid from the marine bacterial strain MM1. Appl Microbiol Biotechnol 37: 281–286. [Google Scholar]
  37. Peix, A. , Ramírez‐Bahena, M.‐H. , and Velázquez, E. (2018) The current status on the taxonomy of Pseudomonas revisited: an update. Infect Genet Evol 57: 106–116. [DOI] [PubMed] [Google Scholar]
  38. Peña‐García, C. , Martínez‐Martínez, M. , Reyes‐Duarte, D. , and Ferrer, M. (2016) High throughput screening of esterases, lipases and phospholipases in mutant and metagenomic libraries: a review. Comb Chem High Throughput Screen 19: 605–615. [DOI] [PubMed] [Google Scholar]
  39. Popovic, A. , Tchigvintsev, A. , Tran, H. , Chernikova, T.N. , Golyshina, O.V. , Yakimov, M.M. , et al (2015) Metagenomics as a tool for enzyme discovery: hydrolytic enzymes from marine‐related metagenomes. Adv Exp Med Biol 883: 1–20. [DOI] [PubMed] [Google Scholar]
  40. Popovic, A. , Hai, T. , Tchigvintsev, A. , Hajighasemi, M. , Nocek, B. , Khusnutdinova, A.N. , et al (2017) Activity screening of environmental metagenomic libraries reveals novel carboxylesterase families. Sci Rep 7: 44103. [DOI] [PMC free article] [PubMed] [Google Scholar]
  41. Sánchez, D. , Mulet, M. , Rodríguez, A.C. , David, Z. , Lalucat, J. , and García‐Valdés, E. (2014) Pseudomonas aestusnigri sp. nov., isolated from crude oil‐contaminated intertidal sand samples after the Prestige oil spill. Syst Appl Microbiol 37: 89–94. [DOI] [PubMed] [Google Scholar]
  42. Sankararaman, S. , and Sferra, T.J. (2018) Are we going nuts on coconut oil? Curr Nutr Rep 7: 107–115. [DOI] [PubMed] [Google Scholar]
  43. Schmidt, J. , Wei, R. , Oeser, T. , Dedavid e Silva, L. , Breite, D. , Schulze, A. and Zimmermann, W. (2017) Degradation of polyester polyurethane by bacterial polyester hydrolases. Polymers (Basel) 9: 65. [DOI] [PMC free article] [PubMed] [Google Scholar]
  44. Studier, F.W. , and Moffatt, B.A. (1986) Use of bacteriophage T7 RNA polymerase to direct selective high‐level expression of cloned genes. J Mol Biol 189: 113–130. [DOI] [PubMed] [Google Scholar]
  45. Thies, S. , Rausch, S.C. , Kovacic, F. , Schmidt‐Thaler, A. , Wilhelm, S. , Rosenau, F. , et al (2016) Metagenomic discovery of novel enzymes and biosurfactants in a slaughterhouse biofilm microbial community. Sci Rep 6: 27035. [DOI] [PMC free article] [PubMed] [Google Scholar]
  46. Troeschel, S.C. , Thies, S. , Link, O. , Real, C.I. , Knops, K. , Wilhelm, S. , et al (2012) Novel broad host range shuttle vectors for expression in Escherichia coli, Bacillus subtilis and Pseudomonas putida . J Biotechnol 161: 71–79. [DOI] [PubMed] [Google Scholar]
  47. Ufarté, L. , Laville, É. , Duquesne, S. , and Potocki‐Veronese, G. (2015) Metagenomics for the discovery of pollutant degrading enzymes. Biotechnol Adv 33: 1845–1854. [DOI] [PubMed] [Google Scholar]
  48. Urbanek, A.K. , Rymowicz, W. , and Mirończuk, A.M. (2018) Degradation of plastics and plastic‐degrading bacteria in cold marine habitats. Appl Microbiol Biotechnol 102: 7669–7678. [DOI] [PMC free article] [PubMed] [Google Scholar]
  49. Vogel, H.J. , and Bonner, D.M. (1956) Acetylornithinase of Escherichia coli: partial purification and some properties. J Biol Chem 218: 97–106. [PubMed] [Google Scholar]
