Open Access

A preliminary report on the contact-independent antagonism of Pseudogymnoascus destructans by Rhodococcus rhodochrousstrain DAP96253

  • Christopher T Cornelison1Email author,
  • M Kevin Keel2,
  • Kyle T Gabriel1,
  • Courtney K Barlament1,
  • Trudy A Tucker1,
  • George E Pierce1 and
  • Sidney A Crow1
BMC Microbiology201414:246

DOI: 10.1186/s12866-014-0246-y

Received: 3 June 2014

Accepted: 11 September 2014

Published: 26 September 2014

Abstract

Background

The recently-identified causative agent of White-Nose Syndrome (WNS), Pseudogymnoascus destructans, has been responsible for the mortality of an estimated 5.5 million North American bats since its emergence in 2006. A primary focus of the National Response Plan, established by multiple state, federal and tribal agencies in 2011, was the identification of biological control options for WNS. In an effort to identify potential biological control options for WNS, multiply induced cells of Rhodococcus rhodochrous strain DAP96253 was screened for anti-P. destructans activity.

Results

Conidia and mycelial plugs of P. destructans were exposed to induced R. rhodochrous in a closed air-space at 15°C, 7°C and 4°C and were evaluated for contact-independent inhibition of conidia germination and mycelial extension with positive results. Additionally, in situ application methods for induced R. rhodochrous, such as fixed-cell catalyst and fermentation cell-paste in non-growth conditions, were screened with positive results. R. rhodochrous was assayed for ex vivo activity via exposure to bat tissue explants inoculated with P. destructans conidia. Induced R. rhodochrous completely inhibited growth from conidia at 15°C and had a strong fungistatic effect at 4°C. Induced R. rhodochrous inhibited P. destructans growth from conidia when cultured in a shared air-space with bat tissue explants inoculated with P. destructans conidia.

Conclusion

The identification of inducible biological agents with contact-independent anti- P. destructans activity is a major milestone in the development of viable biological control options for in situ application and provides the first example of contact-independent antagonism of this devastating wildlife pathogen.

Keywords

Pseudogymnoascus destructans Mycelia Conidia Rhodococcus rhodochrous White-Nose Syndrome Biocontrol

Background

The rapid spread and high mortality rates associated with white-nose syndrome (WNS) make the development of in situ treatment options for the causative agent, Pseudogymnoascus destructans[1],[2], a significant objective for wildlife management agencies. Accordingly, the development of biologically-derived treatment options may have advantages over chemical or physical treatments, since classic examples of chemical and physical treatments in karst environments are now a cautionary tale [3]. To this end, "A National Plan for Assisting States, Federal Agencies, and Tribes in Managing White-Nose Syndrome in Bats" [4] was released in May, 2011. In this plan, significant focus was placed on the identification and development of biological control options for WNS.

Rhodococcus rhodochrous strain DAP 96253 is a ubiquitous, soil-associated, Gram-positive bacterium with tremendous metabolic and physiological diversity [5]-[9]. Rhodococcus rhodochrous has been used extensively in bioremediation as well as in the production of nitrile-containing compounds [5]-[7] and it has demonstrated delayed fruit ripening activity with climacteric fruits and vegetables [8]. Several enzymes have been shown to have increased activity and prevalence in bacteria induced to delay fruit ripening and these enzymes may play a role in the observed antifungal activity [8]. Initial investigation of the potential antagonism of P. destructans by R. rhodochrous indicated that, when induced under the protocol outlined in US patents 7,531,343, and 7,531,344 [10],[11], R. rhodochrous strain DAP 96253 demonstrated significant contact-independent antagonism of P. destructans in vitro. As a result, the principal objective of this was evaluation of R. rhodochrous induced with urea for potential in situ application as a biological control agent for P. destructans.

In addition to the strong evidence established via in vitro analysis of the observed antagonism, the evaluation of the efficacy of induced R. rhodochrous was pursued in order to establish in vivo efficacy at preventing fungal invasion of bat tissue. This goal was accomplished using a bat-skin explant assay. The evaluation of induced R. rhodochrous to prevent or reduce the infective potential of P. destructans conidia was demonstrated by the inhibition of P. destructans growth on living bat tissue. This is the first example of antifungal efficacy on living bat skin for any biological control agent of WNS and represents a major milestone in this effort.

