July 27, A NEW EPA APPROVED METHOD FOR TURBIDITY ANALYSIS 360 x 90, Turbidity Method TURBIDITY MEASUREMENT HISTORY

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A NEW EPA APPROVED METHOD FOR TURBIDITY ANALYSIS 360 x 90, Turbidity Method 10258 TURBIDITY MEASUREMENT HISTORY 2 1

TURBIDITY MEASUREMENT OVER THE LAST 50 YEARS 3 TURBIDITY MEASUREMENT Turbidity is the interaction between light, suspended particles and amedium (water). Turbidity may be determined by measuring the attenuation of a radiant flux as it passes through the liquid or by measuring the intensity of scattered light. Measurement is made at an angle of 90 degrees ( NEPHELOMETRY) Two main historical methods based on different regulations : radiation USEPA 180.1 (white light, 400 600 nm) ISO 7027 (IR light, 860 nm +/ 30 nm) transmission 4 2

WHY SCATTERED LIGHT IS MEASURED AT 90 Nephelometry 90 small particles larger particles even larger particles Measurement of light scattering at 90 in order to minimize effects caused by particle size! 5 WHICH WATER? 6 3

TURBIDITY UNITS HISTORICAL AND MODERN ppm silica (SiO 2 ): In 1955, the relationship of ppm silica (SiO 2 ) concentration and turbidity had been abandoned and the Standard methods described turbidity in terms of light scattering due to suspended matter. The term ppm units and silica scale were discontinued FTU / Formazin Turbidity Unit: When Formazin was accepted as the primary reference standard, units of turbidity measurement became known as Formazin Turbidity Units (FTU). FAU / Formazin Attenuation Unit: LED 860 nm, calibration standard Formazin, absorption measurement (Photometer); ISO 7027 Using a Nephelometer (detector 90 angle): NTU (Nephelometric Turbidity Unit) tungsten filament lamp with EPA filter; calibration standard Formazin USEPA180.1 FNU( Formazin Nephelometric Unit) LED 860 nm; calibration standard Formazin ISO7027 7 TECHNICAL DESIGNS Today, numerous turbidity measurement technologies exist, with some designed specifically for regulatory use and others to meet the monitoring requirements associated with process control applications. Turbidity monitoring technologies can be categorized by three design criteria: The type of incident light source used The detection angle for the scattered light The number of scattered light detectors used 8 4

LIGHT SOURCE Three types of light sources are commonly used in turbidimeters: White light: Incandescent light sources emit a broad spectrum of light that includes shorter wavelengths that are better suited to detection of smaller particles. IR (ISO7027): used in turbidity measurements 830 890 (nm). Light that is typically not absorbed by visible color in the sample, eliminating a common source of error. Laser: very sensitive to small changes in turbidity and are often used to monitor the performance of filters producing ultrapure water such as is commonly used in many industrial processes. 9 NUMBERS + ANGLE OF DETECTORS The detection angle is formed between the centerline of the incident light beam and the centerline of the detector s receiving angle. 90 : Most common detection angle because of its sensitivity to a broad range of particle sizes. 180 : The attenuated detection angle is 180 degrees relative to the incident light beam so it measures the attenuation of the incident light beam due to both light scatter and absorption. 0 45 : This angle is sensitive to light that is reflected in the direction of the incident light source, which is characteristic of extremely high turbidity samples. 45 90 135 180 10 5

INSTRUMENTS USEPA METHOD 180.1 Most common regulatory method used in the world Standard Methods for the Examination of Water and Wastewater Method 2130B is very similar. Required Design Criteria Primary detector for nephelometric (90 ) measurement ±2.5 Light source tungsten filament lamp with a color temperature between 2200 and 3000 K. Spectral response peak for the detector between 400 and 600 nm, the primary wavelengths of visible light Measurement range 0.0032 NTU to 40 NTU. Any sample above this range must be diluted until it is within this range. 11 INSTRUMENTS METHOD 10133 Laser turbidimeter method EPA approved for drinking water reporting since 2002 Required design criteria Primary detector must operate at 90 2.5 Laser Diode operated at a wavelength of 660 30 nm Method detection limit: 1 mntu Instrument range: 1mNTU to 5 NTU Any sample above this range must be diluted until it is within this range. 12 6

CURRENT MEASUREMENT TECHNOLOGY Incandescent Lamp or Laser Response time: Between 1.5 2 minutes Sample required: >1L Built in Bubble Trap Cleaning time: >10 minutes No similar laboratory measurement technology 13 STANDARDS FORMAZIN AND STABLCAL FOR QUALITY CONTROL FORMAZIN Formazin is the closest mimic for real world samples (0.01µm...10µm) Formazin particle distribution is similar to natural water samples, size distributions is approximate the 1/d 3 relationship: When particle size decreases by a factor 10, number of particles increases by factor of 1000 If a sample contains 1 particle of 10 µm/ml, one ml of sample would contain: 1,000 particles of 1 µm and 1,000,000 particles of 0.1 µm. 14 7

