Sunday, August 26, 2007

Overview of Pharmaceutical Product Development and Its Associated Quality System Potency Method Validation

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M2 Presswire , 09/21/2006

Overview of Pharmaceutical Product Development and Its Associated Quality System Potency Method Validation.

COPYRIGHT 2006 M2 Communications Ltd.


M2 PRESSWIRE-21 September 2006-Research and Markets: Overview of Pharmaceutical Product Development and Its Associated Quality System Potency Method Validation(C)1994-2006 M2 COMMUNICATIONS LTD RDATE:22092006
Dublin - Research and Markets (http://www.researchandmarkets.com/reports/c42485) has announced the addition of "Analytical Method Validation and Instrument Performance Verification" to their offering.
Validation describes the procedures used to analyze pharmaceutical products so that the data generated will comply with the requirements of regulatory bodies of the US, Canada, Europe and Japan. Calibration of Instruments describes the process of fixing, checking or correcting the graduations of instruments so that they comply with those regulatory bodies. This book provides a thorough explanation of both the fundamental and practical aspects of biopharmaceutical and bioanalytical methods validation.
It teaches the proper procedures for using the tools and analysis methods in a regulated lab setting. Readers will learn the appropriate procedures for calibration of laboratory instrumentation and validation of analytical methods of analysis. These procedures must be executed properly in all regulated laboratories, including pharmaceutical and biopharmaceutical laboratories, clinical testing laboratories (hospitals, medical offices) and in food and cosmetic testing laboratories.
KKey Topics Covered Include:
Method Validation for HPLC Analysis of Related Substances in Pharmaceutical Drug ProductsOverview of Pharmaceutical Product Development and Its Associated Quality SystemPotency Method ValidationDissolution Method ValidationDevelopment and Validation of Automated MethodsAnalysis of Pharmaceutical Inactive IngredientsValidation Study of JP Heavy Metal Limit TestBioanalytical Method ValidationProcurement, Qualification, and Calibration of Laboratory Instruments: An OverviewPerformance Verification of UV-Vis SpectrophotometersPerformance Verification of HPLCOperational Qualification of a Capillary Electrophoresis InstrumentLC-MS Instrument CalibrationKarl Fisher Apparatus and Its Performance VerificationThe pH Meter and Its Performance VerificationQualification of Environmental ChambersEquipment Qualification and Computer System ValidationValidation of Excel Spreadsheet
For more information visit http://www.researchandmarkets.com/reports/c42485

CONTACT: Laura Wood, Senior Manager, Research and MarketsFax: +353 1 4100 980 e-mail: press@researchandmarkets.com
((M2 Communications Ltd disclaims all liability for information provided within M2 PressWIRE. Data prepared by named party/parties. Further information on M2 PressWIRE can be obtained at http://www.presswire.net on the world wide web. Inquiries to info@m2.com)).

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Test scripts speed validation.(IN THE SPOTLIGHT

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Pharmaceutical Technology , 11/01/2006 30 11

Test scripts speed validation.(IN THE SPOTLIGHT: Editors' Picks of Pharmaceutical Science & Technology Innovations)(MasterControl introduced validation test scripts for its software suite)(Brief article)

COPYRIGHT 2006 Advanstar Communications, Inc.


MasterControl (Salt Lake City, UT, www.mastercontrol.com) has introduced an addition to its software suite for quality-management. The "Transfer Operational Qualification" (TOQ) CD contains validation test scripts executed by the company. David Ade, product manager at MasterControl, says the TOQ CD offers full documentation, including the validation plans, risk assessment, user requirements, and functional requirements for MasterControl's software suite. "We executed the test scripts just like our customers would, using proper documentation procedures," Ade explains. Based on their risk assessments, the software suite's users can incorporate the TOQ scripts as part of their validation projects, thereby saving time and expense that otherwise would be dedicated to retesting and revalidation. The time users save can be dedicated to executing performance qualification.
New Product Announcements may be sent to New Products Editor, Pharmaceutical Technology, 485 Route One South, Building F, First Floor, Iselin, NJ 08830, fax 732.596.0005, ptpress@advanstar.com.
[ILLUSTRATION OMITTED]

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A single adulteration limit for cleaning validation: in a pharmaceutical pilot-plant environment

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Pharmaceutical Technology , 01/01/2007 31 1
A single adulteration limit for cleaning validation: in a pharmaceutical pilot-plant environment.(Data and Review: Cleaning Validation) Forsyth, Richard J. *~|~*Leblanc, Alain *~|~*Voaden, Mark *~|~*
COPYRIGHT 2007 Advanstar Communications, Inc.