In order to optimize biocontrol efficacy and reduce potential cross-contamination of karst environments, various whole- and fixed-cell applications were investigated. The evaluation of various application methods of induced cells of R. rhodochrous for potential in situ application, including whole-cell application, non-growth fermentation cell-paste, and fixed-cell catalyst [8],[12],[13], were conducted. Non-growth fermentation cell-paste demonstrated persistent inhibitory activity and represents the most promising application method evaluated. The associated cell-paste activity is a significant development as it represents multiple hallmarks of ideal biocontrol agents.

Methods

Culture acquisition and maintenance

All P. destructans isolates used in the project were acquired from the WNS diagnostic lab at The University of Georgia Southeastern Cooperative Wildlife Disease Study (UGA SCWDS). Initial investigations have shown very low genetic and physiological variability amongst P. destructans isolates [14]. Accordingly, all assays were conducted with a small isolate sample size (n ≤ 3). P. destructans cultures were maintained on Sabouraud Dextrose Agar (SDA, Difco) or in Sabouraud Dextrose Broth (SDB, Difco) at 4°C, 7°C, or 15°C depending on anticipated usage. P. destructans conidia were harvested from fungal lawns on SDA plates by adding 10 ml of conidia harvesting solution (CHS; 0.05% Tween 80, 0.9% NaCl) to the surface of the plate and gently scrapping with a sterile loop to dislodge conidia. The resulting solution was filtered through glass wool and centrifuged at 5000 rpm for 10 minutes. The resulting supernatant was removed and the spore pellet washed with 5 ml of sterile phosphate buffered saline (PBS, pH = 7), re-suspended, and filtered through glass wool. Conidia were stored in sterile PBS at -20°C. Conidia were stored no longer than six weeks prior to use based on in-house assessment of conidial viability under these conditions (unpublished data). R. rhodochrous strain DAP 96253 cells were maintained as glycerol stock aliquots (30% v/v) from 10 l fermentations carried out at GSU. Fresh glycerol stocks were used as the source of cells at the onset of each assay. The induction process was performed using the addition of urea or urea and cobalt as described in US patents 7,531,343 and 7,531,344 [8],[10],[11].

Co-culture assays with R. rhodochrous

A single-compartment Petri plate (150 mm × 15 mm) was used for a contained air-space to assess P. destructans growth characteristics in the presence of induced cells of R. rhodochrous. A 10 μl inoculum of P. destructans conidia solution (106 ml-1) in a phosphate buffer solution was spread onto SDA in Petri plates (35 mm x 10 mm). Multiply induced cells of R. rhodochrous[10],[11] were inoculated onto Petri plates (35 mm × 10 mm) containing Yeast Extract/Malt Extract agar (YEMEA) with or without urea (7.5 g/l) [8], and cultured in the contained air-space for up to 30 days. All assays were conducted in triplicate. The ability of induced R. rhodochrous to inhibit healthy established hyphae of P. destructans was assessed using mycelial plug assays. A lawn of P. destructans was allowed to grow for up to 20 days at which time a 5-mm-diameter transfer tube was used to remove a plug from the mat of fungus. The plugs were then inserted into a similarly sized core removed from an uninoculated culture plate. The plates were co-incubated in a shared air-space as described previously and radial growth from the plug was assessed over time.

Induced R. rhodochrous germule suppression assay

Thin layers (~750 μl) of 10% SDA were applied to standard microscope slides (24.5 × 76.2 mm) and 100 μl of P. destructans conidia solution (106 ml-1) were spread across the agar surface. R. rhodochrous-inoculated Petri plates (35 mm × 10 mm) were placed in larger Petri plates (150 mm × 15 mm) and sealed with parafilm. Negative controls consisted of similarly-cultured conidia with no R. rhodochrous exposure. All trials were conducted in triplicate. At 4 and 7 days post-inoculation, conidia were observed in a light microscope at 200X magnification for the presence of germule formation. Germules were defined as single mycelial extensions emanating from conidia with a length equal to or greater than the intact conidia. Control and exposed slides were retained and examined daily for up to 21 days after germule formation was first observed on control slides. Recovery of conidia was determined by removing the R. rhodochrous after 24 hours, 72 hours, and 7 days. Slides were observed for 21 days after removal of control agent to assess recovery.

