Technical Bulletin // Up-Flo Filter

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Technical Bulletin // Up-Flo Filter Evaluation of Sil-Co-sil 106 Removal Performance using cpz mix tm media 2006 Hydro International 94 Hutchins Drive Portland, ME 04102 Tel: 207.756.6200 Fax: 207.756.6212 www.hydrointernational.biz

2006 Hydro International SW-UF-003-01 COPYRIGHT STATEMENT: The contents of this document are intended for the use of the recipient to whom the document and all associated information are directed. Hydro International plc owns the copyright of this document (including graphics), which is supplied in confidence. It must not be used for any purpose other than that for which it is supplied and must not be reproduced, in whole or in part stored in a retrieval system or transmitted in any form or by any means without prior permission in writing from Hydro International plc. Up-Flo Filter is a trademarked filtration device of Hydro International plc. A patent covering the Up-Flo Filter has been granted.

Technical Bulletin // Up-Flo Filter Evaluation of sil-co-sil 106 Removal Performance using cpz mix tm media Introduction The Up-Flo Filter is a high rate, modular filtration system designed to meet the most stringent stormwater treatment regulations. It incorporates multiple elements of a treatment train design into a single, small-footprint device. The Up-Flo Filter is engineered to remove over 80% of fine TSS and associated pollutants. Filter Media can be customized to target site-specific pollutants. This test evaluated the TSS removal performance of Hydro International s CPZ Mix media at an operational filtration rate of 25 gpm per Filter Module. The feed pollutant used was Sil-Co-Sil 106, a commercially available ground silica gradation having 100% of particles smaller than 212 microns in diameter and 75% of particles smaller than 45 microns in diameter. The particle size distribution for Sil-Co-Sil 106 can be found in Figure 1. TESTING ARRANGEMENT AND PROCEDURES A full-scale, Catch Basin configuration Up-Flo Filter equipped with one Filter Module was used for this test. The Filter Module contained two (2) media bags of Hydro International s CPZ Mix. A 3-inch Flygt pump delivered influent from the 23,000 gallon clean water reservoir to the Up-Flo Filter through an 8-inch PVC pipe network. The pipe network was equipped with a Hershey VP-820 butterfly valve to return flows in excess of the desired influent flow rate to the feed reservoir. A slurry supply tank containing Sil-Co-Sil 106 and clean water was continuously mixed and fed to the delivery line with a Watson Marlow 704 S/R peristaltic pump at 80 rpm. The slurry was fed to the delivery line three (3) feet upstream of the Up-Flo Filter. The Sil-Co-Sil 106 Particle Size Distribution 100% 90% 80% %FINER THAN 70% 60% 50% 40% 30% 20% 10% 0% 1 10 100 1000 MICRONS Figure 1: Sil-Co-Sil 106 particle size distribution verified according to ASTM D422 (AASHTO T88) 1

delivery line freely discharged the synthetic waste stream with a Sil-Co-Sil 106 concentration of 200-300 mg/l into the open top of the Up-Flo test tank at a rate of 25 gpm. A steady-state water level in the Up-Flo Filter test tank was continuously maintained to confirm the desired filtration rate of 25 gpm per Filter Module. Influent grab samples were taken from the free discharge of the delivery network. Effluent grab samples were taken from the free discharge of the Up-Flo Filter outlet pipe, two (2) feet downstream of the Up-Flo Filter. SAMPLE ANALYSIS Influent and effluent samples were analyzed using an equivalent standard to the TSS Test Method 2 Filtration in ASTM, 1999, D 3977-97 - the Standard Methods 19th Ed 1995 for the Examination of Water and Wastewater prepared and published by the American Public Health Association (APHA), American Water Works Association (AWWA), and Water Environment Federation (WEF) chapter 2-2540 D Total Suspended Solids Dried at 103-105 Celsius. A total of 15 paired influent and effluent samples were analyzed for Total Suspended Solids concentration. All influent samples had a TSS concentration in the 200 300 mg/l range, while all effluent samples were in the 28 40 mg/l range (see Figure 2). DATA ANALYSIS The percent of Sil-Co-Sil 106 removed was derived from the concentrations of each paired sample. To ascertain the representativeness of the data, the sample sets were subjected to a Dixon Q s test and an ANOVA analysis. Table 1 shows the percent of Sil-Co-Sil 106 removed by the CPZ Mix during the test trials. The percent of Sil- Co-Sil 106 removed for each sample pair was determined using Equation 1: % Removal = 100 x ( [TSS] INF [TSS] EFF ) / [TSS] INF Paired Sample Concentrations for CPZ Mix Trials 350 TSS Concentration (mg/l) 300 250 200 150 100 50 0 Influent (mg/l) Effluent (mg/l) Sample 1 Sample 2 Sample 3 Sample 4 Sample 5 Sample 6 Sample 7 Sample 8 Sample 9 Sample 10 Sample 11 Sample 12 Sample 13 Sample 14 Sample 15 Figure 2: Influent and Effluent TSS concentrations 2

