Monitoring dissolved ozone in the pharmaceutical industry

October 1, 2008
Michael Strahand

Pharmaceutical Technology Europe

Pharmaceutical Technology Europe, Pharmaceutical Technology Europe-10-01-2008, Volume 20, Issue 10

Emerging technologies now enable continuous on-line monitoring and control of ozone systems, providing precise and reliable results, revolutionizing the way dissolved ozone is measured.

Ozone is commonly used in the pharmaceutical industry for disinfecting pharmaceutical-grade water, which is present in process systems, such as washers, autoclaves or secondary water purification systems, and used to clean delicate pharmaceutical manufacturing equipment. High-purity pharmaceutical-grade water followed by distillation forms the base ingredient in the manufacture of ingestible and injectable medical products. According to US Pharmacopoeia (USP) regulations, pharmaceutical-grade water must be validated to demonstrate that it meets certain requirements for ionic and organic chemical purity, and must also be protected from microbial contamination.1

Ozone is used for microbial disinfection purposes during the sanitization of pharmaceutical-grade water production to disinfect the water network prior to distillation. It is essential that the water is disinfected effectively during this process to ensure the highest quality water and to avoid increased costs during the distillation process. In creating such high-quality water, it is essential to measure the levels of dissolved ozone at various points in the process to ensure that adequate ozone concentrations are present during sanitization and that there is no residual ozone at the point of use.

Ozone monitoring

Ozone is the strongest stand-alone oxidizer currently available for water treatment. One of its largest uses is in the production of pharmaceutical-grade water, where it is dissolved in the water and reacted with bacteria, viruses and other microorganisms to create removable solids of dissolved minerals and to neutralize certain chemicals. During the pharmaceutical manufacturing process, ozone is used to treat pharmaceutical-grade water and water for injection (WFI) to ensure that the water distribution network is sanitary/cleaned. As the ozone-injected water is flushed through the distribution system, disinfection is extremely effective when compared with conventional steam cleaning solutions.

Ozone can also break down pesticides, kill microorganisms and remove unwanted colour, leaving behind no taste, odour and, most importantly, no dangerous chemical residues. Ozone also has a very high oxidation potential and is exceptionally quick-working, enabling pharmaceutical manufacturers to significantly reduce downtime and increase productivity.

Dissolved ozone has traditionally been monitored and controlled using redox analyzers, ultraviolet (UV) spectrophotometers, amperometric or potentiometric electrochemical monitors, colorimeters and sensors that measure the photochemical reaction of ozone with ethylene. However, these instruments can demonstrate significant shortcomings: redox analysers are nonlinear and not sensitive enough to accommodate certain applications, and UV spectrophotometers are expensive and complicated to use, requiring a reference gas, moving parts in the form of solenoid valves and also incorporate optics that may become easily misaligned. Additionally, the UV spectrum of ozone may be confused with that of other compounds present in the water sample being monitored.

The use of amperometric or potentiometric electrochemical monitors can be problematic when monitoring ozone as the instruments are not ozone-specific, produce a very small signal in low-conductivity water and are not efficient in ultra-pure water. Such sensors have proved unreliable and inaccurate as electrodes and membranes are easily fouled, internal solutions may become contaminated and maintenance requires complex disassembly.

An alternative technique, the use of colorimeters, does not offer continuous sample analysis and requires the disposal of contaminated samples. The photochemical approach is also becoming less common because of the need for a continuous supply of reagents and the ability to handle exhaust products.

Alternative technologies

To overcome common issues with colorimetric monitoring techniques, an alternative technology has been developed that enables continuous on-line monitoring and control of ozone systems. This technology, shown in Figure 1, has been designed and proven to meet a variety of monitoring applications, and is capable of measuring dissolved ozone concentrations as low as 0–200 ppb full scale down to 0.5 ppb. While providing the sensitivity needed for demanding applications, such as pharmaceutical-grade water or semiconductor wash water, this technique can also accommodate high-range applications that require 0–20 or 0–200 ppm.

Figure 1

Unlike on-line colorimetric and most amperometric methods, this innovative technology uses a highly selective, membrane-covered polarographic sensor that does not require the addition of chemical reagents. Dissolved ozone readings are easily achieved without measurement interference from other sample components such as residual chlorine. The need for maintenance is also greatly reduced as the technology does not require the use of moving parts, meaning there are no tubing breaks or pumps and motors that burn out. The technology has been designed with the flexibility to enable optional dual measurement capability, and provides both dissolved ozone and pH analogue outputs. Dual analogue outputs can also be configured to track ozone and temperature, ozone and ozone, or ozone and pH for increased process control.

Dissolved ozone sensors incorporating this technique are generally installed in a flowcell, with sample piped to the flowcell using 6.35-mm inner diameter sample tubing. The standard flowcell arrangement uses a constant-head overflow system to ensure stable flow and pressure across the sensor, regardless of sample line fluctuations. A low-volume flowcell is used for installations where minimum sample flow is desired, and sample flow and pressure can be carefully controlled.