Preparation and evaluation of fixed-cell catalyst and fermentation cell-paste in non-growth conditions

Immobilization of whole bacteria was carried out based on the methods of DeFilippi [12] and Lopez-Gallego et al. [13]. Refinement of immobilized cells to produce active catalyst was carried out according to the methods of Pierce et al. [10],[11]. Evaluation of anti-P. destructans activity of fixed-cell catalyst and fermentation cell-paste was determined in co-culture assays with P. destructans conidia and mycelial plugs with various amounts of control agent (<1.0 g), as described previously. Efficacy was determined by observation of germule formation as compared to unexposed controls for growth from conidia, and as percent reduction in radial growth of mycelial plugs.

Ex vivo anti-infectivity assay

The potential for induced R. rhodochrous to inhibit fungal growth on bat skin explants was evaluated using an ex vivo model of WNS. A 10-mm-diameter biopsy punch was used to collect full-thickness samples of skin (n = 40) from the patagium of bats (n = 2) immediately after euthanasia. The explants were adhered to a mesh support with tissue adhesive (TissueTek®) so that they would retain their shape and could be supported at the medium surface without allowing media to come in contact with the inoculated surface of the skin. The skin explants were then maintained on Eagle's modified minimal essential medium supplemented with antibiotics (kanamycin, 100 μg/ml: amikacin, 20 μg/ml; and vancomycin 50 μg/ml). A suspension of spores was placed onto the center of the explant and allowed to dry. The inoculated explants were incubated in a shared air-space with induced R. rhodochrous. Uninoculated control explants were incubated alone or with uninduced R. rhodochrous. Initial experiments were conducted at 7°C. Anti-infective efficacy was determined by visual and microscopic evaluation of bat wing membrane tissue cultures exposed to induced R. rhodochrous as compared to unexposed and uninduced controls.

Results

Anti-P. destructans activity of induced R. rhodochrous

Initial experiments with induced cells of R. rhodochrous demonstrated complete inhibition of growth from conidia of P. destructans when cultured with a shared air-space at 15°C (Figure 1a-c). Uninduced cells of R. rhodochrous showed no signs of inhibition, and were comparable to unexposed controls. Subsequent testing at 4°C demonstrated fungistatic activity of induced cells of R. rhodochrous and resulted in slower germination and reduced total mycelial growth as compared to uninduced cells of R. rhodochrous and unexposed controls (Figure 1d-f). Inclusion of activated carbon into the shared air-space abolished the anti-P. destructans activity of induced R. rhodochrous (Figure 1c). Mycelial plugs of P. destructans cultured in a shared air-space with induced R. rhodochrous had a significant reduction in radial mycelial extension as compared to control plugs cultured in the absence of induced cells of R. rhodochrous (Figure 2). Radial growth of induced R. rhodochrous-exposed P. destructans at 28 days post inoculation indicated a 35% reduction in radial mycelial extension as compared to unexposed controls. This inhibitory activity was statistically significant (p ≤ 0.05) on days 8, 12, 16, and 20 across all replicates (Figure 2).
https://static-content.springer.com/image/art%3A10.1186%2Fs12866-014-0246-y/MediaObjects/12866_2014_Article_246_Fig1_HTML.jpg
Figure 1

Shared air-space co-culture of P. destructans conidia with R. rhodochrous . Uninduced cells (e), induced cells (b, c and f) and P. destructans control (a, d) were incubated in a shared air-space at 15°C (top panel) and 4°C (bottom panel). Induced R. rhodochrous fails to inhibit growth from conidia when activated carbon is included in the head-space (c).

https://static-content.springer.com/image/art%3A10.1186%2Fs12866-014-0246-y/MediaObjects/12866_2014_Article_246_Fig2_HTML.jpg
Figure 2

Induced R. rhodochrous inhibits radial mycelial growth of P. destructans . Growth areas of P. destructans plugs exposed to induced R. rhodochrous compared to P. destructans control plugs. All trials were conducted at 15°C. * indicates days post inoculation with statistically significant (P ≤ 0.05) radial growth inhibition.

Induced R. rhodochrous permanently and persistently inhibits conidia germination

Slide agar overlays inoculated with P. destructans conidia and exposed to induced R. rhodochrous failed to produce germules 21 days after removal of R. rhodochrous (Figure 3). Conidia exposed to induced cells of R. rhodochrous for only 24 hours revealed no signs of germule formation, whereas conidia exposed for 4 and 7 days exhibited early signs of germination but no obvious germules (Figure 3).
https://static-content.springer.com/image/art%3A10.1186%2Fs12866-014-0246-y/MediaObjects/12866_2014_Article_246_Fig3_HTML.jpg
Figure 3

Persistent suppression of P. destructans germination by induced R. rhodochrous . P. destructans conidia are unable to recover after 24-hour exposure to induced R. rhodochrous. P. destructans control slide (a) produced significant mycelia growth and conidiation (white arrow) after 5 days. P. destructans conidia exposed to induced Rhodococcus for 24 hours (b), 72 hours (c) and 7 days (d) failed to form germules 21 days after removal of induced R. rhodochrous. Halted germination was observed in 72-hour and 7-day exposures (black arrows). All images were captured at 200X magnification.