An adulteration limit of 100 [micro]g/25[cm.sup.2] (4 [micro]g/[cm.sup.2]) was proposed for pilot-plant facilities. The dynamic changes in equipment, formulation, and residue determination made implementation of a constantly changing, calculated adulteration limit impractical. A single adulteration limit was simpler to communicate and document, making compliance achievable. The limit would be used only after it was determined to be lower than a health-based evaluation and a visual-cleanliness assessment. Keywords: adulteration limit, cleaning validation, compliance, pilot plant.
**********
A well run cleaning-validation program requires a significant amount of planning and resources. Planning takes into account the size, configuration, and complexity of the manufacturing equipment; the physical properties of the soils encountered, which directly affect the cleaning procedure used; the detergent to clean the equipment; the type of swab or rinse sampling to capture residue levels; the analytical test methods to determine residue levels; the periodic monitoring of the system to ensure ongoing compliance; change control to address new residues and equipment; appropriate documentation; and training for personnel cleaning equipment and performing validation challenges. Required resources include equipment downtime for the validation, raw materials for the formulations tested, analytical instrumentation for analysis, detergents for cleaning, solvents for testing, and personnel to perform the validation.
The entire cleaning-validation program and its execution depend directly on the acceptable residue limit (ARL) for the formulation residue. The active pharmaceutical ingredient (API) residue is monitored because it is the most phamacologically active component of the formulation. The ARL established for a program must be scientifically justified on the basis of the needs and capabilities of the manufacturing facility. In its Guide to Inspection of Validation of Cleaning Processes (1), the US Food and Drug Administration stated that residue limits should be logical, practical, achievable, and verifiable. The agency did not intend to set acceptance limits for validating cleaning processes. One of the examples cited as a possible residue limit used in industry, however, was 10 ppm of carryover into the subsequent batch manufactured.
The purpose of cleaning validation is to prevent the cross-contamination of a drug formulation. The primary concerns of cross-contamination are an evaluation of the therapeutic-dose carryover or the toxicity of the potential contaminant. Any contaminant is undesirable, but one with a pharmacologic or toxicological effect is far more serious. The Food, Drug, and Cosmetic Act (2) states: "A drug ... shall be deemed to be adulterated if it consists in whole or in part of any filthy, putrid, or decomposed substance," that is, something that will cause an adverse pharmacological effect. This definition supports the pharmacological and toxicological concerns.
If, however, the amount of a residue is below the level at which it would have an unintended, adverse health effect, what is the allowable level from an adulteration standpoint? Should a health-based limit be the only limit for equipment cleaning? Should the analytical-method detection limit be the standard (3)? Or, if an intermediate adulteration limit exists, what rationale determines that level? In the past, analytical methodology had limited sensitivity, making health-based and adulteration-based contaminations essentially equivalent. The increased sensitivity of analytical methodology seemingly has created a contradictory situation. Modern analytical detection limits are far lower than the pharmacological levels of drugs, thus creating a divergence between the previously equivalent health-based and adulteration definitions.
A logical residue limit would be one that demonstrates no pharmacological or toxicological effect, without regard to analytical sensitivity. This would indicate that residue levels can be as high or as low as the health-based limit will allow. This approach, however, would allow equipment to be visually dirty for relatively safe residues, which indicates an inadequate cleaning procedure. A logical residue limit also should leave the equipment visually clean. Setting residue limits any lower than the health-based and visible levels does not appear to be necessary or logical and adds no additional value to the cleaning process.
Several cleaning-validation programs use the dual health-based--adulteration-based criterion (4-6). Evaluations based on toxicity, tablet weight, number of doses administered, swab recovery, swab area or equipment surface area, and batch size determined the ARLs from both an adulteration-based and health-based perspective. The lower of the two limits was the designated ARL for the formulation and the equipment.
The cleaning-validation program in our pilot-plant facility calculated ARLs for both the health-based and adulteration-based criteria and used the lower of the two (7). The dynamic nature of the pilot plant and the drug-development process necessitated regular re-evaluation of the ARL for each API. Each API required a health-based evaluation, but the majority of development compounds had such low toxicity that their adulteration limits were lower. A proposed alternative to the constant re-evaluation of adulteration limits was to use a constant adulteration limit of 100 [micro]g/25 [cm.sup.2] swab or 4 [micro]g/[cm.sup.2]. This technique would streamline the cleaning process and minimize potential errors without compromising quality or safety.
Health-based risk assessment
To implement an adulteration limit, it must be lower than the associated health-based ARL. The adulteration limit would be lower at the level at which compounds are not likely to be potent, highly toxic, or carcinogenic. A corresponding allowable daily intake (ADI) for this category of material is 100 [micro]g/day (0.1 mg/day) (8).
The calculation for the health-based ARL with an ADI of 0.1 mg/day includes:
ADI x tablets per batch x swab area x recovery x 1000 [micro]g/mg/max. daily dose x SSA = ARL [micro]g/swab [1]
0.1 mg/day x tablets per batch tablets x 25 [cm.sup.2]/swab x 1 x 1000 [micro]g/mg/max. daily dose tablets/day x SSA [cm.sup.2] = ARL [micro]g/swab [2]
in which ADI is the allowable daily intake for the compound, SSA is the shared product-contact surface areas of the manufacturing equipment train, and recovery is the percentage of spiked material recovered for assay.
Table I shows the health-based ARLs with associated parameters for an ADI of 0.1 mg/day, tablet weight from 0.11.5 g and maximum daily dose from 1-10 tablets. The number of tablets per batch ranged from 266-10,000 (small) to 3600-160,000 (medium) to 46,666-1,000,000 (large), based on batch sizes of 0.4-1 kg (small), 5.4-16 kg (medium), and 70-100 kg (large), respectively. It was assumed that the next batch was manufactured in equipment with the same SSA.
The shaded portions of the small, medium, and large batch ranges in Table I fell below the proposed limit of 100 [micro]g/swab (4 [micro]g/[cm.sup.2]). The low end of each range assumed the smallest batch size, the largest tablet weight (1500 mg), and the highest number of tablets dosed (10).
In the pilot plants, about 5% of manufactured batches fell below the 100 [micro]g/swab (4 [micro]g/[cm.sup.2]) limit. The batches that fell below the 4 [micro]g/[cm.sup.2] limit were typically for clinical studies with large tablet sizes (> 1000 mg), multiple-tablet doses (>6 tablets/dose) or small batch sizes (<500 g). Small batch sizes generally are for first-in-man studies or preclinical and Phase I studies. These clinical-trial programs are dosed on small populations to establish dose levels.
The risk of falling below the 4 [micro]g/[cm.sup.2] limit for compounds with ADIs&gt;100 [micro]g/day was small, based on the site data. Also, of the 1225 swab samples taken in support of cleaning validation, none failed the ARE for the compound tested, greater than 98% of the swabs were below 1 [micro]g/[cm.sup.2], and more than 99.5% were below 4 [micro]g/[cm.sup.2], further reducing potential risk.
Finally, a continuing program for monitoring cleaning effectiveness using visible residue limits (VRL) was conducted. Of the manufactured batches that fell below the 100 [micro]g/swab (4 [micro]g/[cm.sup.2]) limit, the highest VRL was 1.23 [micro]g/[cm.sup.2], which is well below the health-based limit. Therefore, for compounds with ADIs&gt;100 [micro]g/day, it is extremely unlikely that the adulteration limit selected will be greater than the health-based limit.
Adulteration-based calculation
The adulteration limit was used when it was lower than the health-based limit. For development compounds in the pilot plant (7), the adulteration limit originally was calculated using the following equation:
UAL x batch size/SSA x swab area x recovery x 1000 g/kg = ARL [3]
10 [micro]g/g x MBS kg/SSA [cm.sup.2] x 25 [cm.sup.2]/swab x 1 x 1000 g/kg = ARL [micro]g/swab [4]
in which UAL was the upper acceptance limit; SSA the shared surface area, MBS the minimum batch size for the equipment train, and recovery the fraction of spiked material recovered for assay. The UAL of 10 [micro]g/g (10 ppm) cited by FDA (1) was used in various cleaning-validation programs (3, 9, 10). The SSA was the combined product-contact surface areas of the manufacturing equipment train. The MBS provided the most conservative limit because any residue would be most concentrated in the subsequent batch. The swab area of 25 [cm.sup.2] was used widely (3, 7, 11, 12) in industry.
Calculation of an allowable adulteration level was a logical cleaning limit for a pilot plant but in the long term proved to be impractical. The number of factors that went into the pilot-plant production schedule, the drug-development formulations, and the residue determination made an adulteration assessment a constantly changing number.
Pilot-plant issues
Number of pilot-plant programs. The pilot plant manufactured varied formulations of numerous compounds. The programs in the pilot plant increased with new compounds and decreased as programs ceased development or were transferred to commercial manufacturing. Schedulers, formulators, equipment cleaners, analytical chemists, and quality personnel were involved. The number of programs and personnel along with the associated ARL calculations, documentation, and communication made it difficult to maintain a consistent, compliant program.
