Minutes Saltwater Intrusion Steering Committee Meeting March 4, 2011

Similar documents
Exploring Regional Groundwater Supply Alternatives to Manage Saltwater Intrusion in the Hilton Head Island Area

Strategies for Managing Water Resources in Saltwater Intrusion Environments

HILTON HEAD WATER SUPPLY & SALTWATER INTRUSION. Beaufort County Council September 2012

Coastal Georgia Water & Wastewater Permitting Plan For Managing Salt Water Intrusion

ALTERNATE WATER SOURCES

Hilton Head PSD 24-Hour Service Hotline (843)

Carpinteria Valley Water District. Q&A Carpinteria Groundwater Basin (CGB) August 20, 2014

Potable Reuse as an Alternative Water Supply. AWRA Conference Orlando, FL

APPLYING AQUIFER STORAGE RECOVERY TECHNOLOGY TO ADDRESS WATER RESOURCE CHALLENGES IN DIFFFERENT COASTAL PLAIN SETTINGS

Water Supply in Coastal Georgia Meeting Water Demand Using Alternative Water Sources to the Upper Floridan Aquifer

Technical Memorandum. United States Army Corps of Engineers Savannah District

TABLE OF CONTENTS. Purpose and Scope of the Coastal Georgia Water & Wastewater Permitting Plan for Managing Salt Water Intrusion...

Synopsis. Geoffrey R. Tick Dorina Murgulet Hydrogeology Group The University of Alabama UA Project Number Grant # 09-EI UAT-2

UPRR Tie Treating Plant, The Dalles, OR

Planning Today For Water Tomorrow

The Future of Alternative Water Supplies in the SWFWMD. Workshop: Practicable Sustainability: Implementing Water Reuse/Supply/Resource Projects

THE GLYNN COUNTY WATER RESOURCES MANAGEMENT PLAN

Modeling the Contamination of an Aquifer from a Highway Salt Storage Facility

Georgia s. State Water Plan

Capital Area Ground Water Conservation Commission

Surface Water and Seawater Interactions in the Coastal Environment of Biscayne Bay, Southeast Florida

MEMORANDUM. RAI Responses Related to East Lake Road Wellfield Drawdown Analysis, WUP No SDI Project No. PCF-180.

The Feasibility of Using Reclaimed Water for Direct and Indirect Aquifer Recharge in the Tampa Bay Area

Partnerships Changing Water Management Challenges & Strategies. David MacIntyre Parsons Brinckerhoff

U.S. Geological Survey (USGS) Florida Water-Use Program

Understanding Florida s Karst Results & Lessons Learned from the Woodville Karst Plain Research

Michael Weatherby, P.G., MWH, Tampa, FL

The Largest Flowing Artesian Well in the State of Wisconsin is (sometimes) an Abandoned Deep Quarry

Sensitivity to Sea Level Rise (NRCan, 2009) :

Capital Area Ground Water Conservation Commission

Reclaimed Water Aquifer Storage Recovery: Optimization of Our Freshwater Resources

SECTION SIX. Water Quality. Water Quality. Section 6

Aquifer Storage and Recovery Challenges and Solutions Frederick Bloetscher, Ph.D., P.E. Florida Atlantic University

Seawater intrusion into coastal aquifers a case study

RED ZONE WATER SUPPLY MANAGEMENT PLAN

Hydrogeology of the Merti Aquifer. Impact of abstractions on drawdown of water level and salinity. Arjen Oord Jan de Leeuw (presenter)

NORTHWEST FLORIDA WATER MANAGEMENT DISTRICT

400,000. MILLION GALLONS of water per day. The Desalination Plant and Process Locations. Welcome and Overview. people in San Diego County

Measuring the Economic Benefits of America s Everglades Restoration

South Carolina Water Plan Update

Climate Change and Sea Level Rise

Issues of Common Pool Resources

Exhibit D to Lion Oil Petition. Memorandum Regarding Submittal of Environmental Impact Statement to Arkansas Economic Development Commission

Hydraulic Head in 1999 Saline plume migration in 1999

A MODEL OF SEAWATER INTRUSION IN SURFICIAL AND CONFINED AQUIFERS OF NORTHEAST FLORIDA

Groundwater Flow Evaluation and Spatial Geochemical Analysis of the Queen City Aquifer, Texas

Manfred KOCH 1 and Phatsaratsak ARLAI 1, Department of Geotechnology and Engineering Hydrology, University of Kassel, Germany

PUBLIC UTILITIES. Water Service

Office of Water Supply Groundwater Withdrawal Permitting Program

TIERED APPROACH TO EVALUATION AND MANAGEMENT OF PRODUCED WATER IMPACTS ON GROUNDWATER RESOURCES

Water Availability and Use Science Program. WestFAST September 24, 2015

Environmental Cleanup & Restoration Design Project Summer 2002 Overview

Salt Water Intrusion in Coastal Aquifers March, 2015 L. Pilgrim, P.Geo.

