Opinion Article | Open Access | Published 9th January 2021
Why it’s time to strengthen and widen the microbial test panel
Tim Sandle, Bio Products Laboratory, UK | EJPPS | 254, (2020) | Cite this article | Download this PDF Paper
Introduction
The testing of culture media, and conducting microbiological method suitability studies, disinfectant
efficacy studies, Antimicrobial Effectiveness Test (or Preservative Efficacy Test) and associated
activities, requires the use of a test panel of microorganisms. These organisms need to be
representative of the intended application and be of a suitable range in order to demonstrate that a
low level of viable cells can be recovered without any indication of the inhibition of growth or
excessive growth-promotion (typically defined as the recovery of between 50 to 200% of the
challenge count). This activity provides the basis for the release of culture media or for verifying that
a method is suitable for recovering any microorganisms that might be present in a product sample.
This approach has been established for several decades and in many cases the types of organisms
selected for the panel are drawn from guidance presented in the major pharmacopeia. The test
panels of organisms recommended by compendia along with specific standards are in place to allow
for reproducibility between laboratories. In the case of most standards (such as the disinfectant
efficacy norms), these are designed to be multi-industry. Hence the presented organisms may or
may not be suitable for the intended application.
In addition, with the compendia, all too often the organisms recommended for, say, the Microbial
Limit Test method verification, are applied to the release of all culture media used for all activities,
be that the test for sterility or for the recovery of organisms from water systems.
Not only is this inappropriate – for the microbiologist should be reviewing the panel and deciding
upon the appropriate organisms – the recommended panels have not kept pace with improvements
with our understanding of the types of microorganisms likely to cause contamination. Take, for
example, the inclusion of Salmonella in the panel for the recovery of so-called ‘objectionable
microorganisms’ for use with the Microbial Limits Test ¹. To my knowledge and based on
discussions with microbiologists over a couple of decades, no Salmonella has ever been recovered
from a raw material.
Equally the selection, especially in relation to the testing of culture media used for cleanroom
environmental monitoring, has not moved forwards with the findings from the human microbiome
project and the depth of species richness found on the human skin microbiome.
The argument that the test panel quoted in the compendia is representative and thus if culture
media release testing can recover such organisms then it can reasonably be assumed that any other
similar organisms can be recovered does not really hold up. Unless, that is, the only concern is with
the recovery of non-fastidious mesophilic organisms.
Instead, I maintain that in terms of the appropriate panel, this should be based on:
What is currently being recovered, and
What should theoretically be recovered.
Representing what is in the environment
Addressing the former, the aim would be to widen the test panel, to make the challenge organisms
used more representative of what is being recovered from the environment or samples. With this
many of the organisms recommended by compendia are less suitable. For example, for cleanroom
monitoring if Cladosporium species are the most commonly isolated fungi, why not include these
organisms? Consequently, why continue to include alternative organisms isolated many decades
ago? Such as the isolate from a North Carolina blueberry bush (Aspergillus brasiliensis ATCC 16404).
In addition, if Ralstonia pickettii is the most common isolate recovered from a purified water system,
why not use this organism in place of the isolate from an outer ear infection (Pseudomonas
aeruginosa ATCC 9027), as described in the compendia. Similar arguments can be made with
Staphylococcus aureus, carried on the nares of around 25% of the population. Why use this
organism rather than organisms found in greater abundance on microbial carrying particles released
from the outer epithelial layers of the skin, such as Micrococcus luteus or Staphylococcus
epidermidis? ²
Another consideration is with Acinetobacter, which the is the genus of Gram-negative organisms
most commonly associated with the moist areas of the outer layers of the human body (such as
between the toes or under the arms) ³. Where anaerobic spore formers are of a concern,
metagenomic analysis has identified a higher abundance of Cutibacterium acnes associated with
human hair follicles, meaning that this organism is far more representative than the compendia
prescribed Clostridium sporogenes ⁴.
In terms of what to include, microbiologists should regularly screen and trend the microorganisms
recovered according to area monitored and sample type. Studying the range, types and patterns of
microorganisms also assists with contamination control.
Using environmental isolates?
A related matter is whether replacement organisms or panel extension should be made up from
cultures purchased from a culture collection (and hence which permit inter-laboratory
reproducibility, should it be necessary) or made up of environmental isolates (synonyms are
'wildtype' and 'plant isolate') drawn from the manufacturing site. Arguments in favour of
environmental isolates is that they will not have been sub-cultured innumerable times; they are
representative of the facility microbiota; and they are sometimes more challenging to recover, given
the adaption they have undergone when subjected to environmental stressors within the cleanroom
(such as nutrient depletion, exposure to ultraviolet light, or osmotic shock) ⁵.
Whereas cultures derived from culture collections will not be in the same physiological state.
