PEER-R EV IEW ED Cleaning Validation: Factors Affecting Recovery Data and Material of Construction Grouping Richard J. Forsyth ABSTRACT Material of construction is a factor in recovery of residue for cleaning validation. Analysis of existing recovery data demonstrated that recovery factors for drug products on different materials of construction could be categorized into several groupings. The groupings based on the recovery data were not aligned with the material composition (e.g., metal, plastic, glass, etc.). An examination of additional factors clarified the grouping of materials versus recovery data. Materials of construction used in laboratory studies to represent commercial manufacturing equipment must be representative of equipment. Materials of construction that exhibit low recovery should be replaced wherever practical for an alternative material with a higher recovery to avoid any potential cross-contamination due to slow release of residue from the material of construction. If problematic materials cannot be released, equipment should be dedicated or restricted for use to the active pharmaceutical ingredient with low recovery. INTRODUCTION Residue assays are a critical requirement in establishing a validated cleaning program. They are essential to accurately determine amounts of residual active pharmaceutical ingredient (API) remaining on equipment after cleaning. This determination is then compared to the acceptable residue limit (ARL) for a given process or equipment train (1). For more Author information, go to gxpandjvt.com/bios The residue assay methods are typically validated for the following parameters: • Linearity • Precision • Sensitivity • Specificity • Recovery. From an analytical standpoint, recovery is from the cleaning test sample, usually from a swab. For the cleaning program, the concern is the recovery of the residue from the manufacturing equipment (1, 2). Recoveries are determined through experiments in which sample equipment materials spiked with known amounts of the substance of interest are swabbed and tested. The swab and the swabbing solvent must be capable of recovering a sufficient amount of material to allow an accurate and precise measurement of the spiked component. The most important aspects for product recovery factors are that the data are consistent, reproducible, and provide an adjusted ARL that is above the limit of quantitation of the analytical method. The ARL must be achievable and practical. If recoveries are too low, either the methods need to be optimized or the manufacturing equipment must be dedicated or restricted for manufacturing only the specific API. A recent study (3) gathered and statistically analyzed all available historical data and achieved the following: • Grouped materials of construction according to recov- [ gxpandjv t.com ABOUT THE AUTHOR Richard Forsyth is a pharmaceutical consultant with a background in cleaning validation and analytical chemistry. He may be reached by e-mail at [email protected]. Journal of Validation T echnology [Autumn 2009] 91 PEER-R EV IEW ED ery performance. This resulted in five distinct groupings with statistically different recovery levels. These groupings, however, could not be correlated to material properties. For example, different types of plastics were noted in all five groups. Most metals, including stainless steel, were categorized into the two groups with the highest recovery levels; however, aluminum was in the second lowest recovery group. • Selected representative materials from each grouping for potential testing if appropriate. The end result of the analysis was a reduction in the number of studies required for new substances in a cleaning validation program. The analysis concluded that a recovery study conducted at one site using stainless steel would serve as a representative material of construction for most materials used in drug product manufacturing, and is applicable across multiple sites. The study was not able to identify the physical characteristics of the materials and parameters that influence recovery data results. There was no obvious correlation between the recovery data and the similarity in composition (e.g., metals, plastics, glass) of the materials of construction. Different metals, rubbers, and plastics occupied different groups across the range of residue recoveries. Because the data set was generated at numerous sites worldwide over several years, it was not practical to assemble representative samples of all of the materials of construction. The following are a number of additional parameters that could affect the recovery of residue from equipment surfaces (4): • Residue solubility • Swab material • Solvent type • Recovery technique by sampling technician • Residue cleanability (5), which in turn may be related to its solubility. These parameters are interrelated. The cleanability of the residue impacts the choice of cleaning procedure; the harder a residue is to clean, the higher the anticipated