Comprehensive Plan for Unincorporated Hillsborough County Potable Water Element - DRAFT

Planning for Our Water Future: City of Santa Cruz & Soquel Creek Water District. September

Groundwater Modeling Guidance

CHAPTER 2. Objectives of Groundwater Modelling

USGS National Water Census. Coastal Carolinas Water Availability Study

The Droplet. Florida Water Environment Association Integrated Water Resources Committee. September 2013 Volume 5 Issue 3. Chair: Saurabh Srivastava

AQUIFER STORAGE AND RECOVERY EVALUATION REPORT

12th Annual Louisiana Water Conference March 27-28, 2018

Development of Decision Support Systems for Estimating Salinity Intrusion Effects due to Climate Change on the South Carolina and Georgia Coast

K.Fujinawa 1 ABSTRACT

The Interconnectedness Between Spring Creek Springs and Wakulla Spring and the Effects on Flow at Wakulla Spring

Reclaimed Water ASR Permitting

Coastal Georgia Regional Water Planning Council

Developing a Sustainable Water Supply Strategy for the City of Plantation, Florida

Robert W. Buddemeier*, Hillel Rubin**, and David P. Young *

Cape Coral Integration of Irrigation Source Waters

Water Resources on PEI: an overview and brief discussion of challenges

Wellsite Salt Remediation: Subsoil Salinity Tool vs. Site- Specific Salt Risk Assessment? Erik J. Martin, Ph.D., DABT

Here is yet another topic you asked to hear about.

CONFERENCE SCHEDULE - Wednesday September 20, 2017

Future Water Demand and the Role of Alternative Sources and Water Reuse in Texas

TSUNAMI DISASTER AND GROUNDWATER RESOURCES: THE SOUTHEASTERN COAST OF INDIA. Bhanu Neupane Regional Hydrologist, UNESCO

NUMERICAL MODELLING OF SALTWATER PLUME MOVEMENT IN A FRACTURED AQUIFER ON SUB-REGIONAL SCALE

Framework for Water Resilience in Long Island. Samudyatha Mysore Subbarama

Building A State of Conservation

Irrigation modeling in Prairie Ronde Township, Kalamazoo County. SW Michigan Water Resources Council meeting May 15, 2012

by Phatcharasak Arlai 1*, Manfred Koch 1, Sucharit Koontanakulvong 2

Cabot Koppers Superfund Site, Gainesville, FL

REPRESENTING HYDRODYNAMIC DISPERSION IN SALTWATER INTRUSION MODELS THAT DIFFER IN TEMPORAL RESOLUTION. Alyssa Dausman 1 and Christian Langevin 1

POSSIBILITIES FOR GROUNDWATER DEVELOPMENT FOR THE CITY OF JAKARTA, INDONESIA

Overview of the Draft 2010 Water Supply Assessment Report. Suwannee River Water Management District

Appendix I. Potential Adverse Change to Wetland Function Methodology and Results

Since the 1920s, the City of Clearwater

The use of an interstage boost on brackish

Receive Site Fact Sheets by . See "For More Information" to Learn How. PUBLIC MEETING ANNOUNCEMENT:

Potential for Accumulation of Recycled Water Contaminants

Biscayne National Park

Quantifying Effects of Humans and Climate on Groundwater Resources Through Modeling of Volcanic-Rock Aquifers of Hawaii

Salt or Sewer? Supplemental Water Supplies for Santa Cruz County

Recommendations for Changes to the Requirements of Section (9), Florida Statutes - Domestic Wastewater Ocean Outfalls

Increasing Acceptance of Direct Potable Reuse as a Drinking Water Source in Ventura, CA

Our Eastern Shore Groundwater Part IV Groundwater Quality on the Eastern Shore: How safe is our groundwater and are there ways we can protect it?

