SLIDE 1 Trends In Indirect and Direct POTABLE REUSE IN THE UNITED STATES California WateReuse Association Central Valley/Sierra Foothills Chapter Central Valley/Sierra Foothills Chapter
July 18, 2013 George Tchobanoglous
Department of Civil and Environmental Engineering University of California, Davis
SLIDE 2 Topics
- Types of reuse accepted worldwide
- Reuse: Projected worldwide growth
- Indirect and direct potable reuse
- Treatment technologies
- Treatment technologies
- A Southern California Case Study
- Regulatory framework
- Need for uniform accepted vocabulary
SLIDE 3
TYPES OF REUSE ACCEPTED WORLDWIDE AND PROJECTED AND PROJECTED GROWTH
SLIDE 4 Types of Reuse Worldwide
- Agricultural irrigation (seasonal demand)
- Landscape irrigation (seasonal demand)
- Industrial (constant demand, site specific)
- Non-potable urban uses (limited volumes)
- Recreation/environmental uses (site specific)
- Recreation/environmental uses (site specific)
- Indirect potable use through groundwater
recharge (requires suitable aquifer)
- Indirect potable use through surface water
augmentation (availability of reservoir sites)
- Direct potable use (best option, but public
perception issues must be dealt with)
SLIDE 5 Reuse Market Size and Growth 2008
15 20 25 30
mand, 10
6 m 3/d
East Asia and Pacific North America Middle East and Africa
Source: GWI Global Water Market 2008
5 10
2006 2008 2010 2012 2014 2016 2018 Water dem Year Western Europe
SLIDE 6 Driving Forces for Direct and Indirect Potable Reuse
- The value of water will increase significantly in the
future (and dramatically in some locations)
- De facto indirect potable reuse is largely
unregulated (e.g., secondary effluent, ag runoff, urban stormwater, highway runoff)
- Infrastructure requirements limit reuse opportunities
- Infrastructure requirements limit reuse opportunities
- Existing and new technologies can and will meet the
water quality challenge
- Population growth and global warming will lead to
severe water shortages in many locations. A reliable alternative supply should be developed
- Must think differently about water
SLIDE 7 De Facto Indirect Potable Reuse
Courtesy City of San Diego
SLIDE 8
Definition of Planned Indirect and Direct Potable Reuse
SLIDE 9 De Facto and Indirect Potable Reuse
(existing in fact, whether recognized legally or not)
OCWD Groundwater Buffer Upper Occoquan, San Diego, CA (Proposed) Surface Water Buffer
SLIDE 10
TYPES OF PROJECTS
SLIDE 11
Infiltration Basin, Florida, USA
SLIDE 12
SLIDE 13
Kraemer/Miller Spreading Basins, OCWD and Legacy Regulations
SLIDE 14
Barrier Injection Wells
SLIDE 15
Groundwater Injection Wells
SLIDE 16 Indirect Potable Reuse Through Surface Water Augmentation: San Diego, CA
Courtesy City of San Diego
SLIDE 17
San Vincente Reservoir, San Diego County
SLIDE 18
San Vincente Reservoir, San Diego County
SLIDE 19
TRENDS IN TREATMENT TECHNOLOGIES
SLIDE 20 Existing and New Treatment Technologies
- Technologies for the removal of BOD,
TSS, nutrients, and pathogens
- Technologies for the removal of TDS,
trace constituents, and unknowns
- Brine management for inland locations
- TREATMENT IS NOT THE ISSUE
SLIDE 21 What Are Others Doing?
