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Bakgrund: För att bibehålla ett liv med en hög livskvalité är det viktigt att ha en tillräcklig muskelstyrka för att klara av vardagen och minska skador. Styrketräning kan utveckla skelettmuskulaturen och anses vara ett populärt träningssätt. Användningen av icke-steroida antiinflammatoriska läkemedel (NSAID) har ökat inom idrotten. Forskningsläget var sparsamt bland den yngre befolkningen, men mer forskning fanns inom området på den äldre befolkningen. Dock saknades forskning kring påverkan av olika doser under en längre användningsperiod. Syfte: Litteraturöversiktens syfte var att granska användandet av preparaten (NSAID) och tydliggöra vilken effekt dessa hade på styrkeutveckling, skelettmuskeltillväxt och signaler i skelettmuskulaturen i samband med styrketräning. Metod: Den systematiska litteraturöversikten skapades med publikationer från databaserna Pubmed och SPORT Discus där 86 studier identifierades. För att kunna besvara frågeställningen resulterade det i nio studier totalt. De valda studiernas validitet bedömdes och samtliga var av god kvalité. Resultat: Äldre runt 65 år undersöktes i fem av nio studier då alla förutom en inte påvisade någon skillnad i skelettmuskulaturen medan en påvisade en signifikant positiv effekt i muskelmassa vid intag av icke-steroida antiinflammatoriska läkemedel i jämförelse med placebo. De resterande fyra studierna var gjorda på yngre individer runt 25 år och spretade åt olika håll. Där de visade på att ingen skillnad fanns i att det blev en minskad styrkeutveckling och skelettmuskeltillväxt och att det hämmar signaler men att individerna även orkar utföra ett större arbete med läkemedlen. Slutsats: För yngre individer visade preparaten ha en hämmande effekt på muskeltillväxten men för äldre individer verkade inte muskeltillväxten påverkas. / Background: To maintain a life with a high quality of life, it is important to have sufficient muscle strength to cope with everyday life and reduce injuries. Strength training can develop skeletal muscle and is considered a popular exercise method. The use of non-steroidal anti-inflammatory drugs (NSAIDs) has increased in sports. The research situation was sparse among the younger population, but more research was found in the field of the older population. However, there was no research on the effect of different doses over a longer period of use. Purpose: The purpose of the literature review was to examine the use of the preparations (NSAIDs) and to clarify their effect on strength development, skeletal muscle growth and signals in the skeletal muscle in connection with strength training. Method: The systematic literature review was created with publications from the Pubmed and SPORT Discus databases, where 86 studies were identified. In order to answer the question, it resulted in nine studies in total. The validity of the selected studies was assessed, and all were of good quality. Results: Elderly people around the age of 65 were examined in five of nine studies, all except one showing no difference in skeletal muscle, while one showed a significant positive effect in muscle mass when taking non-steroidal anti-inflammatory drugs compared to placebo. The remaining four studies were done on younger individuals around 25 years of age and spread in different directions. Where they showed that there was no difference in the fact that there was a decrease in strength development and skeletal muscle growth and that it inhibited signals but that the individuals also can do a greater work on the drugs. Conclusion: For younger individuals, the preparations were shown to have an inhibitory effect on muscle growth, but for older individuals, muscle growth did not appear to be affected.