Organisms that have resided in culture collections for decades have been grown on nutritive rich
media over many, many generations and hence they have 'adapted' to be recovered on such media).
The sole use of these organisms may not be sufficient to provide confidence that the medium can
recover sublethally damaged organisms, exposed to a disinfectant, for example ⁶.
Some microbiologists, who favour an expanded panel, have a preference for type cultures and
maintain that environmental isolates are not able to be standardized and therefore the test methods
developed and used across different laboratories will not be comparable since different organisms
have been used. Others are of the opinion organisms may well have been recovered in a stressed
condition, but the stress adaptive response is not permanent and, after subculturing, the organism
from the environment is not significantly different from any other laboratory strain.
Regulatory trends
Microbiologists should also pay attention to regulatory concerns in relation to certain products or
their route of administration. With inhalation products, simply screening using the compendial test
panel does not address the serious contamination potential posed by the thirty or so serovars that
constitute the Burkholderia cepacia complex ⁷.
What theoretically should be recovered?
With the second point, the human microbiome studies indicate that the organisms deposited into
the environment are more diverse than perhaps environmental monitoring data suggests. While it is
impossible to test every potential organism, the desire to ensure that the test panel is
representative should lead microbiologists to reconsider what is included.
An example is with the inclusion of Streptococcus. Not only is this organism difficult to recover from
some formulations or preparations of tryptone soya agar its recovery signifies a contamination
control concern (such as an ill-fitting face mask). In aseptic operations in particular, pharmaceutical
microbiologists should wish to know whether or not their agars and incubation regime can recover
organisms associated with the nasopharynx contamination vector ⁸.
Summary
The arguments made here are for a review if the panel and the likely replacement of some or all of
the test set, with the test varying according to application (media used for water testing will have a
different panel to organisms used for sterility testing, for example) ⁹ ¹⁰. There can be no specific
guidance given in terms of the size of the panel, as this needs to be based on risk assessment,
balancing practicalities and resources against the desire to be suitably representative.
In outlining the argument for a more scientific approach for the microbial test panel, it should also
be noted that there is some regulatory shift in this direction. While this is less so with method
qualification there are indications, from FDA warning letters for instance, for requiring periodic
challenges of prepared media with low levels of organisms beyond compendia indicator organisms,
such as those which represent normal flora.
References
01. Sutton S. (2012) What is an objectionable organism? Am Pharm Rev.15(6): 36–48.
02. Jiminez, L. (2004) Microorganisms in the Environment and their relevance to
Pharmaceutical Processes. In Jiminez, L. (Ed.) Microbial Contamination Control in the Pharmaceutical Industry, Marcel-Dekker, New York, pp 8-9
03. Grice, E.A. and Serge, J. A. (2011) The Skin Microbiome, Nat Rev Microbiol. 9(4):244-53. https://doi.org/10.1038/nrmicro2537
04. Tidswell, E.C. and Boone, K. (2020) Microbiological risk, Cutibacterium acnes, culture medium, incubation conditions, monitoring, controls, PDA Journal of Pharmaceutical Science and Technology pdajpst.2019.010975; DOI:
https://doi.org/10.5731/pdajpst.2019.010975
05. Westney, R. (2013) The Role of In-House Microbial Isolates in Contamination Control. In Madsen, R. E. and Moldenhauer, J. (Eds.) Contamination Control in Healthcare Product Manufacturing, Volume 1, Parenteral Drug Association / DHI, U.S., pp475-504
06. La Duc, M. T.; Dekas, A.; Osman, S.; Moissl, M.; Newcombe, D.; Venkateswaran, K. (2007) Isolation and characterization of bacteria capable of tolerating the extreme conditions of cleanroom environments. Appl. Environ. Microbiol., 73 (8), 2600 –2611
07. Torbeck L, Raccasi, D., Guilfoyle, D. E., Friedman, R. L., Hussong, D. (2011) Burkholderia cepacia: This Decision is Overdue. PDA J. Pharm. Sci. Tech., 65(5): 535-43
08. Ylikoski, J., Savolainen, S. and Jousimies-Somer, H. (1989) Bacterial flora in the
nasopharynx and nasal cavity of healthy young men, ORL J Otorhinolaryngol Relat Spec. 51(1):50-5
09. Sandle, T. (2011) A Review of Cleanroom Microflora: Types, Trends, and Patterns, PDA Journal of Pharmaceutical Science and Technology, 65 (4): 392-403
10. Sandle, T. (2015) Characterizing the Microbiota of a Pharmaceutical Water System-A Metadata Study, SOJ Microbiology & Infectious Diseases, 3 (2): 1-8
Author Information
Corresponding Author: Tim Sandle, Bio Products Laboratory,
Dagger Lane
Elstree
Hertfordshire
WD6 3BX
Email: tim.sandle@bpl.co.uk
Tel (0) 0208 258 2200