  50. Wallace, P.W. , Haernvall, K. , Ribitsch, D. , Zitzenbacher, S. , Schittmayer, M. , Steinkellner, G. , et al (2017) PpEst is a novel PBAT degrading polyesterase identified by proteomic screening of Pseudomonas pseudoalcaligenes . Appl Microbiol Biotechnol 101: 2291–2303. [DOI] [PMC free article] [PubMed] [Google Scholar]
  51. Wang, M. , and Sun, L. (2016) Pseudomonas oceani sp. nov., isolated from deep seawater. Int J Syst Evol Microbiol 66: 4250–4255. [DOI] [PubMed] [Google Scholar]
  52. Wei, R. , and Zimmermann, W. (2017) Microbial enzymes for the recycling of recalcitrant petroleum‐based plastics: how far are we? Microb Biotechnol 10: 1308–1322. [DOI] [PMC free article] [PubMed] [Google Scholar]
  53. Wei, R. , Oeser, T. , Then, J. , Kühn, N. , Barth, M. , Schmidt, J. , and Zimmermann, W. (2014) Functional characterization and structural modeling of synthetic polyester‐degrading hydrolases from Thermomonospora curvata . AMB Express 4: 44. [DOI] [PMC free article] [PubMed] [Google Scholar]
  54. Wei, R. , Oeser, T. , Schmidt, J. , Meier, R. , Barth, M. , Then, J. , and Zimmermann, W. (2016) Engineered bacterial polyester hydrolases efficiently degrade polyethylene terephthalate due to relieved product inhibition. Biotechnol Bioeng 113: 1658–1665. [DOI] [PubMed] [Google Scholar]
  55. Wierckx, N. , Narancic, T. , Eberlein, C. , Wei, R. , Drzyzga, O. , Magnin, A. , et al (2018) Plastic biodegradation: Challenges and opportunities In Consequences of Microbial Interactions with Hydrocarbons, Oils, and Lipids: Biodegradation and Bioremediation. Handbook of Hydrocarbon and Lipid Microbiology. Steffan R. (ed). Cham: Springer International Publishing, pp. 1–29. [Google Scholar]
  56. Wilkes, R.A. , and Aristilde, L. (2017) Degradation and metabolism of synthetic plastics and associated products by Pseudomonas sp.: capabilities and challenges. J Appl Microbiol 123: 582–593. [DOI] [PubMed] [Google Scholar]
  57. Yoshida, S. , Hiraga, K. , Takehana, T. , Taniguchi, I. , Yamaji, H. , Maeda, Y. , et al (2016) A bacterium that degrades and assimilates poly(ethylene terephthalate). Science 351: 1196–1199. [DOI] [PubMed] [Google Scholar]
  58. Zhang, D.‐C. , Liu, H.‐C. , Zhou, Y.‐G. , Schinner, F. , and Margesin, R. (2011) Pseudomonas bauzanensis sp. nov., isolated from soil. Int J Syst Evol Microbiol 61: 2333–2337. [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Fig. S1. Molecular structures of the discussed substrates.

Fig. S2. Growth and polyesterase activities exhibited by Pseudomonas species on agar plates based on artificial sea medium and MME minimal medium.

Fig. S3. Coconut oil/rhodamine B agar plates exposed to different light conditions.

Fig. S4. Effect of the additional supplementation of Fe2+ on the autofluorescence of P. putida on coconut oil +rhodamine B agar plates.

Fig. S5. Polyesterase activities exhibited by Pseudomonas species after prolonged incubation at 4°C.

Fig. S6. Polyesterase exhibited by E. coli BL21(DE3) expressing the F. solani f.sp pisi cutinase gene.

Fig. S7. Schematic workflow for agar plate‐based screening for polyesterase active clones within a (meta‐)genomic library.


Articles from Microbial Biotechnology are provided here courtesy of Wiley

RESOURCES