The research addressed in this thesis focuses on monitoring and characterization of pharmaceutical compounds by laser backscattering. In particular, this study covers two topics: (1) the determination of naproxen sodium solubility in water, and its phase transition; and (2) comparisons of batch and laminar flow tubular crystallizers for the production of paracetamol (acetaminophen) and D-mannitol. Using a Lasentec™ Focused Beam Reflectance Measurement (FBRM) device, the solubility of naproxen sodium in aqueous solutions was determined over a temperature range from 15.2 to 39.7 ℃ With the determination of the solubilities of two pseudopolymorphs, anhydrous and dihydrated naproxen sodium, the phase transition point between these two forms of the pharmaceutical compound was determined to occur at 30.3 ℃ Enthalpy of solution and metastable zone widths were also determined for the experimental conditions. Crystallizations of paracetamol and D-mannitol were performed in a batch crystallizer and in a laminar flow tubular crystallizer (LFTC) system. In the latter system, supersaturation was generated rapidly in the solution being transported through a temperature-controlled tube and recovered in a batch vessel where product crystals were grown to equilibration. Because of the rapid rate at which supersaturation was generated in the LFTC, the resulting crystals were of smaller mean size than those obtained from batch crystallizations. The total time required for crystallization was significantly less with the LFTC than with the batch unit. Additionally, the rapid cooling in the LFTC led to the formation of two different polymorphs of paracetamol, Forms I and II.

NSAIDs are among the most used drugs in the world. It is estimated that 30 million people take NSAIDs daily world-wide, without including drugs sold over the counter. They are effective in alleviating pain and inflammation. Even though they are very common there does not appear to be any clear-cut guidelines to when which NSAID should be used. It has therefore been the purpose of this thesis to analyze if there is a need to differentiate between different NSAIDs according to contemporary evidence. Since the withdrawal of rofecoxib in 2004 there has been a general idea that coxibs as a group are cardiotoxic, recent evidence suggests that this holds true for all NSAIDs however. As such this work included 5 drugs, three common over the counter non-selective NSAIDs; naproxen, ibuprofen and diclofenac as well as the two coxibs currently on the Swedish market; celecoxib and etoricoxib. Pubmed and google scholar were searched for relevant studies on the subject. The results showed that there is a need to differentiate between NSAIDs, however the clinical setting is complex and a one-size fits all solution is difficult to come by. Naproxen and moderate doses of celecoxib (100 mg b.i.d.) show the best cardiovascular profiles whilst etoricoxib, celecoxib and diclofenac show the best gastrointestinal profiles. Coxibs show similar upper GI-profiles as tNSAIDs if combined with PPI however PPI are not without adverse events and the lower GI is not affected by PPI. Longer half-life is in general the better option in situations with lasting pain since it has been shown that lower dosing intervals increase adherence. In terms of pain management there does not appear to be any differences in efficacy amongst different NSAIDs

Pharmaceuticals are group of organic substances with significant worldwide consumption in human and veterinary medicine. These compounds may be metabolized in the organism, but in some cases they remain unchanged and both are usually excreted via renal excretion in the native form or as metabolites. Large quantities of pharmaceuticals and their metabolites contaminate municipal wastewater. The wastewater treatment plants are unable to remove these substances completely, so they contaminate surface water, groundwater and soil as well. Due to the biological activity of pharmaceuticals, long - term effect may cause bacterial resistance, endocrine influence, DNA and renal damages in non-target organisms. The phytoextraction and the translocation of radiolabeled diclofenac with 125 I were experimentally studied by using of in vitro cultivated plants Helianthus annuus and Zea mays. Efficiency od phytoextraction was monitored as decrease of radioactivity of tested substance [125 I]diclofenac in Murashige-Skoog cultivation medium. Both species are able to extract tested substance during 8 to 10 days of cultivation, with efficiency approximately 85 % using Zea mays and 79 % using Helianthus annuus. Better extraction ability of diclofenac was observed at Helianthus annuus - 80 mg/ kg of dry weight compared...