Ex vivo anti-infectivity activity of induced R. rhodochrous

Induced R. rhodochrous completely inhibited the colonization of bat wing explants by P. destructans conidia in all replicates (n = 20) when incubated in a shared air-space for up to 21 days at 7°C (Figure 4). Explants exposed to uninduced R. rhodochrous and unexposed explants were fully colonized at 14 days post inoculation. Histopathological assessments of explants were conducted. However, in this experiment no fungal growth was detected on any induced Rhodococcus exposed explants. Therefore the histopathology of otherwise "healthy" explants provided no additional data to this experiment. Histopathology of the control explants adheres to the histopathology of WNS in bats as described by Cryan et al. [15]. Spore germination assays, and the bat wing explant study relied upon qualitative visual and microscopic evaluation and produced definitive results (i.e. no exposed explants developed fungal growth) therefore a statistical evaluation is unwarranted and omitted.
https://static-content.springer.com/image/art%3A10.1186%2Fs12866-014-0246-y/MediaObjects/12866_2014_Article_246_Fig4_HTML.jpg
Figure 4

Induced R. rhodochrous prevents fungal colonization of bat tissue when contained in a shared air-space. Bat wing tissue explants in a shared air-space with induced R. rhodochrous 21 days post-inoculation with P. destructans conidia (a). Magnified image of a control explant with visible fungal colonization 21 days post-inoculation (b).

Evaluation of fixed-cell catalyst and fermentation cell-paste

Fixed-cell catalyst [8],[10],[11] failed to inhibit or slow growth from conidia of P. destructans when grown in a shared air-space. Fermentation cell-paste in quantities of 1.0 g, 0.5 g, and 0.25 g completely inhibited growth from conidia of P. destructans for greater than 80 days (Figure 5a-c).
https://static-content.springer.com/image/art%3A10.1186%2Fs12866-014-0246-y/MediaObjects/12866_2014_Article_246_Fig5_HTML.jpg
Figure 5

Non-growth cell-paste of R. rhodochrous inhibits growth from conidia of P. destructans . Non-growth fermentation cell-paste of induced R. rhodochrous was incubated in a shared air-space with P. destructans conidia inoculated plates. Quantities of 1.0 g, 0.5 g, and 0.25 g (a, b, and c) all demonstrated complete inhibition of growth from conidia of P. destructans as compared to unexposed controls (d, white arrow). Image taken 21 days post-inoculation.

Discussion and conclusion

Since its initial documentation in 2006, WNS has spread to twenty-four states and four provinces and has been implicated in the mortality of millions of North American bats [16]-[18] which may have a significant impact on North American agricultural practices [19]. WNS is characterized by invasive mycelial growth on the wings, muzzle and ears of hibernating bats that perturbs physiological functions of the host tissues leading to mortality [15]. Cave closures and culling of infected individuals appears to have little to no impact on the spread and mortality associated with this devastating disease [20]. Classic disease management practices applied in agriculture, such as vaccination and broad-spectrum dissemination of antibiotics, present many challenges in the management of disease in wild, highly disseminated, and migratory animal populations. Consequently, the development of novel treatment options are needed to avert the spread of WNS and reduce the mortality associated with currently infected hibernacula. To this end, the development of biologically-based control tools is the preferred option for application in karst environments.

Since the publication of the national response plan [4], several groups have initiated investigations to identify potential biological control agents for P. destructans[21]-[23]. Several of the investigations have relied on traditional sources of biocontrol agents or probiotics such as bacilli and lactobacilli, or competitive exclusion fungi such as Trichoderma sp., as well as attempts to isolate bat-skin-associated microbes with anti-P. destructans activity [21]-[23]. While these approaches have proven successful in agricultural and human health applications [24]-[27], their application in the attempted remediation of WNS in bats has not been demonstrated. The requirement for contact with P. destructans and the bat hosts is a major hurdle for any agents reliant on competitive exclusion or non-volatile antimicrobial compound production. These potential control agents may prove to have limited efficacy against P. destructans in situ and potentially be harmful to the bat hosts. In contrast, the evaluation of induced R. rhodochrous strain DAP 96253 for application as a biological control agent of P. destructans aligns ideally with the needs of wildlife management agencies tasked with combatting WNS and is the first documented contact-independent microbial antagonism of P. destructans.

