Optimizing the Ballasted Sedimentation Process at the Anacortes Water Treatment Plant Jeff Marrs Plant Manager Greg Pierson - HDR

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Optimizing the Ballasted Sedimentation Process at the Anacortes Water Treatment Plant Jeff Marrs Plant Manager Greg Pierson - HDR 2014 HDR, Inc., all rights reserved.

Presentation Overview Project drivers and objectives Raw water quality Treatment process system overview Optimization of ballasted sedimentation

Anacortes Water System Service Area Del Mar Anacortes Tesoro & Shell Oil Refineries Mount Vernon Swinomish Tribe La Conner Naval Air Station Oak Harbor Skagit PUD

Project Drivers Challenges/Limitations Floodplain elevation Challenging Raw Water Quality Dramatic fluctuations of Turbidity and Color Ineffective Pre-treatment Need to Expand Treatment Capacity 2007 max. day demand: 29 MGD 2030 max. day demand: 40.7 MGD Condition of existing structures Reliability and Redundancy needed for continuous operations

Raw Water Quality (2003-2008) Turbidity Average: 28 NTU 95th-%: 81 NTU 98th-%: 164 NTU Maximum: 5475 NTU Color: 1 4872 Pt Co ph: 6.5-7.8 Alkalinity: 16-38 mg/l TOC 0.5 to 3.0 mg/l

Treatment Scheme Ballasted sedimentation Rapid sand filtration Chlorine contacting CT compliance Finished water ph adjustment

Treatment Facilities General Arrangement Standby Generators High Service Pumps Ballasted Sedimentation (2 trains) Lagoons Decant PS FW Storage Tank 8 Filters Pipe Gallery (Lower), Electrical and Operation Control (Upper)

Design Production Requirements Treatment capacity 42 MGD Future expansion capacity 55 MGD Emergency conditions treatment capacity 21 MGD

Ballasted Sedimentation Process Add Coagulant to Grow Large Floc particles Flocculate Microsand Particle Microsand Particle Add Ballast and Polymer Floc Particles Large Solid Particle Ballasted Flocculation Settling use plate settlers to enhance separation

Ballasted Sedimentation - Actiflo SLUDGE (0.5 to 1%) HYDROCYCLONE POLYMER MICRO-SAND BALLASTED FLOCS TO HYDROCYCLONE CLARIFIED WATER ALUM COAGULANT / CAUSTIC / RAW WATER INJECTION COAGULATION MATURATION TUBE SETTLER WITH SCRAPER Manufacturer: Kruger

Key Design Parameters from Pilot Testing Raw Turbidity (NTU) Coagulant Dose (mg/l) Polymer Dose (mg/l) Target Settled Water ph with Lime Dose Mixing Speed (Hz) Hydraulic Loading Rate (HLR) (gpm/ft 2 ) Low (< 15) High (up to 2200) 18 0.4 Not Required 90 18-43 50* 0.5 7.55 90 18-43

Treatment Goals for Ballasted Sedimentation Raw Water Turbidity Range Less than or equal to 200 NTU Between 201 NTU and 500 NTU Greater than 500 NTU Settled Water Turbidity Less than or equal to 2 NTU Less than or equal to 3 NTU Less than 5 NTU Settled Water Quality Performance Requirements Parameters Turbidity (NTU) Settled Water Quality Criteria Target: Not greater than 1 NTU 95th percentile: Not greater than 2 NTU* 98th percentile: Not greater than 5 NTU * Washington Department of Health (DOH) Treatment Optimization Program turbidity goal

Ballasted Sedimentation System Two parallel trains with 27 MGD capacity each

Ballasted Sedimentation Equipment Micro-sand Recycle Pumps

Ballasted Sedimentation - Equipment Mixer Drives Hydrocyclones

Filtration System 8 cells, each with 2 bays

Residuals Handling Three lagoons: One in-service One in standby One out-of-service Floating decanter each lagoon Decant water booster pumps for high river level conditions

Optimization

Optimization Aluminum Sulfate o Range from 5 40 mg/l depending on river changes Coagulant Polymer o Ranges from 0.40-0.50 mg/l o Not frequently adjusted o Carry over to filters Caustic Soda o Used for ph control when raw water does not meet treatment requirements. o Ranges from 1.0 6 mg/l Chemical injection and in-line rapid mix for ballasted sedimentation trains

Optimization Microsand o Maintain 3-6 grains per liter. (manufacturers recommendation) o Rarely add sand due to high sediment in source water o Regular monitoring with infrequent adjustments. o Highest amount of maintenance required. Soda Ash o Used for alkalinity control o Not regularly used

Optimization Following year 1 of operation, operators began experimenting with chemical dose ranges Resulted in reduced chemical costs with improved results Added laboratory analysis for quality control

Laboratory Charge Analyzer vs. Jar Testing

Operator Challenges Frequent changes in source water conditions Imbalance in chemical doses in pre-treatment process affects filter operations Changes can occur in minutes due to short detention time (This is a good and bad thing) Due to high flow demand and limited storage operators have little time to correct any problems

Typical Results Raw Water o 5 1100 NTU o 7.00-7.40 ph o Alkalinity is 15 30 mg/l Settled Water o Target is less than 1.0 NTU at all times. Typical is less than 0.50 NTU. 95% or greater removal typical. o ph range is 6.80-7.20 o Alkalinity is 15-25 mg/l

Typical Results - Filtration o Alum is added to aid in filter performance (1.0-1.5 mg/l) o Filter Aid Poly is added for enhanced performance o Typical run time varies but normally is 72-96 hours o Finished water turbidity is typically 0.020 NTU or less

Results 1050 Raw Water NTU 0.90 NTU Settled 99.9 % Removal