Number of new compounds. The number of new compounds entering the pilot plant was significantly greater than the number of new compounds entering a commercial manufacturing facility. These new programs had to be included in the overall cleaning-assessment program. Validating a new compound required significant analytical method development and validation. In addition, the small, early-phase manufacturing equipment was in great demand, and extended downtime for cleaning validation support was problematic.
Subsequent product. The manufacturing schedule in the pilot plant was variable. Equipment was scheduled for use several weeks in advance, but other programs sometimes took priority. Even knowing the subsequent product was no guarantee that a particular formulation was the same as the previous one manufactured for the product. Calculating an ARL based on the subsequent product manufactured in the equipment was problematic.
Current equipment train versus subsequent equipment train. The equipment train was the order in which equipment was used to manufacture a formulation. Blending, granulation, roller compaction, drying, and tablet pressing were examples of unit operations that together manufactured a clinical formulation. The ARL calculation for the equipment train assumed that the same train was used for the subsequent product. This almost never was the case in a pilot plant, which made the value of the ARL limited. An alternative ARL calculation considered each individual piece of equipment without regard to the manufacturing train. This type of ARL consideration became exceedingly cumbersome without adding increased value to the ARL process.
Formulation-development issues
Formulation changes. The formulation for each research compound evolved during development. A dry-filled capsule for a Phase I compound became a film-coated tablet in Phase II. Refinements in formulation composition also were common. Excipient levels changed to optimize the physical properties of the formulation. Formulation changes also resulted from scale-up issues. Formulation modifications often changed the ARL for the subject compound.
Establishing effective dose. The effective dose of an API was unknown when clinical trials began. Dose levels could cover several orders of magnitude for early clinical trials. The results of the ongoing trials determined the dose for file next phase of testing and the eventual market-dose level. Formulations of early-development compounds had different dose levels and batch sizes. The amount of API in a formulation had a direct effect on the ability to clean the equipment. Therefore, cleaning could be assessed after every batch, based on the API factors involved.
Scale-up. Each clinical trial required a larger batch size than the previous trial, which necessitated equipment with a larger capacity. The physical interactions of the formulation components for larger batches often resulted in changes to the formulation or required a different type of manufacturing equipment. Each time the batch size or the equipment train changed, the ARL was reassessed.
Adulteration-determination issues Effect of small batch size or unit operations.
In the pilot-plant environment, initial batch sizes were very small, often on the order of several hundred grams. Calculating an ARE based on the smallest batch size reduced the cleaning limit to a low level and potentially affected a Phase II compound manufactured just before a Phase I compound. Similarly, calculating an ARE for each individual piece of equipment in the manufacturing train resulted in very low cleaning limits for small surface-area equipment.
Rather than calculate the ARL for every clinical batch manufactured, certain assumptions were made to generalize the equation. The most conservative assumption used the minimum batch size for the equipment. This assumption made the generalized ARL lower than a specifically calculated ARL under most circumstances.
The adulteration limit calculation was the following:
UAL x batch size/SSA x swab area x recovery x 1000 g/k. = ARL [5]
10 [micro]g/g x BS kg/SSA [cm.sup.2] x 25 [cm.sup.2]/swab x 1 x 1000 g/kg = ARL [micro]g/swab [6]
Table II shows the product-contact surface areas for a typical equipment train for Phase I (small), Phase II (medium), and Phase III (large) formulations. Table III shows the range of ARLs for a constant UAL of 10 [micro]g/g, a swab area of 25 [cm.sup.2], and a recovery of 100%. The calculated adulteration limit varied from 17 to 216 [micro]g/swab for the same compound, depending on the manufacturing train. The adulteration limit varied from batch to batch for the same compound, making reassessment a routine occurrence.
The variable adulteration limit also brought into question the value of the calculated limit to the overall cleaning program. For small batches, the limit was far below the 10 [micro]g/g level. For larger batches, the calculated adulteration limit was greater than the visually clean level, thus making it obsolete.
Analytical limits. High-performance liquid chromatography and total organic carbon methods were used most frequently. Each analytical test method had very low detection limits, either in the ppm or ppb range. Analytical limits were lower than the calculated health-based and adulteration-based limits. On the basis of instrumental capabilities, the use of analytical limits was considered for the adulteration limit.
Using 0.1% of the subsequent API as the adulteration limit was not appropriate. The 0.1% limit, determined during release testing, was intended for qualifying impurities that were associated with the manufacturing process or related compounds, and not for extraneous impurities caused by cross-contamination. Acceptance limits should reflect the capability of the cleaning processes (13).
Visible residue limits
The determination and use of VRLs demonstrated that the vast majority of formulations and APIs had VRLs lower than 100 [micro]g/25 [cm.sup.2] swab (4 [micro]g/[cm.sup.2]) (14, 15). Of the 54 formulations evaluated to date, all were well below 100 [micro]g/25 [cm.sup.2] swab. Of the 102 APIs, excipients, and detergents evaluated, only five excipients and one API had VRLs greater than 100 [micro]g/25 [cm.sup.2] swab. Limited applications of VRLs have saved resources without sacrificing quality (16, 17).
Swab area. An often cited adulteration limit was 10 ppm or 100 [micro]g/swab, using a swab area of 25 [cm.sup.2] for cleaning validation. This amount was a feasible limit. The swab area was not as important as the scientifically justified limit but was a practical compromise to obtain a representative residue sample against the occasional need to swab smaller pieces of equipment.
Conclusion
The factors that affect the adulteration calculation made it an impractical situation for a pilot-plant application. A constantly changing adulteration limit caused documentation problems and made compliance difficult to enact and enforce.
An alternative single adulteration limit was proposed for compounds with ADIs&gt;100 [micro]g/day. An adulteration limit of 100 [micro]g/25 [cm.sup.2] swab (4 [micro]g/[cm.sup.2]) was satisfactory as long as the equipment was visually clean. This limit ensured that there were no toxicity cross-contamination problems and that the equipment was visually clean. A single, scientifically determined adulteration limit is logical, practical, achievable, and verifiable, making it a justifiable adulteration limit for a pilot-plant facility.
Submitted: June 20, 2006. Accepted: Aug. 24, 2006.
References
(1.) US Food and Drug Administration, Guide to Inspection of Validation of Cleaning Processes, (Rockville, MD, Office of Regulatory Affairs, 1993).
(2.) Food, Drug and Cosmetics Act, Chapter V, Section 501(a)(1), 1938.
(3.) FDA, CDER Human Drug CGMP Notes, 9 (2) (Rockville, MD, Division of Manufacturing and Product Quality, Office of Compliance, Center for Drug Evaluation and Research, 2001).
(4.) G.L. Fourman and M.V. Mullen, "Determining Cleaning Validation Acceptance Limits for Pharmaceutical Manufacturing Operations" Pharm. Technol. 17 (4), 54-60 (1993).
(5.) A.O. Zeller, "Cleaning Validation and Residue Limits: A Contribution to Current Discussions," Pharm. Technol. 17 (10), 70-80 (1993).
(6.) K.M. Jenkins and A.J. Vanderwielen, "Cleaning Validation: An Overall Perspective," Pharm. Technol. 18 (4), 60-73 (1994).
(7.) R.J. Forsyth and D. Haynes, "Cleaning Validation in a Pharmaceutical Research Facility," Pharm. Technol. 22 (9), 104-112 (1998).
(8.) D.G. Dolan et al., "Application of the Threshold of Toxicological Concern Concept to Pharmaceutical Manufacturing Operations," Regul. Toxicol. Pharmacol. 43 (3), 1-9 (2005).
(9.) R. Baffi et al., "A Total Organic Carbon Analysis Method for Validating Cleaning Between Products in Biopharmaceutical Manufacturing," J. Parenter. Sci. Technol. 45 (1), 13-19 (1991).
(10.) R.J. Romanach et al., "Combining Efforts to Clean Equipment in Active Pharmaceutical Ingredient Facilities," Pharm. Technol. 23 (1), 46-58 (1999).
(11.) M.A. Stege et al., "Total Organic Carbon Analysis of Swab Samples for the Cleaning Validation of Bioprocess Fermentation Equipment," BioPharm 9 (4), 42-45 (1996).
(12.) D.A. LeBlanc, "Establishing Scientifically Justified Acceptance Criteria for Cleaning Validation of Finished Drug Products," Pharm. Technol. 22 (10), 136-148 (1998).
(13.) FDA, CDER Human Drug CGMP Notes, 6 (2), 5-6 (Rockville, MD, Division of Manufacturing and Product Quality, Office of Compliance, Center for Drug Evaluation and Research, 1998).
(14.) R.J. Forsyth, V. Van Nostrand, and G. Martin, "Visible Residue Limit for Cleaning Validation and its Potential Application in a Pharmaceutical Research Facility," Pharm. Technol. 28 (10), 58-72 (2004).
(15.) R.J. Forsyth and V. Van Nostrand, "Application of Visible Residue Limit for Cleaning Validation in a Pharmaceutical Manufacturing Facility," Pharm. Technol. 29 (10), 152-161 (2005).
(16.) R.J. Forsyth and V. Van Nostrand, "Using Visible Residue Limits for Introducing New Compounds into a Pharmaceutical Research Facility," Pharm. Technol. 29 (4), 134-140 (2005).
(17.) R.J. Forsyth, J. Hartman, and V. Van Nostrand, "Risk-Management Assessment of Visible-Residue Limits in Cleaning Validation," Pharm. Technol. 30 (9), 104-114 (2006).
* To whom all correspondence should be addressed.
Richard J. Forsyth * is an associate director in global clinical GMP quality with Merck &amp; Co., Inc., WP53C-307, West Point, PA 19486, tel. 215.652.7462, fax 215.652.7106, richard_forsyth@merck.com. Alain Leblanc is a facility manager at Merck Frosst Canada's Center for Therapeutic Research. Mark Voaden is head of service for validation and compliance for facilities with Merck, Sharp &amp; Dohme in the United Kingdom.
<pre>
Table I: Calculated health-based acceptable residue limit
([micro]g/swab).