amount of residue to be swabbed. The amount of anticipated residue affects the choice of swab and solvent as well as the validation of the analytical testing method. The materials used to recover the residue also affect recovery. The swab material must be able to absorb sufficient residue and solvent to remove the residue from the equipment material surface. The type and amount of recovery solvent must dissolve the residue sufficiently for removal without leaving residue or solvent behind. The swabbing technique should be standardized and 92 Journal of Validation T echnology [Autumn 2009] adequately controlled to minimize subjectivity and should consistently recover enough residue so that a precise measurement is assured. The combination of swab material and recovery solvent should not interfere with the subsequent sample assay. Although the composition of the materials of construction provided no correlation with the recovery data, the physical properties of the materials could affect recoveries. There have been studies that have examined surface roughness and how it affects the ability to clean surfaces (6). The hardness of the individual materials might also help explain certain residue recoveries. The porosity of certain materials could account for several of the low recovery data sets. The objective of this study was to gather historical data, generate necessary additional data, and statistically analyze the data relating to these parameters. The end result of this analysis identified the physical characteristics of the materials of construction and parameters that influence recovery data results. An understanding of the relationship between the recovery data and the materials of construction was achieved. EXPERIMENTAL The solubility of the recovered materials was considered as a factor affecting swab recovery. The solubility of a number of APIs was tabulated and analyzed in comparison to the respective recovery data. The swab technique was also examined as a factor in recoveries. The swab techniques from the different sites were reviewed and the swab materials were examined for possible correlation to low recoveries. The recovery solvent and extraction procedure were examined for several low recovery APIs to determine if recoveries could be raised. The cleanability data for a number of APIs and formulations were tabulated, statistically analyzed, and compared to the recovery data. The gravimetric-based cleanability method consisted of placing a wet slurry consisting of a set amount of water and formulation and API onto a preweighed coupon (23 mm x 20 mm). The coupon was 316L SS foil. In a single run, five soiled coupons were made along with three control coupons, and were placed into a humidity-controlled box (RH = 30%) for a set amount of time (dirty hold time, usually 24 hrs). The coupons were then weighed and photographed and then placed into a modified cuvette holder. The coupons were then exposed to a cleaning cycle that usually consisted of three process steps including pre-rinse, detergent wash, and final rinse. The typical cycle consisted of a 10-second dip in 80°C USP water; a 10-second dip in 80°C clean-in-place (CIP) solution (0-3%), and a last 10iv thome.com R ICH A R D J. FORSY T H seceond dip in 80°C USP water. The coupons were then returned to the glove box for an additional 24 hours. After which, the coupons were weighed and photographed. The cleanability was then calculated based on weight. Recovery experiments were conducted with representative materials of construction that had provided both high and low recoveries. Earlier recovery data (3) defined groups of material of construction inclusive of variability due to individual compounds. Therefore, the groupings were independent of the compound recovered. For this study, two compounds were tested to provide adequate data points for each material of construction. Stainless steel and a smooth Neoprene rubber coupons not only represented the high and low recoveries (3), they also represented a hard and soft material, respectively. Stainless steel coupons machined to different roughness factors provided data. A Surtonic Duo surface finish analysis instrument (Taylor-Hobson, ID C-5524) was used to measure surface roughness of the coupons. Coupons with relatively smooth surfaces presented a uniform roughness. Rough surface coupons had grains resulting in different roughness measurements in perpendicular directions. In these cases, unidirectional swab samples attempted to discern recovery differences between the two roughness measurements. A rough Neoprene rubber and anodized aluminum coupons provided data to address porosity. Residue spots were prepared in triplicate and individual, single swabs taken for recovery. The swab samples were assayed with a validated high performance liquid chromatography (HPLC) method specific for the API and an average recovery factor was determined. Table I: Solubility and recovery data comparison. Compound Recovery Water