Central Florida has historically utilized

C-51 Reservoir Project Potential Opportunities. Robert M. Brown, Assistant Executive Director

MEMORANDUM. Suwannee River Water Management District Governing Board

Numerical Groundwater Flow Model Report. Caloosa Materials, LLC 3323 Gulf City Road Ruskin, Florida 33570

Tracer Tests with Resistivity Detection to Estimate Seepage Velocity in the Biscayne Aquifer, Florida

Transcription:

Minutes Saltwater Intrusion Steering Committee Meeting March 4, 2011 Attending: David Baize, Brian Baker, Richard Cyr, Billy Edwards, Kelly Ferda, Chris Foldesi Bill Garbett, Chuck Gorman, Rusty Hildebrand, Donna Katula, Dr. Jim Kennedy, Jeff Larson, Steve Liotta, Camille Ransom, John Sawyer, Charles Sexton, Mark Smith, Dr. Richard Spruill, Paul Vogel Richard Cyr opened the meeting by welcoming the Saltwater Intrusion Steering Committee to Hilton Head. David Baize reviewed the action steps from the last meeting, noting that potential management scenarios and associated costs which will be presented at today s meeting. Jeff Larson stated that much progress has been made since the last meeting. This Committee will ultimately identify management scenarios that will be presented to the Governor s Committee (should it continue) and other appropriate state agencies, etc that will need to understand and act on this information.. Dr. Jim Kennedy then presented his work entitled Simulations of Options and Order-of- Magnitude Cost Estimates For Managing the Upper Floridan Aquifer For Salt Water Intrusion. Discussion Related to Dr. Kennedy s Presentation Do the studies include the Colleton River or Broad Creek plume? No, but they can be added. There are ongoing studies that include monitoring wells on a piece of property that has limited access How long has Dr. Kennedy been working on this and what would it cost us if a consultant were hired to do the work? Since late December. The cost would be between $80,000 and $120,000 or higher. Regarding extraction wells, what would be done with the salt water that is extracted? The order-of-magnitude cost estimate assumed that salt water would be discharged to Port Royal Sound. A discharge into the sound may need an NPDES permit, which could take time. Will extraction wells on the north end of Hilton Head Island draw salt water into the system? Yes, and the chloride concentration in the plume would eventually stabilize. Fresh water will be used for injection wells, correct?

Which level of the aquifer would injection wells be placed? Level 6-10, which is in the Upper Floridan Aquifer as defined by South Carolina. Would injection wells drive the salt water plume further south on Hilton Head Island? Yes, but the Sustainable Yield metric to increase the hydraulic head and stop salt water from entering the aquifer under Port Royal Sound will be met. Injection wells on the northern end of Hilton Head Island would cut off the source of salt water from Port Royal Sound and would allow the salt water plume south of the injection wells to continue to move downgradient to the south. Was any consideration given to using injection wells as a buffer and withdrawing some of the injected water for use when needed, like ASR? No, injection was considered only for hydraulic head restoration. Using injection wells as a buffer could be modeled. The model is currently a steady state model so it could not be used to model transient conditions such as ASR. Where would the water go that is injected? It may stay in the system or find its way into the sound. Do we treat injection wells and extraction wells as mutually exclusive? On Hilton Head Island, yes. They would not be used at the same time. However, combinations of injection wells in the Savannah area and extraction wells on Hilton Head Island could be considered because they are far enough apart. Will all combinations of extraction wells, injection wells, and withdrawal reductions have the same effect on the hydraulic gradient? No, each combination will have a different effect on the gradient. Is the model combination with the highest gradient reduction also the most expensive? Model combination 1 included a 97.5 percent reduction in groundwater withdrawals and resulted in elimination of the southward hydraulic gradient on Hilton Head Island. Model combination 1 had the highest order-of-magnitude cost estimate. Model combination 27 resulted in a 55.3 percent reduction of the hydraulic gradient on Hilton Head Island and was one of the six model combinations with an order-of-magnitude cost estimate higher than $500 million. Would model combination 1 have the most effect on the hydraulic gradient? Even with the implementation of any of these options, the regional hydraulic gradient would still exist. These options will solve some of the problems, but not all. Can we take some of the 13.7 mgd indentified in the extraction well model combination for use as a water supply? That was not included in the order-of-magnitude cost estimates.