Allowable daily intake 0.1 mg/day. Swab area is 25 [cm.sup.2].

Tablets per batch/max daily dose (100 could
mean 100 tablets of 1-tablet dose or 400
Shared tablets of 4-tablet dose.)
surface area
[cm.sup.2] 25 100 200 400 500 1000 2000

1000 63 250 500 1000 1250 2500 5000
1500 42 167 333 667 833 1667 3333
2000 31 125 250 500 625 1250 2500
2500 25 100 200 400 500 1000 2000
3000 21 83 167 333 417 833 1667
3500 18 71 143 286 357 714 1429
4000 small 16 63 125 250 313 625 1250
4500 14 56 111 222 278 556 1111
5000 13 50 100 200 250 500 1000
7500 8 33 67 133 167 333 667
10,000 6 25 50 100 125 250 500
15,000 4 17 33 67 83 167 333
20,000 3 13 25 50 63 125 250
37,500 medium 2 7 13 27 33 67 133
50,000 1 5 10 20 25 50 100
75,000 1 3 7 13 17 33 67
100,000 1 3 5 10 13 25 50
150,000 large 0 2 3 7 8 17 33
175,000 0 1 3 6 7 14 29
200,000 0 1 3 5 6 13 25

Tablets per batch/max daily dose (100
could mean 100 tablets of 1-tablet dose
Shared or 400 tablets of 4-tablet dose.)
surface area
[cm.sup.2] 4000 5000 10,000 20,000 50,000

1000 10,000 12,500 25,000 50,000 125,000
1500 6667 8333 16,667 33,333 83,333
2000 5000 6250 12,500 25,000 62,500
2500 4000 5000 10,000 20,000 50,000
3000 3333 4167 8333 16,667 41,667
3500 2857 3571 7143 14,286 35,714
4000 2500 3125 6250 12,500 31,250
4500 2222 2778 5556 11,111 27,778
5000 2000 2500 5000 10,000 25,000
7500 1333 1667 3333 6667 16,667
10,000 1000 1250 2500 5000 12,500
15,000 667 833 1667 3333 8333
20,000 500 625 1250 2500 6250
37,500 267 333 667 1333 3333
50,000 200 250 500 1000 2500
75,000 133 167 333 667 1667
100,000 100 125 250 500 1250
150,000 67 83 167 333 833
175,000 57 71 143 286 714
200,000 50 63 125 250 625

Tablets per batch/max
daily dose (100 could
mean 100 tablets of
1-tablet dose or 400
Shared tablets of 4-tablet dose.)
surface area
[cm.sup.2] 100,000 1,000,000

1000 250,000 2,500,000
1500 166,667 1,666,667
2000 125,000 1,250,000
2500 100,000 1,000,000
3000 83,333 833,333
3500 71,429 714,286
4000 62,500 625,000
4500 55,556 555,556
5000 50,000 500,000
7500 33,333 333,333
10,000 25,000 250,000
15,000 16,667 166,667
20,000 12,500 125,000
37,500 6667 66,667
50,000 5000 50,000
75,000 3333 33,333
100,000 2500 25,000
150,000 1667 16,667
175,000 1429 14,286
200,000 1250 12,500

Table II: Product-contact surface areas (SSA) for typical
equipment trains by phase.

Product-contact surface area ([cm.sup.2])
Equipment
Phase 1: small Phase II: medium Phase III: large

Granulator 851 5833 40,643
Dryer 2643 14,922 27,207
Mill 692 1888 1888
Blender 1364 5436 41,049
Press 406 3738 4957
SSA 5956 31,817 115,744

Table III: Calculated adulteration limit range by phase.

Equipment Surface area Smallest batch ARL
train ([cm.sup.2]) size (kg) ([micro]g/swab)

Small 5956 0.40 16.8
Medium 31,817 5.4 42.4
Large 115,744 75 162

Equipment Medium batch ARL
train size (kg) ([micro]g/swab)

Small 0.80 33.6
Medium 10.0 78.6
Large 90 194

Equipment Largest batch ARL
train size (kg) ([micro]g/swab)

Small 1.0 42.0
Medium 16.0 125.7
Large 100 216

Data represents an upper acceptance limit of 10 [micro]g/g, a swab
area of 25 [cm.sup.2], and a recovery of 100%. ARL is acceptable
residue limit. </pre>

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Validation of a method for the determination of polysorbate 20 residue for the support of the cleaning of pharmaceutical vial closures

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Journal of Validation Technology , 02/01/2007 13 2
Validation of a method for the determination of polysorbate 20 residue for the support of the cleaning of pharmaceutical vial closures. Juarbe, Nieves *~|~*Strege, Mark *~|~*
COPYRIGHT 2007 Advanstar Communications, Inc.