A bench-scale study of the degradation of four selected pharmaceuticals and personal care products (PPCPs) was carried out using UV and UV/H₂O₂ treatment employing low pressure (LP) and medium pressure (MP) lamps. The target substances included the pharmaceutical compounds ibuprofen, naproxen, and gemfibrozil, along with the bactericide triclosan. There were four main objectives of the study, as follows: to evaluate the removal of the target compounds using UV irradiation alone and UV/H₂O₂, to determine the reaction kinetics for direct and indirect photolysis of each selected compound, to determine the influence of major water quality parameters on the efficacy of treatment, and to compare the applied UV and UV/H₂O₂ doses to those that have been found to be effective for disinfection and removal of taste and odour compounds, respectively. For initial ultra-pure water experiments the target compounds were spiked at concentrations of approximately 250 µg/L (~1 µM). In latter ultra-pure water experiments and in the partially-treated water experiments, the selected PPCPs were spiked at a lower range (c~500-1000 ng/L), which is more representative of reported environmental concentrations. In an ultra-pure water matrix, a high LP fluence of 1000 mJ/cm² caused only triclosan to substantially degrade. Furthermore, with LP-UV/H₂O₂ only triclosan and naproxen had average percent removals above 60% at a typical disinfection fluence of 40 mJ/cm² with 100 mg/L H₂O₂. Complete degradation of all four compounds in ultra-pure water was achieved with very high fluences (compared to those used for UV disinfection) with MP-UV alone (at or above 1000 mJ/cm²) or with relatively high fluences for MP-UV/H₂O₂ (200-300 mJ/cm²) with 10 mg/L H₂O₂. Overall, when compared at similar applied fluences, the MP lamp was much more effective than the LP lamp. Furthermore, the addition of H₂O₂ typically increased removal rates, in some cases substantially, through formation and subsequent reaction of the PPCP with the •OH radical. When target substances were treated all together in an ultra-pure water solution, removals were lower than when they were treated independently at the same individual concentrations (~250 µg/L) this may simply have been the result of a higher total contaminant concentration in solution, which lessened the availability of the •OH radical and incident UV irradiation for degradation of all compounds. On the other hand, removals were improved when the combined target compounds were present at a lower individual concentration range (~750 ng/L), which suggests that removals may be concentration driven, with reduced matrix effects seen at lower overall contaminant concentrations. Furthermore, during the partially-treated water experiments, variability in treatment performance was observed with differing water quality; however, it was not evident which specific quality parameters influenced treatment effectiveness. On the other hand, substantial and sometimes complete, degradation of the target compounds was still seen in the partially-treated water with high MP-UV/H₂O₂ doses (e.g. 300 mJ/cm² + 10 mg/L H₂O₂ and 500 + 10 mg/L H₂O₂). For the kinetic experiments, compounds were spiked individually in ultra-pure water (c~250 µg/L = ~1µM). The photolysis of the target compounds during treatment was assumed to be a pseudo-first-order reaction. Kinetic parameters were determined for both direct and indirect photolysis for both lamps. The calculated rate constants confirmed the importance of •OH radicals for degradation of these compounds, especially for ibuprofen and gemfibrozil. For ibuprofen and gemfibrozil, direct photolysis rate constants could not be determined for LP-UV because very little degradation was seen at the fluences tested. LP-UV direct phototlysis rate constants for naproxen and triclosan were 0.0002 and 0.0033 cm²/mJ, respectively. Overall rate constants describing degradation of the four compounds due to LP-UV/H₂O₂ ranged from 0.0049 to 0.0124 cm²/mJ. All four compounds had fluence-based reaction rate constants for MP-UV indirect photolysis of approximately 0.01 cm²/mJ, while MP-UV direct photolysis rate constants ranged between 0.0007-0.007 cm²/mJ, with ibuprofen having the lowest and triclosan the highest. The overall trends were similar to those seen by other researchers for the removal of taste and odour compounds. For example, fluences required for substantial removal were much higher than typical disinfection doses, the MP lamp was more effective than the LP lamp (when compared solely on a fluence-basis), and the addition of H₂O₂ improved removals. On the whole, UV/H₂O₂ appears to be a very promising technology for the removal of these selected PPCPs during drinking water treatment, and is likely to be equally effective for other, similar contaminants.