The water that is extracted could be treated with Reverse Osmosis. With 13.7 mgd extracted and 3 mgd reject, it may give 10 mgd for water supply. What is the highest salinity level that can be treated with Reverse Osmosis? Seawater concentrations. Studies have been done on Hilton Head Island regarding the effects of injection and extraction wells. There will be a significant positive impact on the hydraulic gradient with both injection or extraction wells and what is being proposed here is a feasible approach. The logical next step is to determine how to integrate ASR into these model combinations. We also need to think about protecting individual wells with ASR. With 29 model combinations, we need to choose 2 or 3. Cost is helpful, but should not be the only factor. Whatever our recommendations will be, a feasibility study will be necessary. We don t want to concentrate on just one problem when there may be more to consider, such as the Colleton River plume or downward migration. How will extraction wells affect the rest of the island? North of the extraction barrier, the gradient and plume movement will accelerate. There is also a plume on the backside of the island. A particle tracking model could be done to include that area. We can start with these 29 model combinations and reduce it to the most feasible subset. Other elements or inputs could then be included in the chosen subset of model combinations. The injection wells are just on Hutchinson Island in Savannah? The injection wells on Hutchinson Island were simulated with all other model combinations. The only two model combinations that were not considered together were both injection wells and extraction wells on Hilton Head Island. What do injection wells on Hutchinson Island do? Increases the hydraulic head and reduces the hydraulic gradient on Hilton Head Island. Does a 5 mgd reduction in Savannah have the same result as a 5 mgd barrier in Savannah? No. A 5 mgd reduction is area-wide. Injection occurs at specific points. The cone of depression under Savannah is shaped like concentric circles. If you construct injection wells on the north portion of the cone, you change the shape of the concentric circles. Hilton Head Island has already reduced withdrawals by 50% and the plume is still accelerating. A barrier in Georgia makes more sense. A barrier in Georgia would not capture the salt water plume on Hilton Head Island and keep it from moving downgradient.

We are making assumptions on the cost of surface water. Does Beaufort-Jasper County have the capacity to treat enough surface water to meet the needs of the consumer and injection wells? Both Savannah and Beaufort-Jasper County have the treatment capacity, but not the infrastructure. Per mgd, injection costs more than extraction because of the cost of treating surface water. With injection wells on Hutchinson Island and extraction wells on Hilton Head Island, would salt water leave the system? Probably not. Even with an extraction barrier on the north end of Hilton Head Island, there is still a hydraulic gradient toward Savannah. Can the amount of water injected or extracted be increased so the hydraulic gradient is eliminated? That has not been modeled. We need to define what our objectives are. We defined Sustainable Yield before and it was not to restore contaminated existing wells back to potable water. It will take 100 s of years for salt water to leave the system. We can start with the best options for addressing the existing plume and gradient and then see how the chosen options affect other plumes. Cost is an important factor in the recommended options. The system is out of balance. Any strategy that allows the plume to accelerate or the gradient to increase should not be considered. Injection wells in Savannah helps, but injection or extraction wells on Hilton Head Island will be needed. Does model combination 4 (extraction barrier on Hilton Head Island) stop the plume movement? It would capture the plume on the northern portion of the island. The Colleton River plume is not addressed in any of the model combinations, nor is vertical migration. An extraction barrier could be put at the Colleton River to capture the plume there. How long do we have to implement these options? The chosen options need to be implemented soon to be most effective. Model combination 4 (extraction barrier on Hilton Head Island) looks to be the most attractive. Can we expand that option to include the Colleton River plume? Yes, that can be done. These options are good first steps, but we do not want to leave the impression the problem is solved. We can take steps to address the most urgent problems, then add to that.

If we can develop a plan acceptable by both states, we may have a good chance to get Federal money to assist with implementation. If a chosen option includes extraction wells on north Hilton Head Island, we need to understand the permitting implications. We also need to evaluate the regional effects of the chosen options to make sure there are no unintended consequences. Would extraction wells increase the rate of downward migration of chlorides? No. Injection wells will decrease downward migration of chlorides, correct? Are extraction wells more effective than injection wells? The order-of-magnitude cost estimates of combinations with extraction wells were lower than the cost estimates of combinations with injection wells. Extraction wells would capture the salt water plumes and keep them from moving downgradient. Injection wells would cut off the source of salt water from Port Royal Sound and would allow the salt water plume south of the injection wells to continue t move downgradient to the south Would Dr. Kennedy consider a model run where injection wells are located at the salt waterfreshwater interface and inject water for 300 days and withdraw water during other times of the year? Some of the water injected could possibly be withdrawn at specified times and used for drinking water. Perhaps, but it would involve additional training on the model. The model is currently a steady state model so it could not be used to model transient conditions such as ASR. There is a possibility of combining Dr. Spruill s transient model and Dr. Kennedy s steady state model to evaluate this model combination. Action Steps Dr. Kennedy will complete model simulations requested at today s meeting. David Baize will check on NPDES permitting of a discharge associated with extraction wells.