ABSTRACT This report summarizes the development and validation of an analytical procedure to support cleaning validation of pharmaceutical closures (stoppers). Based on current guidelines by regulatory agencies, a sensitive and quantitative test is needed to demonstrate the post-cleaning removal of cleaning agents from vial closures prior to their use. Specifically, an analytical test was required for trace level quantitation of polysorbate 20 (PS20), a non-ionic surfactant used for stopper cleaning. Samples consisted of aqueous solutions from the extraction of rubber vial stoppers and swabs taken from surfaces of equipment such as stainless steel tanks and fiberglass reinforced polyester wash tubs. Total organic carbon (TOC) determination was employed for sample analysis because of ease-of-use, sensitivity, and fast analysis time. This investigation demonstrated the applicability and validity of using stopper extraction, swab sampling, and TOC analysis for the determ!
ination of residual PS20 in support of cleaning validation.
INTRODUCTION
Good manufacturing practice (GMP) requires Pharmaceutical and Biopharmaceutical Industries to strive for the highest manufacturing standards. (1) All phases of the manufacturing process must be controlled for predictability and for delivery of a finished product that consistently meets predetermined quality standards and specifications. The cleaning processes for equipment and supplies in direct contact with the drug product are closely inspected, because an inadequate cleaning procedure can result in adulterated or contaminated product. Important factors to control include the cleanliness of both pharmaceutical closures used in parenteral drug products and the washing equipment (stainless steel tanks and fiberglass wash tubs) used to clean these closures.
The Food and Drug Administration (FDA) and International Conference on Harmonization (ICH) have published guidelines for validating cleaning processes. (2-6) Currently, rinse water and swab testing are the most common approaches used for cleaning validation and verification. This report describes a strategy to meet the challenge of verifying the cleanliness of vial stoppers, and the associated washing equipment, by demonstrating the post-wash removal of the cleaning agent polysorbate 20 (PS20). The common sampling practice for stainless steel and other surfaces that can be reached by hand is to swab representative areas that have been cleaned, extract the swab, and then analyze the extract to demonstrate the effectiveness of the cleaning procedure. Vial rubber stoppers present a unique challenge since they cannot be swabbed like other surfaces due to their size, shape, and surface characteristics.
The extraction procedure and the solvent must be compatible with both the sample and the TOC assay. Therefore, various approaches were evaluated during development of the testing procedure. The safety acceptance criterion established for PS20 was <5[micro]g/[cm.sup.2]. Therefore, based on guidance from toxicology considerations and assessment of the compatibility of PS20 with process, product, and manufacturing components, the analytical test was required to provide a detection range that contained the acceptance limit of 125 [micro]g of PS20 per swab taken from a 25 [cm.sup.2] surface and 25 [micro]g of PS20 per stopper surface of 5 [cm.sup.2].
The surfaces of interest consisted of halobutyl and butyl elastomer rubber from the stoppers, fiberglass reinforced polyester from the washing tubs, and stainless steel from the tanks. Total organic carbon (TOC) was selected as the analytical technique for this study because it has been successfully used throughout the past decade to analyze aqueous-based cleaning samples for the presence of organics and was expected to provide adequate sensitivity. (7-9) A procedure for the extraction and determination of PS20 in the low parts-per-million (ppm) range on the surfaces of stoppers and cleaning equipment (stainless steel and fiberglass-reinforced polyester (FRP)) was developed and validated.
EXPERIMENTAL
Materials
The experimental setup utilized a sucrose standard (42.1% carbon by mass), the system suitability check reagent, parabenzoquinone (1, 4-benzoquinone, PBQ) (66.7% carbon by mass), and purified water. All glassware was rinsed with dilute aqua regia (1 part concentrated HN[O.sub.3]: 3 parts concentrated HCI), followed by a rinse with purified water. The sampling glass bottles (250 mL) with Teflon[R] lined closures were large enough to accommodate the stoppers. The bottles were also used to extract the samples and eliminated the need to transfer the stoppers. Texwipe Alpha[R] Swab TX761 swabs (ITW Texwipe, Kernersville, NC) were used to swab surfaces.
Equipment
A Shimadzu Model TOC-5000 TOC instrument with an ASI-5000 auto-sampler (Shimadzu Scientific Instruments, Columbia, MD) equipped with 4-mL vials was used for all data generation. An Elga Purelab Ultra-purified water system (Vivendi Water Systems, Bucks, UK) and laboratory bench wrist shaker were also employed for this study.
Method
* Establishment of the TOC Assay Range
As described in the introduction, the procedure was designed to provide an assay range that contained the acceptance limit of 5 [micro]g/[cm.sup.2], equivalent to 125 [micro]g of PS20 per swab for an area of 25 [cm.sup.2] surface and 25 [micro]g of PS20 per stopper with a surface area of 5 [cm.sup.2]. The Shimadzu 5000 TOC response is typically linear over a wide range, such as from 0.1 to 100 ppm C or greater. To enable the sample preparation procedure to extract a measurable amount of residual PS20 within the range of the instrument sensitivity (0.1 ppm C is an approximate limit of detection) and to increase the sampling cross-section of the stoppers' batches, multiple stoppers (four or ten) were combined as one composite sample based on the stopper size. See Figure 1. For example, a set of ten stoppers with an area of 5 [cm.sup.2] each, and a total area of 50 [cm.sup.2] extracted with 100 mL will have an assay limit concentration of 2.5 ppm C. Similarly, a swab used to !
cover an area of 25 [cm.sup.2], which is extracted with a 50 mL, volume will have an assay limit concentration of 2.5 ppm C (see Figure 2). It was also discovered that the sparging of PS20 solutions above 10 ppm resulted in inaccurate readings due to sample foaming resulting in sample loss. Therefore, method linearity was evaluated from 0.25 ppm to 5.00 ppm PS20, and the selected sample working range was from 0 to 5 ppm.
* Swab and Stopper Sample Preparation
Swab sampling took place using the following procedure: The fabric head of the swab was wetted with water (for swab spikes and FRP) or 0.012 N HC1 (for stainless steel); any excess liquid was removed by gently shaking the swab. A surface area of 25 [cm.sup.2] was swabbed, after which the swab stem was cut and each swab head was dropped into a glass bottle with a cap. Each swab sample was extracted with 50 mL of purified water by shaking for 10 minutes using a wrist action shaker. A 5 mL aliquot was immediately transferred into a sampling vial without transferring the swab head. Aliquot samples were then analyzed by TOC.
Stopper sets were extracted with 100 mL of purified water by shaking for 10 minutes using a wrist action shaker. Similarly, blank stoppers were spiked with purified water and extracted to generate blank samples. An aliquot of each extract was immediately transferred into a sampling vial. To minimize the effects of carbon leaching from the stoppers, the stoppers were not transferred with the testing aliquot. The aliquots were then assayed by TOC.
* Instrument Calibration and Controls
The TOC instrument was calibrated using a series of sucrose calibration standards, and the system was checked on a daily basis with the PBQ system suitability solution and a sucrose standard check covering a calibration range of 0.1 ppm to 50 ppm C. The instrument demonstrated a linear response to sucrose and PBQ, with correlation coefficients better than 0.995 for these compounds over this range.
RESULTS AND DISCUSSION
Method Development and Validation
* TOC Analysis
TOC analysis is a non-specific method theoretically capable of quantitation of the carbon content of any aqueous sample. The TOC-5000 instrument measures carbon through oxidation of organic carbon to carbon dioxide (C[O.sub.2]), which is subsequently detected by a C[O.sub.2]-selective detector in an effluent stream. The instrument is designed to measure TOC directly as "non-purgable organic carbon" after total inorganic carbon (carbonates and dissolved carbon dioxide) is purged from the sample matrix prior to analysis by helium sparging. Because TOC analysis is a non-specific analytical technique and measures the total carbon from all compounds in a sample, sample stability will not be an issue unless microbial contamination occurs before sample analysis.
* Linearity
Polysorbate 20 linearity was evaluated by analyzing five levels of PS20 (1.00, 1.75, 2.50, 3.75, and 5.00 ppm) in triplicate. Purified water served as the blank and diluent. The working range covered 40% to 200% of the target level of 2.5 ppm (as indicated in the section labeled, "Establishment of the TOC Assay Range," under the 'Method' heading). The percent carbon load for PS20 is 56.7% (see Figure 3 for calculations). The instrument demonstrated a linear response to PS20 and the fitted curve displayed a coefficient of determination of 0.9955 (see Figure 4). The slope value of 0.5164 compared favorably with the theoretical carbon fraction of 0.567 for PS20. Recoveries calculated from measured TOC vs. theoretical ranged from 80-100% for this data set (see Figure 5).
[FIGURE 4 OMITTED]
* Accuracy and Precision