solubility Clinoril 73 1000 Invanz 98 500 Singulair 90 240 Crixivan 76 100 Tryptanol 75 100 Prinivil 99 97 Fosamax 87 40 Fosamax Plus D3 75 40 Cpd D 82 25 Niacin 87 4.25 Sinemet 81 1 Pepcid 77 0.74 Compound C 83 0.722 Compound A 84 0.19 Moduretic 5/50 mg 87 0.1 Proscar/Propecia 91 0.1 Compound B 98 0.1 Decadron 89 0.1 Noroxin 86 0.091 Arcoxia 83 0.06 Compound E 91 0.03 Zocor 81 0.03 Stocrin 78 0.01 Mevacor 40 mg 81 0.004 RESULTS AND DISCUSSION Results are discussed for API aqueous solubility and recovery; recovery, aqueous solubility, and cleanability; material hardness; surface roughness; and porosity. API Aqueous Solubility and Recovery The initial analysis compared the previously determined recovery data (3) with the solubility data for the respective compounds (see Table I). Solubilities ranged from 1000 mg/mL to 0.004 mg/mL. Recoveries for the compounds examined ranged from 89% to 73%. There was no direct relationship between the water solubility of the compound and its respective recovery. In fact, the compound with the lowest recovery (73%) also had the highest solubility (1000 mg/ml). This was not unexpected for this data set. Although water is the first choice as a recovery solvent, if water solubility is low an alternate organic solvent (e.g., ethanol, methanol, acetonitrile) is employed. Part of the recovery assessment is to assure the compound has gxpandjv t.com adequate solubility in the chosen recovery solvent. The relatively high recovery data demonstrated that acceptable laboratory methods using appropriate recovery solvents had been developed. Depending on recovery data, recovery solvents may use combinations of polar, semipolar, and non-polar solvents. The recovery factors including swab technique, swab material, recovery solvent, and extraction procedure were examined as part of the earlier study (3). These four factors were combined and considered as the site-to-site variability for the recovery data. The additional variability among sites was not significant relative to the variability for repeated measurements due to differences in product and material of construction. Ninety-seven percent of the variability was attributable to different recovery factor (RF) means for each material and product, while only 3% additional variance was attributable to the swab, solvent, and technique factors across sites. This meant that Journal of Validation T echnology [Autumn 2009] 93 PEER-R EV IEW ED Table II: Cleanability and recovery data comparison. Cleanability Compound Recovery Water solubility Water CIP 100 Fosamax Plus D3 75 40 100 100 Mevacor 40 mg 81 0.004 99 100 Stocrin 78 <0.010 99 100 Compound E 91 <0.03 73 90 Arcoxia 83 0.06 68 96 78 Pepcid 77 0.74 61 69 91 Compound A 84 0.19 44 45 50 Zocor 81 <0.03 40 42 37 Table III: Recovery, solubility, and cleanability comparison in descending order. Recovery Water solubility Cleanability Compound E Fosamax Plus D3 Fosamax Plus D3 Compound A Pepcid Mevacor 40 mg Arcoxia Compound A Stocrin Mevacor 40 mg Arcoxia Compound E Zocor Compound E Arcoxia Stocrin Zocor Pepcid Pepcid Stocrin Compound A Fosamax Plus D3 Mevacor 40 mg Zocor across-site and within-site variability could be combined, and comparisons of materials and products across sites had essentially the same precision as comparisons made within a single site. This was a very useful finding, since it allowed RF results to be leveraged among different sites without accounting for site-to-site differences. Recovery, Aqueous Solubility, and Cleanability A similar analysis compared the recovery data with cleanability data for several of the compounds generated in both water and detergents in an independent study (see Table II). For this data set, the cleanability ranged from 100% to 37%. The respective recovery data ranged between 91% and 75%. Again there was no direct relationship drawn from the data. Although cleanability is a good indicator of the ability to clean a compound from manufacturing equipment, it does not necessarily indicate the ability to recover residue for testing. Table II data demonstrates general consistency in rank order cleanability for the three cleaning liquids (water, CIP 100, CIP 300). This may be expected because all cleaning liquids were 94 Journal of Validation T echnology [Autumn 2009] CIP 300 aqueous and differed only in proprietary formulation. CIP 100 is an alkaline cleaning liquid; CIP 300 is a neutral phosphate-free cleaning liquid. Table III more clearly demonstrates the lack of correlation among the data. Recovery, water solubility, and cleanability are listed in descending rank order for the eight compounds with data in all three categories. There is no correlation among the data and there is no obvious relation between the solubility and cleanability data, which might be reasonably expected. The only conclusion is that there is no discernable connection or trend among the data. An analysis of the HPLC recovery data led to a number of conclusions. An initial comparison in Table IV of the