A bench-scale study of the degradation of four selected pharmaceuticals and personal care products (PPCPs) was carried out using UV and UV/H₂O₂ treatment employing low pressure (LP) and medium pressure (MP) lamps. The target substances included the pharmaceutical compounds ibuprofen, naproxen, and gemfibrozil, along with the bactericide triclosan. There were four main objectives of the study, as follows: to evaluate the removal of the target compounds using UV irradiation alone and UV/H₂O₂, to determine the reaction kinetics for direct and indirect photolysis of each selected compound, to determine the influence of major water quality parameters on the efficacy of treatment, and to compare the applied UV and UV/H₂O₂ doses to those that have been found to be effective for disinfection and removal of taste and odour compounds, respectively. For initial ultra-pure water experiments the target compounds were spiked at concentrations of approximately 250 µg/L (~1 µM). In latter ultra-pure water experiments and in the partially-treated water experiments, the selected PPCPs were spiked at a lower range (c~500-1000 ng/L), which is more representative of reported environmental concentrations. In an ultra-pure water matrix, a high LP fluence of 1000 mJ/cm² caused only triclosan to substantially degrade. Furthermore, with LP-UV/H₂O₂ only triclosan and naproxen had average percent removals above 60% at a typical disinfection fluence of 40 mJ/cm² with 100 mg/L H₂O₂. Complete degradation of all four compounds in ultra-pure water was achieved with very high fluences (compared to those used for UV disinfection) with MP-UV alone (at or above 1000 mJ/cm²) or with relatively high fluences for MP-UV/H₂O₂ (200-300 mJ/cm²) with 10 mg/L H₂O₂. Overall, when compared at similar applied fluences, the MP lamp was much more effective than the LP lamp. Furthermore, the addition of H₂O₂ typically increased removal rates, in some cases substantially, through formation and subsequent reaction of the PPCP with the •OH radical. When target substances were treated all together in an ultra-pure water solution, removals were lower than when they were treated independently at the same individual concentrations (~250 µg/L) this may simply have been the result of a higher total contaminant concentration in solution, which lessened the availability of the •OH radical and incident UV irradiation for degradation of all compounds. On the other hand, removals were improved when the combined target compounds were present at a lower individual concentration range (~750 ng/L), which suggests that removals may be concentration driven, with reduced matrix effects seen at lower overall contaminant concentrations. Furthermore, during the partially-treated water experiments, variability in treatment performance was observed with differing water quality; however, it was not evident which specific quality parameters influenced treatment effectiveness. On the other hand, substantial and sometimes complete, degradation of the target compounds was still seen in the partially-treated water with high MP-UV/H₂O₂ doses (e.g. 300 mJ/cm² + 10 mg/L H₂O₂ and 500 + 10 mg/L H₂O₂). For the kinetic experiments, compounds were spiked individually in ultra-pure water (c~250 µg/L = ~1µM). The photolysis of the target compounds during treatment was assumed to be a pseudo-first-order reaction. Kinetic parameters were determined for both direct and indirect photolysis for both lamps. The calculated rate constants confirmed the importance of •OH radicals for degradation of these compounds, especially for ibuprofen and gemfibrozil. For ibuprofen and gemfibrozil, direct photolysis rate constants could not be determined for LP-UV because very little degradation was seen at the fluences tested. LP-UV direct phototlysis rate constants for naproxen and triclosan were 0.0002 and 0.0033 cm²/mJ, respectively. Overall rate constants describing degradation of the four compounds due to LP-UV/H₂O₂ ranged from 0.0049 to 0.0124 cm²/mJ. All four compounds had fluence-based reaction rate constants for MP-UV indirect photolysis of approximately 0.01 cm²/mJ, while MP-UV direct photolysis rate constants ranged between 0.0007-0.007 cm²/mJ, with ibuprofen having the lowest and triclosan the highest. The overall trends were similar to those seen by other researchers for the removal of taste and odour compounds. For example, fluences required for substantial removal were much higher than typical disinfection doses, the MP lamp was more effective than the LP lamp (when compared solely on a fluence-basis), and the addition of H₂O₂ improved removals. On the whole, UV/H₂O₂ appears to be a very promising technology for the removal of these selected PPCPs during drinking water treatment, and is likely to be equally effective for other, similar contaminants.