The evolutionary lineage of R. rhodochrous lends itself to VOC-based fungistasis due to its terrestrial ancestry [28]-[30]. The global prevalence of fungistatic soils is a measure of the natural antagonisms that exists in these complex environments [28]-[32]. Due to the ubiquity of R. rhodochrous in soils [5], it can be expected that R. rhodochrous as well as many other soil-dwelling bacteria have the potential to contribute to VOC-based fungistasis observed in these environments [29],[30]. However, the development of induction methodologies is required to optimize this activity for biocontrol applications and is a decidedly advantageous quality of R. rhodochrous strain DAP 96253 as a potential biological control agent of WNS [33]. Leveraging this naturally evolved antagonism for control efforts has many benefits, particularly in the case of WNS. The complexity of soil ecology selects for antagonisms that are effective at low concentrations in diverse, compartmentalized environments where soluble diffusion may be limited [29]. Therefore, the production of antagonistic VOCs provides a viable means for soil-dwelling bacteria to compete with soil-dwelling fungi for resources and equates favorably with the environmental conditions of susceptible bat hibernacula. The ability of R. rhodochrous to detect and interfere with volatile signals has also been demonstrated in its delayed fruit-ripening activity [8] and is hypothesized to mediate the observed anti-P. destructans activity.

While the efficacy of urea-induced R. rhodochrous under growth conditions is promising for in situ management of WNS, the need for growth media supplementation poses problems for field application. The long term in vitro efficacy of non-growth-condition cell-paste at 4°C allows for increased confidence in forecasting the efficacy of this biocontrol agent in managing WNS in the field as this temperature is a sound approximation of average winter temperature of North American bat hibernacula [34]. The lack of growth media reduces the costs associated with application as well as reduces the likelihood of cross-contamination of control agent media with native cave microflora. In addition, the contact-independent basis of the non-growth antagonism will allow for in situ application methods that will reduce the potential for ecological impacts associated with introducing exogenous organisms to karst environments. The ecological impacts of any potential control agent are of significant concern for wildlife management agencies and the evaluation of potential ecological impacts must be assessed in order to circumvent ecological disasters associated with augmenting cave microflora (e.g. Lascaux cave) [4].

The evaluation of R. rhodochrous using ex vivo bat tissue explants as an indicator of anti-infective activity was paramount to establishing R. rhodochrous as a viable biocontrol agent of P. destructans. This was the first demonstration of inhibition of fungal colonization of bat tissue by a biological control agent. This ex vivo efficacy justifies further in vivo studies with live bats and should be pursued vigorously.

The ability of dormant conidia to remain viable in host-free environments increases long-term impacts of fungal pathogens and renders contaminated environments inhospitable to re-colonization [35]. The impact of WNS in locations such as New York has been tremendous, vastly reducing the populations of insectivorous bats over a broad geographic range. The permanent and persistent inhibition of conidia germination is a promising result and indicates that treatment of previously decimated hibernacula to inactivate resident conidia prior to re-colonization attempts may be feasible by applying induced R. rhodochrous in these environments. However further investigations are needed to confirm the applicability of this approach.

The evaluation of R. rhodochrous strain DAP 96253 has demonstrated the tremendous potential of this organism for application as a biological control agent of P. destructans. This is the first and only demonstration of contact-independent antagonism of P. destructans and represents a significant step toward the development of biologically-based treatment tools for WNS.

Declarations

Acknowledgements

This work was funded by Bat Conservation International through a WNS research grant as well as the Georgia State University Environmental Research Program. The authors would like to thank Lisa Last and Page Luttrell for assistance with the maintenance of tissue explants. The authors would also like to thank Ian Sarad, Blake Cherney, and Ben Poodiak for their contributions to this effort.

Authors’ Affiliations

(1)
Applied and Environmental Microbiology, Georgia State University
(2)
Department of Pathology Microbiology & Immunology, University of California Davis

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© Cornelison et al.; licensee BioMed Central Ltd. 2014

This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.

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