recovery data to the previously determined recovery data (3) demonstrated similar recovery data for all materials except the Neoprene samples. The Neoprene samples for this study had been sourced from a different vendor than the samples for the original (3) work. The Neoprene in the original work was not designated as smooth or rough. This demonstrates the importance of performing recoveries on the same material as used in manufacturing whenever possible. Material Hardness Comparison of the percentage of recovery data for stainless steel and smooth Neoprene in Table IV indicates that the hardness or softness of the material had no impact on recovery. The average recoveries from the mill finish stainless steel and the smooth neoprene were equivalent. Surface Roughness Table V provides recovery data from different surface roughness materials. Data from stainless steel were equivalent across the entire roughness range tested. The smoothest coupons (0.01 µm) were mirror finish stainless and the 0.83 µm were mill finish or 316 finish stainless steel. The rougher stainless steel finishes (1.1 – 4.5 µm) were specifiiv thome.com R ICH A R D J. FORSY T H cally machined for these experiments. The glass, brass, polytetrafluoroethylene (PTFE), and smooth Neoprene, which were comparatively smooth, had recovery numbers in the same range as the stainless steel. The rubber with a 4.94 µm roughness also demonstrated equivalent recovery data. Recoveries from the rough Neoprene were much lower, indicating that surface roughness is a factor in the ability to recover residue from equipment surfaces. However, recoveries from the aluminum sample were also low even though the roughness was comparable to stainless steel and rubber. This indicated that another factor was the cause of the low recoveries. Porosity The rough Neoprene was also very porous and this physical characteristic certainly contributed to the low recoveries. The spotted residue clearly entered the pores of the material as soon as it was spotted. A background check of the aluminum sample revealed that it was anodized aluminum, which is also a porous material (7, 8). Anodized aluminum can have pore diameters from 10–500 nm and with different layer thicknesses. Other materials demonstrating lowest recoveries were plastics containing methacrylate or butadiene-acrylonitrile (3). RF for these materials ranged from 31-44. Understanding the recovery factors for cleaning validation of elastomers (rubbers) and plastics, both uncrosslinked and crosslinked, may be complex. Material contamination during the manufacturing process and during the cleaning process are affected by the transport properties for the pairing of the particular compound and material of construction being considered, including the time of contact between the compound and material of construction, and the time of recovery used for the cleaning validation. The transport properties include permeability, the diffusion coefficient, and the solubility coefficient of the compound into the material of construction. The permeability is essentially the product of the diffusion coefficient and the solubility coefficient, and these three properties are temperature dependent. A higher diffusion coefficient indicates that a compound will diffuse further into the material of construction, and a higher solubility coefficient means that more compound can equilibrate within the material of construction at a given concentration of exposure. Another factor that can influence the recovery is the solvent chosen for the cleaning validation, as the solvent can affect the transport properties of the material of construction. If the material of construction has a high affinity for the solvent, the material could swell and the compound under test could further diffuse into the material along with some of the cleaning solvent, thereby reducing the recovery. gxpandjv t.com Table IV: Material % recovery. Material Average % recovery Average % recovery reference 3 Stainless steel 81.8 83.8 Glass 81.1 85.5 Brass 80.9 80.6 PTFE 85.5 83.9 Neoprene (smooth) 79.4 31-44 Aluminum #7 55.3 53-56 Rubber #5 88.6 81.9 Neoprene (rough) 11.7 31-44 Table V: HPLC recovery data. Material Surface roughness (µm) Amount spotted (µg) Average % recovery Stainless steel 0.01 100 86.6 Stainless steel 0.4 100 77.6 Stainless steel 0.83 100 83.4 Stainless steel 1.1 100 83.7 Stainless steel 1.3 100 79.2 Stainless steel 3.7 100 84.1 Stainless steel 4.5 100 78.3 Glass 0.03 100 81.1 Brass 0.16 100 80.9 PTFE 1.11 100 85.5 Neoprene (smooth) 1.57 100 79.4 Aluminum #7 2.3 100 56.4 Rubber #5 4.94 100 88.6 Aluminum #7 5.34 100 54.1 Neoprene (rough) 12.8 100 13.5 Neoprene (rough) 18.9 100 9.9 Transport of compounds through materials generally occurs more rapidly in elastomers such as Neoprene, EDPM, latex, or silicone. Material transport is relatively less in glassy thermoplastics such as Lexan. The degree of crystallinity, the degree of crosslinking, and the proportion of fillers will also