Plumbing Africa January 2018 | Page 30

28 HEALTH AND SANITATION Legionella – copper-silver ionization (CSI) operational conditions Maintaining copper and silver at the levels recommended by the manufacturer is a best practice in achieving operation effectiveness. By Environmental Protection Agency, document EPA 810-R-16-001 PARAMETER CONDITIONS INDICATING OPERATIONAL EFFECTIVENESS Note that monitoring typically includes measurement of the total metal concentration, which includes copper and silver that are bound up as complexes, as well as copper and silver ions. The presence of copper and silver ions is thought to be critical for treatment effectiveness, so maintaining proper pH and avoiding interfering materials (e.g. phosphates, chlorides) is also important (Zevenhuizen et al., 1979). CSI systems can be plumbed into either the cold water entry pipe or plumbed into the hot water line. Examples of interferences include: • In the presence of 20–40 mg/L of chloride ions, silver ion levels are significantly (60 per cent) decreased by complexing with chloride (and are presumably less microbiocidal) (Lin et al., 2002). • Phosphates, such as those added for corrosion control, can bind to copper ions as well as silver ions, reducing their treatment effectiveness (Zevenhuizen et al., 1979). The presence of dissolved organic carbon at 2mg/L, calcium at 100mg/L, magnesium at 80mg/L, and bicarbonate at 150mg/L did not appear to decrease the treatment efficacy of copper and silver ions against L. pneumophila in a laboratory study (Lin et al., 2002). The impact of pH on the ionic nature (and thus the microbiocidal action) of copper in solution is also January 2018 Volume 23 I Number 11 important. At pH levels >6.0, copper forms insoluble complexes with a number of compounds. While in the pH range typical of potable waters (pH 6–9), silver ions are not diminished. In a controlled laboratory study, Lin et al. (2002) found that at a pH of 7, exposure to 0.4mg/L of copper resulted in a 4-log (99.99-percent) reduction of L. pneumophila in one hour; however, at a pH of 9, there was no appreciable decrease in L. pneumophila over the same period of time with the same copper exposure. Dziewulski et al. (2015) demonstrated efficacy of CSI under alkaline water conditions (pH 8.0-9.8) and found that silver ions controlled the L. pneumophila serotypes 1 and 6, and L. anisa. With regard to the effects of temperature, one study (Landeen et al., 1989) found no significant difference in L. pneumophila inactivation rates in experiments conducted at room temperature (21–23 degrees C, or 69.8–73.4 degrees F) and elevated temperature (39–40 degrees C, or 102.2–104 degrees F) using water with 0.2mg/L free chlorine, with or without 400µg/L of copper and 40µg/L of silver. INSTALLATION CONSIDERATIONS CSI systems can be plumbed into either the cold water entry pipe or plumbed into the hot water line. Care should be taken to install devices downstream of any process that will remove or exchange copper and silver www.plumbingafrica.co.za