Sample Set 1 Sample Set 2 Sample Set 3 Paired Samples for CPZ Mix Trials Sample Influent (mg/l) Effluent (mg/l) % Removed 1 289.51 29.89 89.7% 2 295.89 35.23 88.1% 3 297.56 36.99 87.6% 4 295.24 40.48 86.3% 5 298.73 42.62 85.7% 6 261.11 32.37 87.6% 7 242.67 32.56 86.6% 8 240.00 30.95 87.1% 9 221.52 31.76 85.7% 10 264.00 34.83 86.8% 11 231.58 34.12 85.3% 12 234.67 32.94 86.0% 13 241.25 33.33 86.2% 14 243.71 29.55 87.9% 15 225.97 28.89 87.2% AVG 258.89 33.77 87.0% Table 1: Paired sample TSS concentrations and percent removed The Average % Removal for each laboratory trial was calculated using Equation 2: %REM=100 x ([TSS] AVG INF [TSS] AVG EFF )/[TSS] AVG INF By Equation 2, the average Sil-Co-Sil 106 Removal for all 15 trials is 87% at a flow rate of 25 gpm per Filter Module. To evaluate the sample sets for statistical validity, a Dixon s Q analysis was conducted. Table 2 shows that all samples have a Q < Q 15, thus there are no outliers within the samples and the data set may be deemed valid DIXON Q TEST of CPZ Mix Trials on Sil-Co-Sil 106 Influent (mg/l) Q influent Effluent (mg/l) Q effluent 221.52 28.89 225.97 0.0577 29.55 0.0478 231.58 0.0726 29.89 0.0247 234.67 0.0400 30.95 0.0777 240.00 0.0691 31.76 0.0591 241.25 0.0162 32.37 0.0441 242.67 0.0183 32.56 0.0137 243.71 0.0135 32.94 0.0279 261.11 0.2254 33.33 0.0286 264.00 0.0374 34.12 0.0571 289.51 0.3304 34.83 0.0520 295.24 0.0742 35.23 0.0288 295.89 0.0084 36.99 0.1287 297.56 0.0216 40.48 0.2535 298.73 0.0152 42.62 0.1563 99% confidence Q15=0.475 SAMPLE SET Table 2: Dixon s Q test for paired influent and effluent sample concentrations 3

SUMMARY Groups Count Sum Average Variance Column 1 17 41.024 2.413 0.003 Column 2 17 22.135 1.302 0.031 ANOVA Source of Variation SS df MS F P-value F crit Between Groups 10.49407 1 10.494 621.580 1.56E-22 4.149 Within Groups 0.540252 32 0.017 Total 11.034 33 Table 3: ANOVA regression analysis for the log values of influent and effluent sample concentrations with 99% confidence. An ANOVA single factor test was conducted on the influent and effluent sample sets to show that the data sets were significantly different. The log values of the influent and effluent concentrations were used, as most water quality data follow a log normal distribution. Table 3 shows the results of the ANOVA analysis. The P-value is shown to be 4.21 E-43, which indicates that the influent and effluent sample sets are significantly different with over 99.9% confidence. Conclusions Based on laboratory testing, the Up-Flo Filter with CPZ Mix media will remove 87% of Sil-Co-Sil 106 at a filtration rate of 25 gpm per Filter Module. A detailed lab report is available upon request. 4