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Optimal operation for selecting conductivity function analysis of pharmaceutical water using Sievers M9 total organic carbon TOC analyzer
Date: 2025-09-18Read: 43


This article provides information on how to use Sievers with conductivity options configured®The optimal operation guide for M9 TOC analyzer to simultaneously detect TOC and conductivity of pharmaceutical water.






sampling




The key to effectively detecting pharmaceutical water using an M9 analyzer with conductivity options includes:

  1. Adopting the correct sampling technique

  2. Dual Use Conductivity and TOC Sample Bottles


According to USP<645>, 'Stage 1 conductivity can be tested offline in a suitable container'.1A suitable container for synchronous testing refers to a container that does not affect the TOC or conductivity of the sample when in contact with it. Tests have shown that, with the use of correct sampling techniques, the Sievers DUCT bottle body, cap, and gasket can withstand up to 5 days,It will not make a significant contribution to the TOC and conductivity of the sample.2,3


The cleanliness of Sievers DUCT sample bottles is good, with a certified TOC of less than 10 ppb, so there is no need to rinse before use. The best sampling procedures include:

  1. Do not rinse the DUCT sample bottle before use.

  2. To avoid contamination, do not touch the inside of the DUCT sample bottle and bottle cap with your hands, and do not touch the gasket of the sample bottle.

  3. Fill the DUCT sample bottle at once, leaving no space at the top of the bottle to prevent turbulence in the sample.

  4. After sampling, immediately seal the bottle cap.

  5. Do not reuse DUCT sample bottles to prepare samples.






Method and conditions for using equipment




When using M9 analyzer to analyze pharmaceutical water, the samples should be tested multiple times to obtain good statistical robustness and detection stability. When using M9 analyzer to detect TOC and conductivity, it is recommended to repeat the detection no less than 4 times, and one of the detections should be discarded. The original conductivity and temperature are used to detect the conductivity in the first stage, so there is no need to choose a compensation algorithm. The M9 analyzer provides the original conductivity, temperature, and temperature compensation values. For pharmaceutical water, the original conductivity and temperature should be reported. The acceptance criteria should be determined based on Table 1 in the chapter "USP<645>Stage 1- Temperature and Conductivity Requirements". According to the measured temperature, the corresponding conductivity value is the conductivity limit of pharmaceutical water.1

Figure 1: Method conditions


Set the flow rates of acid and oxidant required for detecting pharmaceutical water with TOC below 500 ppb to 1.0 μ L/min (acid) and 0.0 μ L/min (oxidant), respectively. This flow rate can ensure the oxidation of carbon in the UV reactor while avoiding excessive oxidation of the sample.


Another method is to use an optional Inorganic Carbon Remover (ICR). If the detection value of inorganic carbon (IC) increases by about 10 times or is greater than the TOC detection value, it is recommended to use an inorganic carbon remover to improve the stability and accuracy of TOC detection.4,5


If the first stage conductivity test fails, please conduct the second stage test according to USP<645>.






Determine the confirmation frequency




Challenge instruments and methods with known standards to provide credibility for each test. Determine the frequency of testing through risk assessment, and confirm the nominal performance of the method on the analyzer using TOC system suitability standards and conductivity confirmation standards. Using standard samples that meet the acceptance criteria can ensure that the analysis of unknown water samples meets the pharmacopoeial requirements for pharmaceutical grade production water.1,6


Although the pharmacopoeia does not specify the frequency of confirmation, it stipulates that production units should regularly use conductivity confirmation standards and system suitability standards to confirm methods. The frequency of confirmation should be determined by assessing the risks and potential impacts of each process. Risk management requires clear definition and evaluation of all variables and their impact on the process. Factors that must be considered include frequency of use of standard samples, sampling time, system suitability or risk of confirmation failure, possibility of out of specification (OOS) results, time constraints, etc. As USP<643>and<645>do not specify frequencies, each production unit is responsible for developing robust process flows and procedures to manage process risks. It is important to use conductivity confirmation standards and system suitability standards at a practical and reasonable frequency, while also meeting the requirements of USP<643>and<645>.


The applicability standard of TOC system aims to confirm the relative recovery ability of the analyzer at the pharmacopoeial upper limit of 500 ppb TOC. The system suitability standard ensures that the analyzer can achieve the applicable TOC recovery rate, thereby making the analysis results of unknown water samples unquestionable. The conductivity confirmation standard sample aims to confirm the accuracy of the conductivity detection of M9 analyzer. Running conductivity confirmation standards at a reasonable frequency can ensure the accuracy of unknown water sample detection while meeting pharmacopoeia requirements.


In order to minimize the differences in standard samples, we recommend using standard samples and sample bottles produced by Sievers analyzer to obtain certified standard samples with consistent concentrations. The applicability standards and conductivity confirmation standards of the Sievers system listed in Table 1 have shown good performance. If you use the standard samples in Table 1, you can obtain OOS investigation support from Sievers analyzer. If your sample, system suitability, or confirmation fails, the quality assurance team of Sievers analyzer will investigate and resolve internal variation factors and on-site instrument performance failures for you, and discuss the investigation results in the fault analysis report.


Product Name

Part Number

System Suitability

Standard sample combination

STD 31004-01

100 µS/cm HCl

Conductivity Confirmation Standard Sample

STD 77050-01

TOC and Conductivity Analysis

Dual purpose DUCT sample bottle

HMI 77500-01

Table 1: Consumables for optimal operation


Finally, it should be ensured that there is always water in the flow path of the analyzer. After using the last standard sample, please rinse the syringe with deionized water or MilliQ water to replace the residual sample in the analyzer.






Troubleshooting and equipment maintenance




Due to the sensitivity and low acceptable concentration of the offline detection method for the first stage conductivity, many users use a Sievers M9 TOC analyzer specifically for offline detection of TOC and conductivity7If the same M9 analyzer is used to detect pharmaceutical water and non pharmaceutical water (i.e. clean validation samples), additional operational steps are required to minimize cross contamination when switching between the two samples. These additional steps depend on the type of non pharmaceutical water to be analyzed. For precautions regarding such operations, please refer to technical document UPW 07-10.8Please maintain and confirm the Sievers analyzer according to its operation and maintenance manual to achieve optimal performance.






Conclusion




By adopting the correct sampling techniques, method conditions, and reasonable confirmation frequency, the accuracy of the TOC and conductivity detection results of the Sievers M9 analyzer can be ensured. The best practices outlined in this article can help you accurately detect TOC and conductivity while meeting pharmacopoeia requirements.