Aqueous PS20 stock solutions were prepared at levels of 1000 and 5000 ppm. Surfaces were spiked with purified water for surface blanks, and with PS20 stock solutions corresponding to levels of 50, 125, and 250 [micro]g per swab (resulting in 40%, 100%, and 200% of the target concentration in the extract). A set of swabs was also directly spiked with aliquots of PS20 stock solutions at the same levels. The 125 [micro]g/swab recovery was determined separately by two analysts for the evaluation of intermediate precision. The surfaces were spiked with aliquots of stock solutions and were allowed to air-dry completely prior to swabbing. Six replicates were prepared at each level. To examine the efficiency of the swabbing procedure, a second moist swab was also collected to test for the presence of residues not removed by the first swab. No significant amount of PS20 was found on the second swabs under these conditions (data not shown).
Sets of ten stoppers were used for the 5 [cm.sup.2] stopper sizes (5 [cm.sup.2] x 10 = 50 [cm.sup.2] total area) and stopper sets of four stoppers were used for the 13 [cm.sup.2] sizes (13 [cm.sup.2] x 4 = 52 [cm.sup.2] total area), as indicated in the area calculations of Figure 2. Stoppers sets (n=10) were spiked with a 500 ppm PS20 stock solution to achieve final PS20 concentrations of 10, 25, and 50 [micro]g per stopper (5 [cm.sup.2]), equivalent to 2, 5, and 10 [micro]g /[cm.sup.2]. Stopper sets (n=4) were spiked with a 500 ppm stock solutions of PS20 for a final PS20 concentration of 25, 62.5, and 125 [micro]g per stopper (13 [cm.sup.2]), equivalent to approximately 2, 5, and 10 [micro]g /[cm.sup.2] at the target level. The 62.5 [micro]g/stopper recovery was determined separately by two analysts for the evaluation of intermediate precision. Each stopper was directly spiked with aliquots of 500 ppm PS20 stock solution and the liquid was allowed to evaporate completely!
prior to extraction. Six replicate sets of spiked stoppers were prepared at each level.
Accuracy was determined via the calculation of recoveries across the range studied for each surface. The swabs directly spiked with PS20 demonstrated recoveries ranging from 65-75% across levels (see Figure 6). Swab recoveries from surfaces ranged from a low of 56.6% for fiberglass-reinforced polyester surfaces spiked at the low level to a high of 78.1% for stainless steel surfaces spiked at the high level (see Figures 7 and 8). Accuracy was also evaluated through the calculation of individual stopper recoveries across levels (see Figure 9). Recoveries ranged from a low of 64.1% to a high of 112%. The precision for spiked swabs was calculated using the six replicates prepared at each level, and ranged from 8.0% to 10.8% across all levels. The precision for the swabs taken from the stainless steel and fiberglass-reinforced polyester surfaces ranged from 4.4% to 14.5%. The precision of the recoveries of PS20 from the various stopper materials ranged from 3.5% to 19.4% RSD.
Assay precision repeatability was determined for recoveries from surfaces by preparing a set of six replicate samples by two analysts for each surface and for Stopper 1. Intermediate precision was demonstrated by comparing the data from each analyst for swab spike recovery performed at 125 [micro]g/swab; the pooled RSD (n=12) obtained was 8.9% with an average recovery of 64%. Similarly, the intermediate precision was evaluated for stopper spike recoveries for each analyst at 62.5 [micro]g/stopper; the pooled RSD obtained was 13% with an average recovery of 95%.
* Limit of Detection and Limit of Quantitation
Limit of detection (DL) and limit of quantitation (QL) for the Shimadzu instrument were calculated using six low level replicates of PS20 solution at the 1.75-ppm level with the following equations, where S is the slope of the calibration curve:
DL = Std. conc. x [%RSD/33%] = 3[delta]/S
QL = Std. conc. x [%RSD/10%] = 10[delta]/S
See Figure 10 for the results of this determination. Based on these results, the limit of detection for the Shimadzu instrument was set at 2.5 ppm of PS20.
Optimization of Stopper Extraction
Carbon contamination from stopper handling, packaging components, leaching of organics, and stopper batch/lot variability were anticipated to contribute significantly to the TOC signal, and therefore, a background correction was implemented.
In order to obtain a uniform background control for each stopper type, a cleaning procedure with 0.01% (w/w) PS20 was designed. A set of 100 5 [cm.sup.2] stoppers was cleaned by soaking in the 0.01% (w/w) PS20 solution at 80[degrees]C for 15 minutes, and then rinsed with at least 1 liter of purified water to ensure that no residual PS20 or particulates were present. The cleaned blank stoppers were air dried, and stored for later use in a sealed glass container. Sets of uncleaned stoppers that were spiked with PS20 had replicate preparation variability from 17% to 57% RSD, whereas clean stoppers that were spiked in a similar manner had an RSD that ranged below 10% for replicate preparations. These results suggested that the uncleaned stoppers contained varying levels of organic contaminants that were removed through the cleaning process.
The stoppers were extracted by placing them in an appropriate container and accurately adding 100 mL of purified water. The sample size consisted of ten stoppers for the 5 [cm.sup.2] stoppers and four for the 13 [cm.sup.2] stoppers. The sample was then shaken with a mechanical wrist shaker for 10 minutes, after which an aliquot was immediately removed for testing.
In order to establish extraction time for sample preparation, stoppers were soaked in the extraction solution for a period of time that would represent a practical length of time required by the analyst to perform the preparation steps. TOC responses indicated that stoppers can be in extraction solution for up to 60 minutes with no noticeable background increase due to leaching of organic constituents from the stoppers (Figure 11). The variability observed between measurements across the hold times fell within the expected precision of the TOC responses for the low levels of carbon (below the quantitation limit) in these samples.
Following the cleaning, a study was done to determine the volume and duration of rinsing needed to remove PS20 from the stoppers. The stoppers were washed with the 0.01% PS20 solution and rinsed four times in fresh volumes of 200 mL of purified water for 10 minutes. An aliquot was taken from each rinse and assayed for TOC. A final water sample was collected after stoppers were soaked in the rinse for 24 hours to evaluate for leaching of organics from the stoppers. Figure 12 presents the levels of PS20 plotted against stages of rinsing. The first 200 mL rinse removed most of the cleaning agent added; the highest level of carbon detected was 1.75 ppm C versus the approximate 50 ppm C originally present in the 0.01% PS20. The TOC values for the water rinses stabilized after subsequent 200 mL rinses at an average response of 0.5 ppm C, corresponding to the background measurement for clean stoppers.
Soaking the stoppers in water for an extended time of 24 hrs was also evaluated, and the TOC response within the stoppers was observed to increase up to 1.45 ppm C (Figure 12). This increase was likely due to stopper leaching.
CONCLUSION
Laboratory procedures for the extraction and determination of the residual cleaning agent PS20 on swabs and vial stoppers by TOC analysis were developed and validated. These procedures were designed to provide an assay range that contained the acceptance limit of 5 [micro]g of PS20 per [cm.sup.2] surface area (equivalent to a prepared sample concentration of 2.5 ppm) for both stoppers and processing equipment surfaces. Surface recoveries for PS20 ranging from 56% to 92% were obtained for stoppers, stainless steel, and FRP. The response of the TOC instrument for PS20 was determined to be linear over the range of 1-5 ppm, with limits of detection and quantitation corresponding to 0.7 and 2.2 ppm, respectively, based on signal-to-noise estimation.
ACKNOWLEDGEMENT
The authors wish to acknowledge Dr. Ed Tidswell for supplying stoppers and the FRP wash tub and for his contributions to the establishment of the surface acceptance limits for PS20.
[FIGURE 12 OMITTED]
REFERENCES
1. FDA. Current Good Manufacturing Practices for Finished Pharmaceuticals.
2. FDA. Guide to Inspections of Validation of Cleaning Processes. The Food and Drug Administration. www.fda.gov/ora/inspectref/igs/valid.html.
3. FDA. Guide to Inspections of Bulk Pharmaceutical Chemicals. The Food and Drug Administration. www.fda.gov/ora/inspectref/igs/bulk.html.
4. BioPharm May 2002 Info #50 Cleaning Validation
5. FDA. Cleaning Procedures and Protocols in Focus.
6. Amer, G. and Deshmane, P. "Ensuring Successful Validation: The Logical Steps to Efficient Cleaning Procedures." BioPharm Vol. 14, No. 3. 2001. pp. 26-32.
7. Baffi, R., Dolch, G., Garnick, R., Huang, Y., Mar, B., Matsuhiro, D., Niepelt, B, Parra, C., and Stephan, M. "A Total Organic Carbon Analysis Method for Validating Cleaning Between Products in Biopharmaceutical Manufacturing." J. Parent. Sci. Technol. Vol. 45, No. 1, 1991, pp. 9-13.
8. Strege, M., Stinger, T., Farrell, B., and Lagu, A. "Total Organic Carbon Analysis of Swab Samples for the Cleaning Validation of Bioprocess Fermentation Equipment." BioPharm Vol. 9, No. 4, 1996, pp. 25-42.
9. Wallace, B., Stevens, R., and Purcell, M. "Implementing Total Organic Carbon Analysis for Cleaning Validation." Pharm. Tech. Aseptic Processing, May 2004, pp. 40-44.
ABOUT THE AUTHORS
Nieves Juarbe is an Assistant Senior Analytical Chemist and member of the Manufacturing Science and Technology Analytical Sciences laboratory at Eli Lilly and Company. She has an MS degree in Chemistry from the University of Georgia at Athens.
Mark Strege is corresponding author for this article; he is a Senior Research Scientist and a team leader within the Manufacturing Science and Technology Analytical Sciences laboratory at Eli Lilly and Company. Mark has an MS degree in Analytical Chemistry from Purdue University. He can be reached by email at strege_mark_a@lilly.com or by telephone at (317) 276-9116.
Article Acronym Listing
<pre>
C[O.sub.2] Carbon Dioxide
DL Limit of Detection
FDA Food and Drug Administration
FRP Fiberglass Reinforced Polyester
GMP Good Manufacturing Practice
ICH International Conference on Harmonization
PBQ 1, 4-Benzoquinone
PS20 Polysorbate 20
QL Limit of Quantitation
REF Recovery Efficiency Fraction
RSD Relative Standard Deviation
TIC Total Inorganic Carbon
TOC Total Organic Carbon

