Laserfiche WebLink
<br />2.2 WATER QUALITY PARAMETERS <br /> <br />2.2.1 UV Transmittance <br /> <br />UV transmittance (UVT) is the ratio of UV light transmitted through the sample to that transmitted <br />through a reference solution. UVT is measured using a UV spectrophotometer. Reagent grade water <br />is typically used as the reference solution (i.e., UVT = 100%). UV absorbance (A λ )] measures the <br />amount of light absorbed by a solution over a given path length (l) and at a given wavelength (λ). <br />UVT and UV absorbance are related by the following equation: <br /> <br />UVT=10-Aλx100 <br /> <br />The typical cell pathlength is 1 cm and both transmittance and absorbance values are commonly <br />reported per cm. A key reference wavelength, and one at which UVT is often reported, is 254 nm. <br />This wavelength is used because it is the wavelength at which a low pressure mercury UV lamp emits <br />light. Transmittance decreases in the presence of UV absorbing substances and particles that either <br />absorb or scatter UV light. This results in a reduction of available UV energy for disinfection and <br />oxidation. The UV transmittance is the most important water quality parameter used in the sizing of a <br />UV system. A UV system designer may compensate for low transmittance by increasing the residence <br />time or the amount of equipment. <br /> <br />2.2.2 Hydroxyl Radical Scavenging Demand <br /> <br />While the desired reaction in UV oxidation systems is between photogenerated hydroxyl radicals and <br />contaminant molecules the unselective nature of hydroxyl radical reactions result in reaction pathways that <br />consume hydroxyl radicals by reaction with constituents of the background water matrix. Examples of these <br />hydroxyl radical scavenging reactions are the oxidation reactions with the natural organic matter (NOM) <br />present in natural waters or reactions with carbonate and/or bicarbonate ions. Hydrogen peroxide itself will <br />react with hydroxyl radicals and, therefore, is considered a hydroxyl radical scavenger. All of these <br />scavenging reactions have the effect of reducing the steady state concentration of hydroxyl radicals in the <br />water. Since the rate of contaminant degradation is proportional to the steady state concentration of hydroxyl <br />radicals, these hydroxyl radical scavenging reactions reduce the rate of contaminant degradation. The level <br />of scavenging reactions associated with a water sample can be quantified and is referred to as the hydroxyl <br />radical scavenging demand of the water. Trojan routinely determines the scavenging demand of water <br />samples at its laboratory in London, Ontario. <br /> <br />2.3 THE ELECTRICAL ENERGY PER ORDER PARAMETER <br /> <br />In sizing UV systems for Environmental Contaminant Treatment, a different metric is used than for <br />UV systems for disinfection. This metric is called Electrical Energy per Order, or E EO (Bolton et al. <br />1996). <br /> <br />E EO is the electrical energy (measured line power draw) required to reduce the contaminant <br />concentration by one order of magnitude (one log, or 90%) in one cubic meter (m3) or 1000 gallons <br />(kgal) of water (depending on the choice of flow units). Typical units are: <br />  <br /> <br /> <br /> <br /> <br /> <br />•orderkgal <br />kWh or  <br /> <br /> <br /> <br />•orderm <br />kWh <br />3 . <br /> 3