indirect potable reuse and groundwater injection in the u.s. · 2018-04-04 · indirect potable...
TRANSCRIPT
Indirect Potable Reuse and Groundwater Injection in the U.S.
Erik Rosenfeldt, Ph.D., P.E.
2015 Education Seminar: Bringing Game Changing Innovation Home to VirginiaApril 29-30, 2015 | Westin Hotel in Richmond, VA
Agenda
• Introduction
• Drivers Behind Potable Reuse
• A quick tour of Reuse in the United States
• Challenges in the Near and Far Future
• Regulatory Structure
• Can we trust the technology?
• Can we trust the operations?
What is Water Reuse/Recycling?
Non-Potable• Irrigation—Golf, Residential, etc.• Cooling Towers, Boiler Feed• Wetland Restoration
Potable• Indirect
• Seawater Intrusion Barrier• Groundwater Replenishment• Aquifer Storage/Recovery• Reservoir Augmentation
• Direct• Pipe-to-Pipe
Water Quality Risks Stem from Source
Potential Risks to Water Supplies are often similar
Risks Pristine Surface Waters
Groundwater Sources
Wastewater Reuse Polluted Surface Waters
Pathogens
Disinfection Byproducts
Secondary Standards
Metals
Industrial Contaminants
EDCs and PPCPs
Emerging Contaminants
De Facto Reuse occurring anyhow
Drivers for Water Reuse
People Are Moving to Water-Stressed Areas
Source: www.sandia.gov
Population Growth is 20% to 50%
in Most Water-Stressed Areas
US population will increase
significantly (double over 100 years)
By 2030, 47% of world population will
be living in areas of high water stress
Need to find water for an equivalent of
the population of San Diego per year
What are the Drivers for Water Reuse?
• Opportunity to Sell Recycled Water Product
• Energy Conservation / Resource Recovery
• Wastewater Disposal / Nutrient Management
• Minimizing Potable Demand
• Delay Potable Water Infrastructure Expansion
• Lack of Adequate Water Supply
• Seawater Intrusion Barriers
• Groundwater Replenishment
• Legislated Conservation/Reuse
• Maintaining Environmental Flows/
Parks/Wetlands
California: Relative Costs of Water Reuse Can Be Cost Competitive
California: Water Reuse Can Be Energy Competitive
Potable Reuse in California
• Long history of indirect potable reuse.
• Significant goals to expand
South Florida Drivers
Regional Water Availability Rule (Demand Not Met)
Ocean Outfall Rule
60% Reuse Requirement(160 mgd of reuse needed)
Georgia Drivers
Land Subsidence
Virginia
The aquifer system in the region has been compacted by
extensive groundwater pumping in the region at rates of 1.5- to
3.7-mm/yr; this compaction accounts for more than half of
observed land subsidence in the region.
California
Examples of Planned Reuse Systems in the US
Early Potable Reuse
• Chanute, Kansas, 1956 Emergency
• Secondary WW, 17-day holding pond
• 5 Months of DPR, 100% Recycle 8 – 15 x
• Denver Water Demonstration, 1985-1992
• Evaluated Secondary WW:• High-pH lime
clarification/recarbonation/filtration/UV/ GAC /RO/ aeration/ozonation/chloramination
• High-pH lime clarification/recarbonation/filtration/UV/ GAC /UF/ aeration/ozonation/chloramination
• Health studies NO adverse outcomes
• OCWD built Water Factory 21 in 1975. First useof RO to recycle water for seawater injection barrier 15 MGD.• (2 years earlier than first membrane seawater
RO)
• 1991- California Dept of Health granted first permit to inject 100% recycled water without blending.
• 25 years of business as usual
Water Factory 21 (1975 – 2004)
Orange County Water District – Groundwater Replenishment
• Pop. 2.5 million
• Annual rainfall < 12 inches
• Groundwater basin lowered fromover extraction by 1920s.
• Reliance on Colorado River and Northern California
• 40% Surface Water
• 60% Groundwater
• By 1950s, over extraction of groundwater had led to seawater intrusion contamination of deep water aquifers.