Figure 1 Stoppers and Surfaces

Sample Size
Vendor (stoppers or
Item (item code) Description swabs)

Stopper 1 West Pharma, Butyl / 13.16 [cm.sup.2] 4
ws-450
Stopper 2 West Pharma, Butyl / 5.48 [cm.sup.2] 10
ws-491
Stopper 3 Hospira, Halobutyl / 4.55 [cm.sup.2] 10
88-1839
Stopper 4 West Pharma, Halobutyl / 4.58 [cm.sup.2] 10
ws-808
Stopper 5 Hospira, Halobutyl / 4.55 [cm.sup.2] 10
88-1856
Stopper 6 West Pharma, Halobutyl / 5.48 [cm.sup.2] 10
ws-375
Stainless Steel N/A 5x5 cm coupons created 1
in-house
Fiberglass- N/A washing tub 1
Reinforced
Polyester
(FRP)

Figure 2 Surface and Stopper Area Calculations

Description Extraction
Material Estimated Surface Area Volume

Swab from 25 [cm.sup.2] 50 mL
Stainless
Steel Surface
Swab from FRP 25 [cm.sup.2] 50 mL
Surface
Stopper 1 13 [cm.sup.2] x 4 stoppers = 52 [cm.sup.2] 100 mL
Stopper 2 5 [cm.sup.2] x 10 stoppers = 50 [cm.sup.2] 100 mL
Stopper 3 5 [cm.sup.2] x 10 stoppers = 50 [cm.sup.2] 100 mL
Stopper 4 5 [cm.sup.2] x 10 stoppers = 50 [cm.sup.2] 100 mL
Stopper 5 5 [cm.sup.2] x 10 stoppers = 50 [cm.sup.2] 100 mL
Stopper 6 5 [cm.sup.2] x 10 stoppers = 50 [cm.sup.2] 100 mL

Figure 3 Conversion Calculations

Carbon load calculation for Polysorbate 20 FW = 1228
Chemical formula: [C.sub.58] [H.sub.114] [O.sub.26]
% Carbon load = (58 x 12/1228) x 100% = 56.7%

Figure 5 Polysorbate 20 Linearity and Recovery

TOC
PS20 Actual Prep Average Response Theoretical
Conc Conc TOC Blank PS20 as
(ppm) (ppm) Response Adjusted Carbon % Recovery

Blank Diluent 0 0.323 0 0
1.000 1.009 0.777 0.453 0.567 80
1.750 1.816 1.236 0.913 1.017 90
2.500 2.422 1.478 1.1547 1.356 85
3.750 4.036 2.385 2.062 2.260 91
5.000 5.033 3.009 2.686 2.819 95

Key for Results:
1. TOC response blank adjusted = result (ppm C) - mean blank signal
(ppm C)
2. Calculated ppm C PS20 = (corrected ppb C)/(0.567)

Figure 6 Spiked Swab Recoveries

Target PS 20 Spike Actual PS 20 Spike Mean % Recovery
Level (mcg/swab) Level (mcg/swab) (n=6) % RSD

50 50 71.3 8.6
125 126 66.3 8.0
125 126 62.5 9.5
250 252 74.1 10.8

Figure 7 Stainless Steel Surface Recoveries

Target PS 20 Spike Actual PS 20 Spike Mean % Recovery
Level (mcg/swab) Level (mcg/swab) (n=6) % RSD

50 54 56.7 6.3
125 135 66.1 6.7
250 271 78.1 7.9

Figure 8 Fiberglass-Reinforced Polyester Surface Recoveries

Target PS 20 Spike Actual PS 20 Spike Mean % Recovery
Level (mcg/swab) Level (mcg/swab) (n=6) % RSD

50 54 56.6 9.3
125 135 60.2 4.4
250 271 60.6 14.5

Figure 9 Spiked Stopper Recoveries

Target PS 20 Spike Actual PS 20 Spike Mean % Recovery
Level (mcg/swab) Level (mcg/swab) (n=6) % RSD

Stopper 1
25.0 27 97.2 12.5
62.5 68 101.8 6.1
62.5 63 89.0 9.8
125.0 135 97.5 16.1
Stopper 2
10 10 64.1 19.4
25 25 66.3 6.8
50 50 67.8 4.9
Stopper 3
10 10 84.7 8.8
25 25 80.0 3.5
50 50 73.6 9.8
Stopper 4
10 11 112.1 8.9
25 27 107.1 7.3
50 54 91.8 15.8
Stopper 5
10 10 100.0 16.5
25 25 86.4 4.6
50 50 78.4 4.6
Stopper 6
10 10 82.4 7.7
25 25 72.3 7.2
50 50 72.4 10.5

Figure 10 Average Limit of Detection (DL) and Limit of Quantitation (QL)

PS20 DL and QL Estimates

DL 3 x sigma/slope 0.372 ppm C 0.66 ppm PS20
QL 10 x sigma/slope 1.242 ppm C 2.21 ppm PS20

Figure 11 Stopper Extraction plus Holding Time

TOC Response, ppm C

ITEM + 0 min. hold + 30 min. hold 60 min. hold

Stopper 1, n=2 0.4 0.3 0.4
Stopper 2, n=2 0.5 0.4 0.5
Stopper 3, n=2 0.8 0.7 0.7
Stopper 4, n=2 0.3 0.5 0.4
Stopper 5, n=2 0.8 0.7 0.9
Stopper 6, n=2 0.4 0.4 0.4
Control Water 0.3 0.2 0.3 </pre>

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Validation of API manufacturing operations

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Journal of Validation Technology , 02/01/2007 13 2
Validation of API manufacturing operations: impact of Q7A.(Active Pharmaceutical Ingredients) Fuge, Juanita *~|~*
COPYRIGHT 2007 Advanstar Communications, Inc.