affect the transport properties. The longer period of time a material is exposed to a compound, the further into the material the compound will diffuse, thereby making full recovery of the compound more difficult for a fixed cleaning period of time. Glassy polymers with glass transition temperatures above room temperature tend to allow materials to diffuse more slowly Journal of Validation T echnology [Autumn 2009] 95 PEER-R EV IEW ED than rubbery polymers with glass transition temperatures below room temperature. However, rubbery polymers are usually crosslinked and filled, which tends to decrease diffusion rates within the given rubbery material. Overall, transport properties are very specific. Complex interactions dependent upon the solvent, material of construction, and the compound under test cannot be generalized in a manner that will allow prediction of recovery during cleaning validation tests. Explanation of the relative performance of one compound against another for a given material of construction or the relative performance of one material of construction against another for a given compound cannot be predicted. In order to better understand particular outcomes, specific measurements of fundamental transport properties for the solvents, compounds, and materials of construction would be necessary. These measurements are unnecessary for the established materials of construction for which average recoveries have been determined, regardless of the compound recovered and the solvent employed (3). If a new material of construction is introduced, an alternative to the specific measurements above is to conduct recovery studies with one to three different API and experimentally determine into which recovery group the new material of construction falls. CONCLUSIONS Material of construction is a factor in recovery of residue for cleaning validation. More specifically, the ability of the residue to permeate into the surface of the material lowers recovery. Although the solubility of the residue in the recovery solvent, the ability of the swab to recover the residue, and the sampling technician swab technique also contribute to recovery data, these factors have been standardized to demonstrate recoveries of >75% for many materials of construction. The use of new materials of construction for pharmaceutical manufacturing should be evaluated on an individual basis to determine the ability to recover pharmaceutical residue from its surface. Materials of construction coupons used in laboratory studies to determine recovery data must be exact replicas of materials used to fabricate equipment. The data of this paper demonstrated that all Neoprene was not the same—there were significant recovery differences between “smooth” and “rough” Neoprene. High surface roughness materials as exemplified by rough Neoprene had the lowest % recovery data. Materials of construction that exhibit low recovery should be replaced wherever practical. Replacement materials should be evaluated to ensure a higher recovery of the API of interest to avoid 96 Journal of Validation T echnology [Autumn 2009] any potential cross-contamination due to slow release of residue from the material of construction. If replacement is not possible, equipment should be dedicated or restricted for use to the API that had low recovery. REFERENCES 1.FDA, Guide to Inspection of Validation of Cleaning Processes, Division of Field Investigations, Office of Regional Operations, Office of Regulatory Affairs, Washington, D.C. July 1993. 2.R. J. Forsyth and D. Haynes, “Cleaning Validation in a Pharmaceutical Research Facility,” Pharm. Technol. 22 (9), 104 – 112, 1998. 3.R. J. Forsyth, J. C. O’Neill, and Jeffrey L. Hartman, “Cleaning Validation: Grouping Materials of Construction Based on Recovery Data,” Pharm. Technol., 31 (9), 104 – 112, 2007). 4.G. M. Chudzik, “General Guide to Recovery Studies Using Swab Sampling Methods for Cleaning Validation,” J. Val. Technol., 5 (1), 77 – 81, 1999. 5.R. Sharnez, J. Lathia, et al., “In Situ Monitoring of Soil Dissolution Dynamics: A Rapid and Simple Method for Determining Worst-case Soils for Cleaning Validation,” PDA J Pharm. Sci. and Technol, 58 (4), Jul-Aug 2004. 6.F. Riedewald, “Bacterial Adhesion to Surfaces: the Influence of Surface Roughness,” PDA J Pharm. Sci. and Technol, 60 (3) 164 – 171, May-June 2006. 7. V. Sokol, I. Vrublevsky, et al., “Investigation of Mechanical Properties of anodized Aluminum using Dilatometric Measurements,” Anal. Bioanal. Chem. 375 968 – 973, March 2003. 8.E. S. Koolj, H. Wormeester, et al., “Optical Anistropy and Porosity of Anodic Aluminum Oxide Characterized by Spectroscopic Ellipsometry,” Electrochem.Solid-State Lett. 6 (11) B52 – B54, 2003. JVT ARTICLE ACRONYM LISTING API Active Pharmaceutical Ingredient ARL Acceptable Residue Limit CIPClean-in-Place HPLC High Performance Liquid Chromatography RF Recovery Factor USP United States Pharmacopeia iv thome.com
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