XVI World Water Congress May 31, 2017 Cancun, Mexico

Slides:



Advertisements
Similar presentations
Recreational Water Sampling. References A.Guidelines for Canadian Recreational Water Quality by Health & Welfare Canada 1992 B.CFP 213 CF Health Manual.
Advertisements

Agricultural Engineer Water Quality Specialist
ALLEN BERTHOLD TEXAS WATER RESOURCES INSTITUTE Water Quality and Copano Bay Watershed Efforts.
Fecal Colform Bacteria Contamination during Rain Events in Sayler’s Creek, Virginia Blake N. Robertson Senior Honors Research Under the Supervision of.
Bureau of Water Overview Wastewater issues Drinking water issues Wrap up topics.
Pathogen Removal or Inactivation Technical Advisory Panel Reclaimed Water Rule Jim McCauley (360)
Water Quality: Fecal Coliform How is water quality affected by interactions in a watershed?
Bureau of Water Program Overview Local Government Interest.
Testing Mason Pond. World Water Monitoring Challenge Kit.
Volunteer Monitoring of E. coli in Upper Midwest Streams: A Comparison of Methods and Preferences.
Texas Stream Team …is a joint partnership with Texas Commission on Environmental Quality, U.S. EPA Region VI, Texas State University-San Marcos, and numerous.
April 22, 2005Chester Creek Watershed TMDL Total Maximum Daily Load Chester Creek University Lake & Westchester Lagoon Alaska Department of Environmental.
Recreational Uses & Criteria Chapter TSWQS Changed the indicator bacteria from fecal coliform to E. coli in freshwater and Enterococci in.
Lecture ERS 482/682 (Fall 2002) TMDL Assessment ERS 482/682 Small Watershed Hydrology.
Water Supply & Management Obj: Discuss the nature, importance and sources of water.
BACTERIAL CONCENTRATIONS IN BULL CREEK AUSTIN, TEXAS Patrick Sejkora.
Measuring Stream Microbiology:
Department of the Environment Overview of Water Quality Data Used by MDE and Water Quality Parameters Timothy Fox MDE, Science Service Administration Wednesday.
TMDL – Fecal coliform Frank Henning UGA Watershed Extension Agent.
2011 Lower Basin Stakeholder Forum Nueces River Authority Feb 16, 2011 – Uvalde Feb 23, 2011 – Corpus Christi.
TMDLs on the Clearwater River Fecal Coliform Impairment of the Trout Stream Portion of the Clearwater River By Corey Hanson Water Quality Coordinator Red.
VIRGINIA’S TMDL PROCESS.
Hillsborough River Fecal Coliform BMAP Process Oct. 22, 2008.
2015 Environmental Trade Fair and Conference Jill Csekitz Technical Specialist TCEQ Monitoring & Assessment Section Devils River State Natural Area Image.
Basics Water quality – measurements and standards for safe drinking water and water that is conducive with a healthy ecosystem, Affects the number and.
Nature and Tourism The Beauty of the Natural World 1. What factors influence the number of tourists who will visit a destination?
Actions Taken After 2010 Swimmers are encouraged to use Sandy Beach 2014: Thunder Bay District Health Unit invokes the Ontario Beach Management Protocol.
Sandy Wingert February 25, 2010.
Fecal Coliform Aquatic Ecology.
BacteriALERT: A Program for Monitoring and Real-time Estimation of Indicator Bacteria By Stephen J. Lawrence, Atlanta, Georgia.
2011 Upper Basin Stakeholder Forum Nueces River Authority Feb 16, 2011 – Uvalde Feb 23, 2011 – Corpus Christi.
Restoring Water Quality: Using Nonpoint Source Funding to Improve Water Quality for Recreation Brooke Shireman Kentucky Division of Water.
Pine and Mill Creek E. coli Stakeholder Meeting Pine and Mill Creek E. coli Stakeholder Meeting Michigan Department of Environmental Quality, Water Bureau.
Major Watersheds in Alabama AWW across Alabama Cumulative (cao 3/2015) 79,900 Water Quality Records 64,260 Certified Monitors 2,290.
Kakanui Rachel Ozanne, Water Quality Scientist. Long-term (SOE) monitoring Water quality ~78 sites Monthly sampling.
2.4 Biological Parameters Micro-organisms that bring diseases are called “PATHOGEN”. Their quantities are very small compared to other micro-organisms.
Sources of Bacteria and their Variability in Urban Watersheds Robert Pitt Cudworth Professor Urban Water Systems Department of Civil, Construction, and.
QMRA Exercises. QMRA for Beach Exposure Given) An effluent from a municipal wastewater plant, which has a secondary treatment system, is released into.
Water Quality Testing. Testing of water is used to determine if water needs to be cleaned up.
All Sewers Lead to the Ocean Exploring and Measuring Stormwater Quality SciREN Coast February 12, 2015 Kellen Lauer and Kathleen Onorevole.
Commonwealth of Virginia Fecal Coliform Bacteria TMDLs Four Mile Run Public Meeting #1 June 14, 2001.
The Iowa Water Quality Standards: an overview Nutrient Science Committee June 13, 2007 John Olson Watershed Monitoring & Assessment Section Iowa DNR.
BTEC 223 Lab Exercise Water Module
Sustainable Development Goal for Water: Indicator 6.3.2
Chapter 14 Water Pollution.
Freshwater Attributes
Water Quality & micro-organisms
Mulberry River Watershed
An Efficient Cost Effective System for Wastewater Effluent Reuse
Dr. Alice Ortmann University of South Alabama Dauphin Island Sea Lab
VIRGINIA’S TMDL PROCESS Four Mile Run Bacteria TMDL March 25, 2002
Using Bacterial Source Tracking to Develop Watershed Restoration Plans
Water Quality.
Module 24 Ambient Water Quality Criteria for Bacteria
Water Pollution and Treatment
Total Maximum Daily Loads Development for Holdens Creek and Tributaries, and Pettit Branch Public Meeting March 26, 2008.
Requirements to produce high quality water
Infectious Agent : Pathogens
Tim Cawthon TCEQ Nonpoint Source Program
Total Maximum Daily Loads of Fecal Coliform for the Restricted Shellfish Harvesting/Growing Areas of the Pocomoke River in the Lower Pocomoke River Basin.
Recreational Water Quality Standards, Bacteria Monitoring Chesapeake Bay Program Living Res. Analysis Workgroup Tidal Monitoring Analysis Workgroup.
Warmup 10/22/12 As the population of Durham increases…
Surface Water Ambient Monitoring Program
Results of breakout group
Water quality.
Chapter 14 Water Pollution.
Vimal N. Soomai Undergraduate(Environmental Health Science Major)
Water Quality United States
Marco island water quality monitoring
USES OF DOMESTIC RECLAIMED WATER
Presentation transcript:

XVI World Water Congress May 31, 2017 Cancun, Mexico Application of Consistent Contact Recreation Water Quality Standards Across Hydrological Extremes: Reasonable or Ridiculous? XVI World Water Congress May 31, 2017 Cancun, Mexico Dr. Lucas Gregory Research Scientist Texas Water Resources Institute Co-authors: Stephen Muela & Dr. Kevin Wagner

Water Quality Standards Describe desired condition of waterbody Form legal basis for controlling pollution Advise user of potential health risks Consist of: Designated Uses Numeric Criteria Antidegradation Requirements General Policies

Contact Recreation Primary contact – activities with presumed significant risk of water ingestion Swimming, children wading, water skiing, surfing, diving, tubing, whitewater sports (kayaking, rafting) Secondary contact 1 – commonly occurring activities with limited body contact; less ingestion risk than primary contact Adults wading, fishing, canoeing, kayaking, boating Secondary contact 2 –limited body contact activities with less ingestion risk due to physical waterbody characteristics and limited access Fishing, canoeing, kayaking, boating Noncontact – activities with no significant risk of ingestion; where activities should not occur due to unsafe conditions Birding, hiking, biking; contact prohibited by law

Recreation Types

Protecting Human Health Contact recreation standards provide reasonable assurance that human health risk from fecal pollution is acceptable Feces contains Pathogens including cryptosporidium, pathogenic E. coli, and giardia Non-pathogenic organisms: many strains of E. coli and fecal coliform E. coli commonly used as Fecal Indicator Bacteria Presence of Fecal Indicator Bacteria in water considered indicative of recent fecal contamination Concentrations correlate to human health risk

E. Coli Fate in the Environment E. coli can survive for a period of time outside of the host organism in soil, water, sediment Survival influenced by temperature, moisture level, available nutrition, salinity, solar radiation, and predation levels Levels of each vary in soil, water, and sediment Long-term survival has been documented in all environments E. coli may not be associated with recent contamination events Surviving E. coli can contribute to measured quantity in water samples Baseflow contributions ~90% Stormflow increases of ~ 2 orders of magnitude

Contact Recreation Standards Application in Texas E. coli Public Lakes Rivers Creeks Enterococcus Bays Estuaries No considerations for flow condition No risk conferred to the person recreating due to type of activity No consideration of use type relative to flow conditions

Navasota River Case Study 5 ft/s and depth of 2 ft is unsafe for wading anything above 10ft2/s is dangerous

Hydrologic Conditions Change Recreation

Policy Recommendation Risk based water quality standard Consider the number of people engaged in recreation, appropriate type of recreation, and flow condition Example considering 5,000 swimmers and only 50 whitewater rafters per year Illness rate/1000 people = [Log(E.coli geometric mean)-1.249]/0.1064 At 126 cfu/100 mL E. coli concentration: 40 swimmers get sick; only 0.4 whitewater rafters get sick Applying less restrictive standard to rafting conditions only still yields adequate human health protection At 630 cfu/100 mL: only 0.72 whitewater rafters get sick

Implications Requires more data: water quality and recreation use Must consider type and levels of waterbody use People will assume increased level of risk when recreating Can reduce the number of waterbodies considered impaired Can reduce costs for restoring impaired waterbodies

Questions? Lucas Gregory LFGregory@ag.tamu.edu