During the annual Validation Week event (October 2006) hosted by the Institute of Validation Technology, Max S. Lazar, President of FDA Regulatory Compliance Consulting and an active, contributing member of the JVT Editorial Advisory Board, discussed the impact of the Q7A Guidance on the validation of API manufacturing operations from his perspective as a topic leader of the Expert Working Group (EWG) that developed and negotiated that guidance. As an attendee at that Validation Week discussion, it is my pleasure to share the highlights of Max's unique perspective and to include here, as an important addition to your library, the full text of the Q7A Guidance. INTRODUCTION
Although in theory, validation of Active Pharmaceutical Ingredients (APIs) may be the same as validation for dosage forms, in actual application they are not the same. The differences arise from the differences that exist between APIs and dosage forms in practicality. That is in their complexity, sheer size, robustness, and chemical or biological design. The difference lies in how and when to do the validation; that it must be done remains.
From the introduction section of the Q7A document to its final chapter, validation is noted more than 70 times in the guidance. Validation is noted in the following sections of the guideline:
<pre>
Q7A Guidance Sections

Analytical Methods
API for Use in Clinical Trials
Blending
Change Control
Computerized Systems
Containment
Documentation and Records
Introduction and Glossary
Laboratory Controls
Process and Cleaning Validation
Process Equipment/Cleaning
Product Quality Review
Production Activities
Production/In-process Controls
Purified Water
Quality Management
Stability Monitoring
Viral Removal </pre>
Validation, according to the Food and Drug Administration's (FDA) "Guideline on General Principles of Process Validation" (May 1987), includes:
<pre>
"Establishing documented evidence which provides a high degree of
assurance that a specific process will consistently produce a
product meeting its pre-determined specifications and quality
attributes." </pre>
We will look at the most significant words in this definition to clarify and expand upon their meanings. The first significant word, documented, implies protocols and records and means these must be completed, available, and be the documents upon which the validation is based. The next word, evidence, requires that good science and extensive sampling be used. The use of the word, consistently, implies multiple batches produced by the same process, or more specifically, one process producing batches of similar quality. The final important word used in the definition is pre-determined. Pre-determined implies both a knowledge of the API to be validated and requires that the knowledge be applied to the process before the validation is actuated. In other words, the validation should be completed to prove a pre-determined result.
Therefore, process validation is not an/a:
** Experiment
** Optimization Study
** Process Improvement Program
** Process Capability Study
** "Worst-case" Test
Process validation is a means of confirming in an orderly and scientific way, what we already believe is true. We are trying to meet the "pre-determined quality specifications and attributes" mentioned in FDA's definition.
VALIDATION AND API'S
Why the concern with API validation? We look to control variables that are tested at three levels: high, medium, and low.
Where:
N = [3.sup.X]
N = Total number of experiments
X = Number of control variables
How many experiments may be needed?
If the number of control variables (X) equals 4, then N = 34 or 81 experiments.* API processes are far more complex than this so that the actual number of runs would be extremely large.
*Note: This is an impractical number of experiments and API manufacturers cannot and should not be expected to perform such a large number of validation runs. To make these experiments feasible, API manufacturers must use a fraction of this number when performing validations.
Difference between GMP and Q7A Expectations
There is a distinct difference between what is expected regarding validation of APIs under Q7A Guidance and from the Drug Product GMP.
*** Drug Product GMP Expectations:
** All Steps/Controls
** Analytical Methods
** GMP Computerized Systems
** Purified Water Systems
** All Cleaning Procedures
** All changes that can impact quality
** Do not accept retrospective validatiaon
*** Q7A Expectations:
** Only critical steps/processes
** Specifies that the annual Product Review should be used to determine whether re-validation is needed for API processes
** Specifies that GMP-related computerized systems should be validated
** Allows retrospective validation when proper documentation exists
** Q7A specifies more details about validation than does 21CFR 211
**** Documentation retention system of validation documents (Reports should exist.)
**** For critical physical attributes, validation of blending is expected to ensure homogeneity (these must be defended)
**** Validation of analytical procedures that are NOT compendial
**** Validation policy, including:
***** Intentions
***** Approach
***** Cleaning procedures
***** Analytical procedures
***** Computerized systems
***** Persons responsible for all phases from design to approval and documentation
**** Validation should extend to ... operations ... critical to ... quality and purity of the API
**** Validation protocol
**** Details validation process
**** Validation report
**** Documentation of variation from protocol
**** Appropriate qualification BEFORE validation
**** Accepts (under defined conditions)
***** Prospective validation (norm)
***** Concurrent validation
***** Retrospective validation
****** Critical attributes/parameters identified
****** In-process controls/criteria established
****** No significant process/process failures unless due to human or mechanical causes
****** Impurity profiles established
****** Defines conditions for use of this type of validation
** Establishes Guidance for number of lots to use for validation
**** Prospective -- minimum 3 lots or batches
**** Concurrent -- minimum 3, if possible
**** Retrospective -- 10 to 30 lots or batches
** Periodic review of validation
**** Does NOT mandate automatic re-validation
** Cleaning procedures normally validated, but not always required
**** Is there a risk to API Quality?
**** Analytical checking advised
**** Cleaning limits based upon Pharmacological or Toxicological data
**** Micro and Endotoxin testing where appropriate
** Analytical procedures validated unless from official compendia such as USP/NF
** Impact of change on need for validation should be determined
** Concurrent validation acceptable for reworked API
** Process validation NOT normally expected for API under development
Compliance Expectations for API Validation
The Q7A Guidance was written with intended flexibility so that it could apply in many situations. Regulators throughout the world are expected to use it with this built-in flexibility. Practitioners, understanding this flexibility, must recognize the intent of the writers and use Q7A according to its application in their circumstances.
Process Validation under Q7A
Here are important items to remember when considering process validation under the Q7A guidelines. Remember that the terms qualification and validation are not synonymous; qualification is the testing and review of a piece of equipment, refer above to the FDA's definition of validation. Q7A allows concurrent validation. Changes under retrospective validation are accepted when there is no impact on the quality of the API. Finally, process validation is not required during API development. For API under development, to be used in clinical trials, no validation is required.
CONCLUSION
Basic validation is the same for drug products and APIs. There are numerous differences identified in Q7A; greater detail is provided in the Q7A Guidance than in 21 CFR PART 211 Drug Product GMP. Flexibility is identified for API's under development and in concurrent and retrospective validations. It is most important to understand the intent of the Expert Work Group that wrote and negotiated the International Guidance.
PRESENTER CONTACT INFORMATION: Max S. Lazar, President, FDA Regulatory Compliance Consulting, Surprise, AZ, 85374 USA maxslazar@aol.com 623-556-0556. Member of the ICH Q7A EWG (EWG PhRMA Topic Leader) that developed and negotiated the Q7A Guidance.
Article Acronym Listing
<pre>
API Active Pharmaceutical Ingredient
EWG Expert Working Group
FDA Food and Drug Administration
GMP Good Manufacturing Practice
ICH International Conference on Harmonization
NF National Formulary
USP United States Pharmacopoeia </pre>
VALIDATION WEEK '06 PRESENTATION BY: MAX S. LAZAR
COMPILED BY: JUANITA FUGE, EDITOR

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