Synthetic Media for Removal of 1,4- Dioxane From Groundwater

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Synthetic Media for Removal of 1,4-Dioxane From Groundwater

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Synthetic Media for Removal of 1,4- Dioxane From Groundwater Steve Woodard, Ph.D., P.E. Presentation Outline Overview of existing treatment pump & treat technologies Challenges faced by these technologies Synthetic Media: an alternative solution How does it work? Where does it apply? Full-scale case studies Economics: comparison to existing technologies 1

Quick Refresher: Why is 1,4-Dioxane Such a Challenge to Treat? Miscible in water Low volatility, low sorption Difficult to measure Difficult to remediate (recalcitrant) Travels rapidly in subsurface; plume often extends beyond extraction wells Once discovered, often the driver for cleanup 1,4-Dioxane Treatment Options?? Biological Air Stripping Advanced Oxidation $$ Synthetic Media (Resin) Reverse Osmosis GAC 2

Challenges with Existing 1,4-D Pump & Treat Technologies (AOP) Struggle with variable influent loadings Delivery, storage and consumption of regulated chemicals (e.g. H 2 O 2 ) Frequent change-out of UV lamps Bromate and hex chrome formation potential TSS/turbidity/TDS reduces effectiveness Subject to free radical scavengers ph-sensitive Mixed full scale results Alternative Solution: Synthetic Media Derived from plastics, Synthetic Media can be used to collect various contaminants from liquids, vapor or atmospheric streams and be reused indefinitely AMBERSORB TM 560 3

Unique Properties of Dow s AMBERSORB TM 560 Hydrophobic Unique pore size distribution High affinity for organic compounds: (simple adsorption mechanism) Can achieve non-detect effluent concentration at substantial loading rates Can typically reuse (regenerate inplace) indefinitely Durable structure AMBERSORB vs. GAC 4

AMBERSORB 560 Removal to ppb or Sub-ppb Levels First Ambersorb System for Groundwater: Lake Charles, LA Operating Since 1999 Treating 1,2-DCA from > 2,000,000 ppb to ND @ 5 ppb Recovery and reuse! 15 years of loading and regenerating media No replacement of media 5

Animated Process Flow Diagram http://craesay.squarespace.com/storage/ect/process_flow.html Case Study Site located in Waltham, Massachusetts Contaminated groundwater remediation Design basis o Flow = 15 gpm o 1,4-dioxane = 20-60 µg/l o Total Chlorinated VOCs = 2,000 9,000 µg/l Modular system design for future relocation 1,4-dioxane permit limits o Originally 3.0 µg/l o Now 0.3 µg/l 6

Insert Overview of Plume µg/l Project Objectives 1. Provide long-term contaminant migration control 2. Achieve compliance with present and future permit limits 3. Learn from this smaller system in anticipation of replacing an existing, upgradient 100-gpm air stripper 7

Project Thesis Statement: Installing a synthetic media system will allow reliable, consistent compliance with low 1,4-dioxane standards, today and into the future. Modular System Design 8

Influent and Effluent 1,4-Dioxane Influent 1,4-Dioxane 9

Influent and Effluent 1,4-Dioxane Influent and Effluent 1,4-Dioxane 10

Influent and Effluent TVOCs Lessons Learned Need to fully regenerate media Materials of construction: low ph of condensate Consider local boiler requirements Small, dedicated Synthetic Media team improves communication and execution: the birth of ECT Synthetic Media systems are robust and dependable 11

Summary Long-term contaminant migration control Consistent, reliable performance, regardless of changing influent conditions No stranded capital. Consistently less than new 0.3 µg/l limit without having to upgrade system Several valuable lessons learned Now applying the lessons from this successful installation in operation of larger, 100-gpm synthetic media system on site (closer to the source area) Waltham 100-gpm System 12

St. Petersburg, FL A Unique Approach to Iron Management Phase 2: Long-term plume control Design Basis: Flow = 100-175 gpm 1,4-dioxane = 2,535 ppb Total Organics = 17,450 ppb Iron = 6-30 mg/l 13

Bench & Pilot Testing Pilot Skid Operating in Westville, IN 14

Full-Scale Mobile Demonstration Unit Full-Scale Mobile Demonstration Unit 15

Clifton Springs Skid: Treating cvocs and 1,4-D Summary 1,4-Dioxane is challenging to treat Permit limits are trending downward AOP systems dominate the existing pump & treat installations, but have their limitations AMBERSORB provides a reliable treatment alternative Early bugs have been worked out Adsorption = simple Media can be regenerated in-place, enhancing sustainability Results have been consistent/dependable Like AOP, AMBERSORB systems can be skidded, containerized and mobile Addresses the issue of stranded capital Capital costs are higher than AOP; O&M costs are lower 16

Steve Woodard 207-210-1551 swoodard@ect2.com 17