On the go...

A standard feature of this alternative technology is a proportional-integral-derivative (PID) control function, which can be configured quickly and easily. To use this function, the primary 4–20 mA output must be assigned for PID control. While not suitable for systems with rapid flow changes requiring compound-loop control, the PID function can handle many stable flow applications.

Calibration accuracy

Pharmaceutical companies require efficient calibration systems capable of meeting the strict regulatory requirements specified by the European Pharmacopoeia (Eur. Ph.)2 and the USP, which regulate the quality of purified water and WFI in the manufacture of pharmaceutical products. Additionally, the Eur. Ph. requires that water monitoring systems be regularly calibrated against one or more suitable certified standard solutions. For example, for conductivity monitoring, calibration should achieve accuracy within 3% of the measured conductivity.

Implementation of a reliable and accurate calibration procedure for ozone monitors is of utmost importance to ensure the precision of data derived from the instrument. Following the initial installation of the monitoring system, the calibration of ozone monitors should be checked at least monthly. While verifying calibration accuracy, the instrument should also be examined to determine whether parts need to be replaced and that the general operation is of an acceptable level.

Preparing an analytical standard of ozone with which to calibrate the instrument is not possible because of the instability of aqueous ozone solutions. The most practical and recognized means of calibrating the instrument is the indigo dye method. This is the only recognized calibration standard for ozone analysis by the US Environmental Protection Agency3 and the International Ozone Association.4 Importantly, the indigo dye method is also the only traceable method of calibration. Other convenient calibration methods (e.g., air calibration using relative diffusion coefficients of oxygen and ozone) need to be cross-referenced with the traceable indigo dye method.

This method is referred to as 'bleaching chemistry' because the colour developed on the ozone sample is lighter (or 'bleached') than a reagent blank run on ozone-free water. As ozone reacts quantitatively with the blue indigo dye, the colour of the solution fades. Colour intensity is then measured with a photometer (either a colorimeter or a spectrophotometer) to determine the amount of ozone present.

The indigo dye method is sensitive, precise, fast and simple. However, the masking of chlorine in the presence of ozone can render the method problematic and ineffective. Furthermore, in the presence of hypobromous acid, which forms during ozonation of bromide-ion containing methods, an accurate measurement cannot be achieved. Chlorine and bromide are not present in pharmaceutical-grade water so these problems are not an issue.

Instruments incorporating a membrane-covered polarographic sensor technology, such as the ATi Q45H/64 dissolved ozone monitor (Analytical Technology Inc., UK), can achieve high levels of calibration accuracy. To maximize the accuracy of the calibration, it is recommended that a dissolved ozone concentration of at least 100, and preferably 200 ppb, is used when calibrating ozone monitors, to minimize the effects of small chemical interferences and round-off error that usually occur at lower ozone concentrations. Additionally, calibration should be done when the ozone concentration in the water is steady. Membraned ozone monitoring technology uses a sensor with a linear response, meaning that a two-point calibration, zero and span, is all that is required to calibrate the monitor. By taking at least three samples and using averages, it is possible to calibrate a sensor to ±5 ppb at a concentration of 100 ppb. The linear response of the sensor means that this accuracy at 100 ppb will give accuracies better than 1 ppb at low (<10 ppb) concentrations.

When a dissolved ozone monitor is used for detecting ozone following UV destruction, it can be argued that the accuracy of the calibration is not as important as the stability of the zero. The aim, in this case, is to ensure that UV has removed the ozone. Even an error in calibration as big as 20% will apply to all values subsequently measured with the sensor provided that the zero is stable. This means that for a monitor calibrated at 200 ppb with an error of 40 ppb, the error at 10 ppb would still only be 4 ppb. Calibration accuracies of better than 5% are actually achievable. It is important at low ppb values that the monitor maintains a stable zero point. The new technology demonstrates an intrinsically zero stability better than ±1 ppb per year.

Conclusion

With regulations becoming increasingly stricter regarding ionic and organic chemical purity, as well as microbial decontamination of pharmaceutical-grade water, there is a strong need for reliable water quality monitoring technologies in the pharmaceutical industry. Traditional dissolved ozone monitoring methods lack sensitivity and can be expensive, complicated to use and inefficient. Emerging technologies now enable continuous on-line monitoring and control of ozone systems, providing precise and reliable results, revolutionizing the way dissolved ozone is measured. The new technologies also overcome the limitations of conventional calibration methods, while providing important traceability. Maintaining a stable zero point, these innovative methods achieve the highest levels of calibration accuracy, ensuring reliable and accurate results in this highly regulated industry.

Michael Strahand is General Manager Europe of Analytical Technology Inc. (UK).

References

1. United States Pharmacopoeia 23. www.usp.org

2. European Pharmacopoeia. www.pheurorg

3. US Environmental Protection Agency. www.epa.gov

4. International Ozone Association. www.io3a.org