A bench-scale study of the degradation of four selected pharmaceuticals and personal care products (PPCPs) was carried out using UV and UV/H₂O₂ treatment employing low pressure (LP) and medium pressure (MP) lamps. The target substances included the pharmaceutical compounds ibuprofen, naproxen, and gemfibrozil, along with the bactericide triclosan. There were four main objectives of the study, as follows: to evaluate the removal of the target compounds using UV irradiation alone and UV/H₂O₂, to determine the reaction kinetics for direct and indirect photolysis of each selected compound, to determine the influence of major water quality parameters on the efficacy of treatment, and to compare the applied UV and UV/H₂O₂ doses to those that have been found to be effective for disinfection and removal of taste and odour compounds, respectively. For initial ultra-pure water experiments the target compounds were spiked at concentrations of approximately 250 µg/L (~1 µM). In latter ultra-pure water experiments and in the partially-treated water experiments, the selected PPCPs were spiked at a lower range (c~500-1000 ng/L), which is more representative of reported environmental concentrations. In an ultra-pure water matrix, a high LP fluence of 1000 mJ/cm² caused only triclosan to substantially degrade. Furthermore, with LP-UV/H₂O₂ only triclosan and naproxen had average percent removals above 60% at a typical disinfection fluence of 40 mJ/cm² with 100 mg/L H₂O₂. Complete degradation of all four compounds in ultra-pure water was achieved with very high fluences (compared to those used for UV disinfection) with MP-UV alone (at or above 1000 mJ/cm²) or with relatively high fluences for MP-UV/H₂O₂ (200-300 mJ/cm²) with 10 mg/L H₂O₂. Overall, when compared at similar applied fluences, the MP lamp was much more effective than the LP lamp. Furthermore, the addition of H₂O₂ typically increased removal rates, in some cases substantially, through formation and subsequent reaction of the PPCP with the •OH radical. When target substances were treated all together in an ultra-pure water solution, removals were lower than when they were treated independently at the same individual concentrations (~250 µg/L) this may simply have been the result of a higher total contaminant concentration in solution, which lessened the availability of the •OH radical and incident UV irradiation for degradation of all compounds. On the other hand, removals were improved when the combined target compounds were present at a lower individual concentration range (~750 ng/L), which suggests that removals may be concentration driven, with reduced matrix effects seen at lower overall contaminant concentrations. Furthermore, during the partially-treated water experiments, variability in treatment performance was observed with differing water quality; however, it was not evident which specific quality parameters influenced treatment effectiveness. On the other hand, substantial and sometimes complete, degradation of the target compounds was still seen in the partially-treated water with high MP-UV/H₂O₂ doses (e.g. 300 mJ/cm² + 10 mg/L H₂O₂ and 500 + 10 mg/L H₂O₂). For the kinetic experiments, compounds were spiked individually in ultra-pure water (c~250 µg/L = ~1µM). The photolysis of the target compounds during treatment was assumed to be a pseudo-first-order reaction. Kinetic parameters were determined for both direct and indirect photolysis for both lamps. The calculated rate constants confirmed the importance of •OH radicals for degradation of these compounds, especially for ibuprofen and gemfibrozil. For ibuprofen and gemfibrozil, direct photolysis rate constants could not be determined for LP-UV because very little degradation was seen at the fluences tested. LP-UV direct phototlysis rate constants for naproxen and triclosan were 0.0002 and 0.0033 cm²/mJ, respectively. Overall rate constants describing degradation of the four compounds due to LP-UV/H₂O₂ ranged from 0.0049 to 0.0124 cm²/mJ. All four compounds had fluence-based reaction rate constants for MP-UV indirect photolysis of approximately 0.01 cm²/mJ, while MP-UV direct photolysis rate constants ranged between 0.0007-0.007 cm²/mJ, with ibuprofen having the lowest and triclosan the highest. The overall trends were similar to those seen by other researchers for the removal of taste and odour compounds. For example, fluences required for substantial removal were much higher than typical disinfection doses, the MP lamp was more effective than the LP lamp (when compared solely on a fluence-basis), and the addition of H₂O₂ improved removals. On the whole, UV/H₂O₂ appears to be a very promising technology for the removal of these selected PPCPs during drinking water treatment, and is likely to be equally effective for other, similar contaminants.

