Particularly in the fields of cleanroom technology and sterile products manufacturing, good manufacturing practices (GMPs)
regulations and guidances and technical cleanroom standards are mutually dependent on each other. The classification of air
cleanliness specified in the International Organization for Standardization (ISO) 14644-1:1999 (1, 2) is quoted as a tool
in Annex 1 of the European Union (EU) GMPs (3) and in the US Food and Drug Administration's 2004 aseptic processing guidance
(4). The mutual dependence of GMPs and cleanroom standards is clear in that the ISO cleanroom standards are not application
specific. The standards don't advise which levels of cleanliness are applicable to specific processes. Similarly, the EU GMPs
do not explain how to measure airborne contamination or how to classify a controlled environment.
In May 2003, the European Medicines Agency (EMEA) published a revision to Annex 1 of the EU GMPs that was implemented in September
2003 (5). The 2003 version of the sterile products requirements was created in response to the publication of ISO 14644-1:1999,
the internationally accepted standard for airborne-contamination control. In particular, this version of the EU guidance tried
to clarify a perceived requirement to control ≥5.0-μm airborne particles at very low levels with the ability to measure such
low concentrations reliably. The net effect of the September 2003 changes was to frustrate and confuse industry with requirements
that were written poorly in some areas or were plain bad science in others. In response to industry's negative reaction, the
EMEA initiated another revision to the Annex 1 document. Proposals for the further changes were published on the Eudralex
Web site in November 2004, with a closing date of April 30, 2006 for public comments (6).
The EU GMPs have a much greater impact than on just EU nations and those supplying them with medicines. The complete EU GMPs
are adopted by the Pharmaceutical Inspection Convention and the Pharmaceutical Inspection Co-operation Scheme and are referred
to as the PIC/S GMPs (7). In turn, many nations adopt this document as their GMPs. Thus, the effect of poorly written documents
with elements of poor science could reverberate around the world and lead to confusion and unnecessary environmental control,
monitoring, and deviation investigation work.
 Table I: Proposed number of airborne particles in environmental grades A–D (per the November 2005 draft proposals).
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At present, industry has the opportunity to correct these problems and move forward in a positive way by ensuring that it
makes significant improvements to Annex 1 of the EU GMPs. Failure to improve this document could endorse bad science.
Grade limits for airborne particles: classification
The following list includes the effects of the November 2005 draft proposals for airborne particles (see Table I) and associated
requirements for classification and monitoring:
- Industry wants and expects to have excellent control of ≥0.5-μm particles and expects negligible concentrations of ≥5.0-μm
particles in Grades A (at rest and operational) and B (at rest).
- Industry wants to avoid extremely large sample sizes for formal classification that would be required by specifying a very
low limit.
- 1-m3 samples must be taken at each location for a formal classification of Grade A zones at rest and in operation, which is much
more demanding than the current requirement to collect a total of 1 m3 for the zone under consideration.
- The sample size for Grade B at rest is not provided in the guidance. It might be thought that the 1-m3 sample size applies, however. If this is the case, then industry will bear a huge burden of airborne particle counting with
limited value. It is for this reason that a formal classification of ≥5.0-μm particles in Grade B at rest should be avoided.
- Industry must avoid triggering classification or monitoring failures because airborne particles measurements could be in a
range for which real and false counts might be confused. In formal classification, the proposed acceptance of a limit of 20
particles/m3 will be very helpful.
- A full classification of "in operation" conditions is required. This process would require an invasive testing regime not
demanded previously. It always has been accepted that adequate confidence can be obtained from the "at rest" classification
combined with operational monitoring. The guidance proposals suggest this "operational" classification could be carried out
during media fills. Many parties will find it is an inappropriate time to add challenge to the process environment.