- Windhoek, Namibia
- Pure Cycle Corporation
- International Space Station
- Cloudcroft, New Mexico
- Big Spring, Texas
- Orange County Water District
- Alternative Treatment Processes
SLIDE 22
Treatment Process Flow Diagram Windhoek, Namibia
SLIDE 23
Treatment Process Flow Diagram Pure Cycle Corporation (c.a. late 1970s)
SLIDE 24
Treatment Process Flow Diagram Pure Cycle Corporation (c.a. late 1970s)
SLIDE 25
Urine Treatment Process Flow Diagram International Space Station (c.a. 2011)
SLIDE 26
Treatment Process Flow Diagram Cloudcroft, NM (c.a. 2011)
SLIDE 27
Treatment Process Flow Diagram Big Spring, Texas (c.a. 2011)
SLIDE 28 Technologies for the Removal of TDS, Trace Constituents, Unknowns
Adapted from OCWD
SLIDE 29 Microfiltration, Cartridge Filters, Reverse Osmosis, and Advanced Treatment (UV), OCWD
SLIDE 30
Impact of Recycle Flows on Nitrogen Removal
Return flows contain nitrogen
SLIDE 31
Brine Management: Concentration with Falling-Film Evaporator
SLIDE 32 Technologies for the Removal of Trace Constituents and Unknowns
Adapted from Sundaram et al., 2009
SLIDE 33 Comparison of Technologies for the Removal of Trace Constituents & Unknowns
Item MF-Ozone-BAC MF-RO-UV/Peroxide Fate of trace organics Degraded Removed and degraded Reject/side streams Minor (periodic backwash water) Major (up to 20%) Salinity Unchanged Decreased significantly
Adapted from Sundaram et al., 2009
Salinity Unchanged Decreased significantly Corrosivity Unchanged Increased (requires buffering) Energy consumption without MF 0.03 - 1.0 kWh/m3 8 - 10 kWh/m3
SLIDE 34
Alternative DPR Flow Diagrams With and Without Reverse Osmosis With Engineered Buffer
SLIDE 35
SOUTHERN CALIFORNIA CASE STUDY CASE STUDY
SLIDE 36
DPR Opportunities for the Future: The Southern California Example
SLIDE 37 Electric Power Consumption in Typical Urban Water Systems
System Power consumption, kWh/Mgal Northern California Southern California
Supply and 150 8,900 Supply and conveyance 150 8,900 Water treatment 100 100 Distribution 1200 1200 Wastewater treatment 2,500 2,500 TOTAL 3,950 12,700
SLIDE 38
DPR Opportunities for the Future: The Southern California Example
SLIDE 39 Water Use By County in Southern CA
Item
Quantity, Mgal/d
Los Angeles Orange San Diego Riverside San Bernardino
Population, 9,935 2988 2933 1946 1964 Population, 1000’s 9,935 2988 2933 1946 1964 Groundwater 331 49 75 86 77 Surface water 1529 335 356 349 287 Total 1860 384 431 435 364
SLIDE 40
Wastewater Management Infrastructure
SLIDE 41 Benefits of the Southern California Example
- Reliable alternative source of supply, more secure
from natural disasters
- Lower cost and reduced energy usage
- More water available for agricultural use, especially
during drought periods during drought periods
- Environmental benefits for bay delta habitat
restoration
SLIDE 42
REGULATORY REQUIREMENTS
SLIDE 43 Science Versus Regulations
Pre 1880s Physical observations - No Science - Common sense practices (regulations) Enlightenment 1880-1980s Science develops - Semi-scientific, observational, and empirical regulations follow empirical regulations follow Post 1980s Science leaps ahead - Science based regulations have evolved, but have not kept pace - Semi-empirical and empirical legacy regulations persist. .
SLIDE 44
NEED FOR UNIFORM ACCEPTED TERMINOLOGY TERMINOLOGY
SLIDE 45 Need for Accepted Vocabulary
Issues
- There is a need to speak with one voice
- Not everyone agrees that indirect potable reuse is
acceptable
- Little standardization of terms (e.g., indirect and
direct potable reuse) direct potable reuse) Consequence
- Everyone says whatever suits their particular interest
- The public is confused, especially about the safety of
reclaimed water.
- A uniform vocabulary is of critical importance, if reuse
projects are to be discussed rationally
SLIDE 46 Closing Thoughts
- Direct (and indirect) potable reuse will be a critical
element in the development of sustainable strategies for water resources management
- Technology is now available to produce water for
any use including direct potable pipe to pipe reuse any use including direct potable pipe to pipe reuse
- Must resolve disconnect between existing
standards and regulations and scientific findings
- In promoting water reuse, the profession must
speak with a unified vocabulary
SLIDE 47
THANK YOU FOR LISTENING LISTENING