A bench-scale study of the degradation of four selected pharmaceuticals and personal care products (PPCPs) was carried out using UV and UV/H₂O₂ treatment employing low pressure (LP) and medium pressure (MP) lamps. The target substances included the pharmaceutical compounds ibuprofen, naproxen, and gemfibrozil, along with the bactericide triclosan. There were four main objectives of the study, as follows: to evaluate the removal of the target compounds using UV irradiation alone and UV/H₂O₂, to determine the reaction kinetics for direct and indirect photolysis of each selected compound, to determine the influence of major water quality parameters on the efficacy of treatment, and to compare the applied UV and UV/H₂O₂ doses to those that have been found to be effective for disinfection and removal of taste and odour compounds, respectively. For initial ultra-pure water experiments the target compounds were spiked at concentrations of approximately 250 µg/L (~1 µM). In latter ultra-pure water experiments and in the partially-treated water experiments, the selected PPCPs were spiked at a lower range (c~500-1000 ng/L), which is more representative of reported environmental concentrations. In an ultra-pure water matrix, a high LP fluence of 1000 mJ/cm² caused only triclosan to substantially degrade. Furthermore, with LP-UV/H₂O₂ only triclosan and naproxen had average percent removals above 60% at a typical disinfection fluence of 40 mJ/cm² with 100 mg/L H₂O₂. Complete degradation of all four compounds in ultra-pure water was achieved with very high fluences (compared to those used for UV disinfection) with MP-UV alone (at or above 1000 mJ/cm²) or with relatively high fluences for MP-UV/H₂O₂ (200-300 mJ/cm²) with 10 mg/L H₂O₂. Overall, when compared at similar applied fluences, the MP lamp was much more effective than the LP lamp. Furthermore, the addition of H₂O₂ typically increased removal rates, in some cases substantially, through formation and subsequent reaction of the PPCP with the •OH radical. When target substances were treated all together in an ultra-pure water solution, removals were lower than when they were treated independently at the same individual concentrations (~250 µg/L) this may simply have been the result of a higher total contaminant concentration in solution, which lessened the availability of the •OH radical and incident UV irradiation for degradation of all compounds. On the other hand, removals were improved when the combined target compounds were present at a lower individual concentration range (~750 ng/L), which suggests that removals may be concentration driven, with reduced matrix effects seen at lower overall contaminant concentrations. Furthermore, during the partially-treated water experiments, variability in treatment performance was observed with differing water quality; however, it was not evident which specific quality parameters influenced treatment effectiveness. On the other hand, substantial and sometimes complete, degradation of the target compounds was still seen in the partially-treated water with high MP-UV/H₂O₂ doses (e.g. 300 mJ/cm² + 10 mg/L H₂O₂ and 500 + 10 mg/L H₂O₂). For the kinetic experiments, compounds were spiked individually in ultra-pure water (c~250 µg/L = ~1µM). The photolysis of the target compounds during treatment was assumed to be a pseudo-first-order reaction. Kinetic parameters were determined for both direct and indirect photolysis for both lamps. The calculated rate constants confirmed the importance of •OH radicals for degradation of these compounds, especially for ibuprofen and gemfibrozil. For ibuprofen and gemfibrozil, direct photolysis rate constants could not be determined for LP-UV because very little degradation was seen at the fluences tested. LP-UV direct phototlysis rate constants for naproxen and triclosan were 0.0002 and 0.0033 cm²/mJ, respectively. Overall rate constants describing degradation of the four compounds due to LP-UV/H₂O₂ ranged from 0.0049 to 0.0124 cm²/mJ. All four compounds had fluence-based reaction rate constants for MP-UV indirect photolysis of approximately 0.01 cm²/mJ, while MP-UV direct photolysis rate constants ranged between 0.0007-0.007 cm²/mJ, with ibuprofen having the lowest and triclosan the highest. The overall trends were similar to those seen by other researchers for the removal of taste and odour compounds. For example, fluences required for substantial removal were much higher than typical disinfection doses, the MP lamp was more effective than the LP lamp (when compared solely on a fluence-basis), and the addition of H₂O₂ improved removals. On the whole, UV/H₂O₂ appears to be a very promising technology for the removal of these selected PPCPs during drinking water treatment, and is likely to be equally effective for other, similar contaminants.