Advanced Treatment for
Groundwater Replenishment
Advanced Purification Process – Membrane-Based Treatment
“Tastes like water, because it is water”
SE Florida Searches for Reuse Opportunities
ParameterHollywood
(mg/L)
Biscayne
(mg/L)
Floridan
(mg/L)
Sodium ≈640 ≈20 ≈1,100
Chloride ≈1,400 ≈140 ≈2,100
TDS ≈3,500 ≈300 ≈4,500
Unique hydrogeology facilitatesan alternative approach
Opportunity for a revised recharge treatment approach
Reverse Osmosis WTP
AOP
Secondary
or Tertiary
Effluent
Backwash Waste
Reverse Osmosis
Concentrate
Microfiltration
Floridan
Aquifer
Recharge
Treatment designed specifically for emerging contaminants
Texas Cities: Direct Potable Reuse
IPR in Virginia
• Potomac Region (Unplanned and Planned IPR examples)
Challenges Remaining for Potable Reuse
What’s the Greatest Risk in Recycled Water?
• True Risks
• Pathogens
• ALL Regulated Contaminants
• Industrial Contaminants
• Operations
• Perception Risks
• “Emerging Contaminants”
• Notice of Violation
• Aesthetics
Inconsistent Regulatory Approaches
California Title 22 (Potable)• 12-log Virus removal (99.9999999999%)
• 10-log Giardia and Crypto removal
• Sum of all treatment processes
Plus
• 1,4-dioxane and NDMA removal to non-detect
• Removal of contaminants of emerging concern (CECs) base on chemistry, reactivity
Georgia Reuse Regulations• Three Overarching Themes:
• Managed risks and safeguards adequately provided for IPR
• Concept of IPR is based on sound technology and processes
• Growing public acceptance of emerging technology used to assure the safety of IPR
• Concepts of the methods• Requires “Environmental” or “Engineered”
buffer• Required blending according to 7Q10 flows• Treatment technologies considering both
WW and DW treatment
• “Points” provided for treatment barriers
• OK, TX, NC, VA have different approaches
Ensuring Safety of Potable Water?
• Sure technology is capable, but questions remain…
Multi-Barrier Approaches for Potable Reuse Projects (www.waterreuseguidelines.org)
DPR- Raising the Stakes
Can We Trust the
Technology?
Can We Trust
Operations?
Trust but Verify
Convincing a
Skeptical Public
Convincing
Regulators
WRRF-13-03:
Critical Control Point Assessment to Quantify Robustness and Reliability of Multiple Treatment Barriers of a DPR Scheme
Can We Trust the
Technology?
What Does the CCP Approach Provide?
Review and Manage Risks to Protect Public Health
What are the
risks?
Holistic Review/robust methodology – source water to distribution
What are the
right
technologies?
How are we
sure they are
working?
How do we
respond if a
barrier fails?
Contaminants/
Hazardous Events
Treatment
BarriersMonitoring
Operating
Response
Focus is on health relevant contaminants.
WRRF-13-13:
Development of Operation and Maintenance Plan and Training and Certification Framework for Direct Potable Reuse (DPR) Systems
Can We Trust the
Operations?
Where to I Find Trained Reuse Operators?
A gap in training and certification for reuse...
Weekly Alarm Count
0
100
200
300
400
500
600
700
800
900
1000
10/5/09 -
16/05/09
18/5//09 -
25/5/09
25/5/09 - 1/6/09 1/6/09 - 7/6/09 8/6/09 - 15/6/09 15/06/09 -
22/06/09
22/6/09 - 29/6/09 29/6/09 - 5/7/09 6/7/09 - 13/7/09
Week
Ala
rm
s p
er D
ay (
Weekly
Avg
)
Alarms per day Avg Bundamba 1A
Alarms per day Avg Bundamba 1B
Plant 1
Plant 2
Summary
• Potable Water Reuse is NOT a new concept
• De facto reuse widely practiced in the US
• Diverse drivers for each region
• Intentional IPR and DPR is becoming more common
• Multiple technology options• Membrane-based advanced treatment = MF-RO-UV/AOP• Alternative advanced treatment includes ozone, BAC/GAC, IX, and other
processes
• Several Important Challenges Remain• Risk analysis and operation/response plans needed• Regulatory Approaches?• Public Safety Protection of the utmost importance• Public education and outreach is critical
Collaborators
• Hazen and Sawyer Water Reuse Practice Group
• Ben Stanford, Pat Davis, Kevin Alexander, Anni Luck, Troy Walker, Enrique Vadiveloo
• Many more…
• Hazen and Sawyer Applied Research Group
• Ben Stanford, Bill Becker, Wendell Khunjar, Nicole Blute, Troy Walker, Allison Reinert, Grace Johns, Ben Wright