STANDARDS FORMAZIN AND STABLCAL FOR QUALITY CONTROL Signal 1 There are few particles in the sample. Each particle is hit by the light beam and scatters light at a 90 angle. The correlation between number of particles and signal is linear up to 40 NTU Formazin. NTU 2 An increasing number of particles 3 With an increasing number of causes light to scatter off multiple particles the interference is strong particles. Some of the scattered light enough that the signal (scattered fails to reach the detector. The signal light) decreases. is no longer linear. 15 STANDARDS FORMAZIN AND STABLCAL FOR QUALITY CONTROL FORMAZIN Benefits: Highly reflective standards efficiently scatter incident light Light absorption by the formazin polymer is minimal Can be prepared reproducibly from traceable raw materials Formazin polymer has a density similar to that of water Formazin is the accepted primary turbidity standard (US EPA, ISO etc.) Stable turbidity suspension (in high concentrations like 4000 NTU) that produces stable measurements over time Drawback: Diluted Formazin Suspensions are unstable and must be prepared fresh Raw chemicals are harmful (carcinogenic) and allergenic 16 8

REPRESENTATIVE TURBIDITY: 17 REPRESENTATIVE TURBIDITY: Use a clean sample cell for sample measurement. Do not to touch or scratch the glass of the sample vial. Contamination with dust or fingerprints or scratches on the glass can cause measurement errors. Proper sampling techniques are important to get accurate measurements. Please rinse the sample cell and cap with the sample at least 3 times. After filling the vial with the sample immediately put the cap on the sample cell. Dry the external surface of the sample cell (don t forget the bottom) with a soft, lint free cloth. Hold the sample cell by the top only (on the label) to minimize dirt and fingerprints. 18 9

REPRESENTATIVE TURBIDITY: 19 TURBIDITY METHOD 10258 2.0 SUMMARY OF METHOD 2.1 The method is based upon a comparison of the intensity of light scattered by the sample under defined conditions with the intensity of light scattered by a standard reference suspension. The higher the intensity of the scattered light, the higher the turbidity. Measurements in mntu are made in a 360o nephelometer designed according to specifications outlined in Section 6 of this method. A primary standard suspension of Formazin or stabilized Formazin is used to verify the analytical system s on going accuracy and stability of measurement (Section 9). 20 10

CURRENT CHALLENGES IN TURBIDITY MEASUREMENT Lab results don t always match process results Which instrument is correct? Which measurement should you trust? Accuracy and repeatability is not sufficient. Current technology detects, but cannot overcome, influences of: scratches glass variability finger prints non representative particles in the sample Online instruments require quarterly cleaning and calibration. Lab comparison needs thorough cleaning and storing of vials, oiling and indexing. All steps have a high potential for human errors. 21 OPTICAL PERFORMANCE NEW 360 O X 90 O : Method 10258 Turbidity is measured by directing a laser into a sample to scatter light off suspended particles. The light scattered at a 90 angle from the incident beam is reflected through a conical mirror in a 360 ring around the sample before it is captured by a detector. OLD: Method 180.1 The light scattered at a 90 angle from the incident beam is captured by a detector. Every irregularity in this light path leads to false readings like glass scratches, finger prints, nonrepresentative particles etc. 22 11

360 O X 90 O OPTICS Sample Cell Scattered Light at 90 o 360 o collector 90 o scatter Laser Light Source 23 Detector MATCHING LAB AND ONLINE RESULTS Identical 360 x 90 optical systems in both instruments 24 12

360 O X 90 O TURBIDITY The 360 x 90 technology dramatically reduces the time needed to get a reliable turbidity measurement, with 98% less online sample surface area to clean, sealed vials for calibration, and the elimination of the need for indexing and silicone oil in the lab. A smaller online sample volume means events will be detected almost immediately. Process: 98% less space to clean Lab: no need for indexing and using silicone oil Process: smaller online vial detects change in turbidity faster Lab: sealed vials reduce the time needed for calibration 25 360 O X 90 O TURBIDITY METHOD 10258 Uses a small sample cell 98% less space to clean the current online turbidimeter 26 13

360 O X 90 O TURBIDITY METHOD 10258 Smaller vial = faster detection A 15x increase in speed of response is seen in the process turbidimeter 27 360 O X 90 O TURBIDITY METHOD 10258 Lab: no need for indexing and using silicone oil 28 14

360 O X 90 O TURBIDITY METHOD 10258 Using sealed vials reduces the time needed for calibration in both the lab and online turbidimeters No silicone oil required 29 360 O X 90 O TURBIDITY METHOD 10258 Using sealed vials reduces the time needed for calibration in both the lab and online turbidimeters Calibration 30 15

360 O X 90 O TURBIDITY METHOD 10258 The same sealed vials can be used to calibrate both the lab and online turbidimeters 31 EPA RELATED TOPICS 16

EPA APPROVAL Method 10258 was approved and published in the Federal Register on July 19, 2016 Hach Method 10258 is now approved by EPA for turbidity regulatory compliance monitoring and reporting Individual Water Plants Check utility permit for turbidity measurement requirements: Permit allows use of any EPA approved method Connect with regulator to get quick alignment on installing TU5 Permit requires use of a specific turbidimeter or specific method Work with the regulator to update permit to include Method 10258 33 CALIBRATION Text from TU5 EPA User Manuals: EPA Turbidity Guidance Manual (815 R 99 010), April 1999 Regardless of method, EPA recommends cleaning and calibration of turbidimeters on a quarterly basis. Videos on completing both bulk standard and sealed vial calibrations to be available on YouTube by early September 34 17

LEARN MORE Launch Site: www.hachtu5.com Watch instructional videos on www.youtube.com: Unboxing the TU5 Installation Basic Operation Calibration Routine Maintenance Troubleshooting RFID Workflow, Lab and process result comparison 35 QUESTIONS? DISCUSSION 36 18

Happy Trails 37 19