The motivation for the present study is systematically presented and the aims and objectives of the study are clearly defined. A comprehensive review on modified release drug delivery has been presented to provide the basis for the meltable aqueous dispersion technique as an approach to the formulation of a multiple-unit oral modified release drug delivery system. In addition, a brief discussion on the theory of dissolution testing and the mechanisms and interpretation of the dissolution process has been presented. Naproxen sodium, a potent non-steroidal anti-inflammatory drug (NSAID) with analgesic and antipyretic activity employed in the study, has been briefly discussed. In the present study, the coacervation phase separation technique utilizing ethylcellulose was initially investigated but proved unsuccessful in producing a formulation displaying suitable drug release characteristics. Subsequently, the meltable aqueous dispersion technique utilizing cetostearyl alcohol was successfully employed to formulate a multipleunit modified release naproxen sodium preparation containing 550 mg of naproxen sodium. The use of cetosteary!alcohol, as·a·retarding material, generated modified ·drug release characteristics as a function of its content. Magnesium stearate (anti-tackiness agent) and Span 20 and Tween 60· (surfactants) were incorporated in the formulation to optimize particle size and sphericity. The influence. of various formulation variables on drug release characteristics were investigated: An optimized formulation displaying a desirable modified release profile of naproxen sodium was achieved employing a 1:1 ratio of naproxen sodium:cetostearyl alcohol, 2% m/m .. .. magnesium stearate, and 1%m/m Span 20 dispersed in a liquid manufacturing vehicle of pH 0.6 containing 2% m/m Tween 60. In vitro dissolution studies on the selected formulation showed drug release to be predictable and reproducible, dependent on the dissolution method, agitation rate, and the pH of the dissolution media (i.e. pH-dependent drug release). The density of the microspheres was shown to decrease as the concentration of cetostearyl alcohol increased whilst the mean specific surface area increased with increasing concentrations of cetostearyl alcohol. Differential scanning calorimetric studies reveals a change in the thermograms which is suggestive of eutectic formation. Scanning electron microscopy proved useful in evaluating the integrity and surface morphology of the microspheres as well as in elucidating the drug release characteristics of the formulation. Energy dispersive x-ray microprobe analysis revealed the elemental composition of the microspheres to be a composite of the pure ingredients. X-ray mapping and the line scan depicted the homogenous distribution of drug within the microspheres and confirmed that the formulation is a matrix-type modified release I' preparation. Stability studies were performed on the selected formulation at room temperature (21 :t 1°C), 40°C, 37°C with 80% relative humidity, and at low temperature (5 :t 1°C). The shelf-life of the selected formulation was determined to be 1.29 years. Applying the data to five different kinetic models to investigate the drug release mechanisms showed that first order and cube-root release characteristics were exhibited by the microspheres. / Thesis (M.Sc.)--University of Durban-Westville, 1997.