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2. Agenda for LT2ESWTR Presentation. Overview of the LT2ESWTRCryptosporidium Monitoring and Implementation DetailsRelated Q
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1. Proposed Long Term 2 Enhanced Surface Water Treatment Rule
2. 2 Agenda for LT2ESWTR Presentation Overview of the LT2ESWTR
Cryptosporidium Monitoring and Implementation Details
Related Q&A
Microbial Toolbox
Other rule requirements
Related Q&A
3. Overview of the LT2ESWSTR
4. 4 Applicability and Purpose Applies to all systems using surface water or ground water under the direct influence of surface water
Supplements existing regulations by focusing on Cryptosporidium in systems with higher risk
Filtered systems with high source water occurrence
All unfiltered systems
Maintains microbial protection while systems address health risks from disinfection byproducts
5. 5 Existing Regulations IESWTR and LT1ESWTR
Require 2-log (99%) removal of Cryptosporidium in all filtered systems
Do not require treatment for Cryptosporidium in unfiltered systems, except through watershed control
Do not require existing finished water reservoirs to be covered
6. 6 New Data on Cryptosporidium Occurrence
Source water occurrence overall is lower than previously thought
However, relatively high levels in some filtered systems
Finished water occurrence typically higher in unfiltered systems
Infectivity greater than previously estimated
Effectiveness of treatment technologies including UV light and ozone
7. 7
8. 8 Source Water Monitoring at Large Filtered Systems (?10,000 People) Sample for Cryptosporidium, E. coli, and turbidity for 24 months
Two options for sampling frequency
Monthly OR
Semi-monthly (or more frequent)
Second round of monitoring six years after bin classification
Exempt if system provides at least 5.5 log Cryptosporidium treatment
9. 9 Bin Classification for Large Filtered Systems Determination of bin assignment depends on number of samples taken
For systems conducting monthly sampling, calculate running annual averages (RAAs) for Cryptosporidium and use the highest of these averages
For systems conducting semi-monthly (or more frequent) monitoring, calculate the mean concentration of all 48 (or more) samples
10. 10 Filtered System Bin Classification and Treatment
11. 11 Filtered System Bin Classification and Treatment Treatment requirements listed in table apply to systems using conventional, slow sand, or diatomaceous earth filtration
Based on assumption of 3 log average removal
Direct filtration systems must provide an additional 0.5 log Cryptosporidium treatment for Bins 2-4 (i.e., 1.5, 2.5, and 3.0 log)
Alternative filtration systems must provide total Cryptosporidium treatment of 4.0, 5.0, and 5.5 log in Bins 2-4 as determined by State
12. 12 Source Water Monitoring at Small Filtered Systems (<10,000 People) Initial E. coli screening analysis to determine if Cryptosporidium monitoring is required
Bi-weekly E. coli sampling for one year
If mean E. coli exceeds trigger value, then semi-monthly Cryptosporidium sampling for one year
Mean E. coli > 10/100 mL for lake/reservoir sources
Mean E. coli > 50/100 mL for flowing stream sources
Bin classification based on mean Cryptosporidium concentration
Systems below E. coli trigger levels incur no additional monitoring or treatment requirements
13. 13 Source Water Monitoring at Unfiltered Systems Large systems monitor Cryptosporidium at least monthly for 24 months
All small systems monitor Cryptosporidium semi-monthly for 12 months
E. coli and turbidity monitoring not required
Exempt if system currently provides at least 3 log Cryptosporidium inactivation
14. 14 Treatment by Unfiltered Systems All unfiltered systems must provide Cryptosporidium inactivation
If mean Cryptosporidium concentration is >0.01 oocysts/L, systems must provide at least 3 log Cryptosporidium inactivation
Otherwise must provide at least 2 log Cryptosporidium inactivation
Must use chlorine dioxide, ozone, or UV for Cryptosporidium inactivation
Must use two disinfectants for overall Cryptosporidium, Giardia, and virus inactivation
15. 15
16. 16 Estimated Impact of Rule Total annual costs for systems and States are estimated at $73 to 111 million
Up to 35 percent of systems are projected to add treatment
Mean annual household costs are $1.07 to $1.68
For households in systems adding treatment, median annual cost increase is $3.23
Benefits estimated as 260,000 to 1,020,000 cases of cryptosporidiosis avoided annually
From 37 to 141 associated deaths avoided
17. Cryptosporidium Monitoring and Implementation Details
18. 18 Monitoring Schedule Submit sampling schedule 3 months before beginning monitoring
Schedule must specify calendar dates when each sample will be collected
Calendar dates may vary a little from month to month
Collect sample within 2 days of the dates on the schedule
If system cannot sample on scheduled date due to dangerous or unforeseen conditions, then sample as close to date as feasible
If method requirements are violated, then collect replacement sample within 14 days of notification
19. 19 Analytical Method for Cryptosporidium EPA Method 1622 or 1623
Sample volume analyzed must be at least 10 L or packed pellet volume of at least 2 mL or volume passed through 2 filters
QC criteria include analysis of matrix spike samples initially and after every 20 samples from a given plant
Labs must be certified by EPA or equivalent State program
20. 20 Calculation of Sample Concentration Individual sample concentrations based on total number of oocysts counted in each sample (unadjusted for recovery), including empty oocysts and other oocysts that may not be viable
In samples where no oocysts are detected, concentrations are assigned a value of 0 oocysts/L
21. 21 Example Calculation of Bin Classification Applies to large filtered systems monitoring monthly
Calculate RAA for months 1-12
(0+0+0.1+0.1+0.2+0.1+0.1+0+0+0+0+0)/12 = 0.05
Determine RAAs for months 2-13, 3-14, 4-15 ...
22. 22 Example Calculation for Bin Classification (cont.) Determine maximum of all RAAs
Maximum annual average concentration is 0.075 oocysts/L
System is classified in Bin 2 (1 log additional treatment for conventional plant)
23. 23 Sampling Location Requirements Samples must be taken at intake prior to any treatment, except as described below
Systems that add chemicals at intake must sample as close to intake as possible, at similar depth and distance
Special directions for systems using bank filtration, off-stream storage, presedimentation, or multiple sources
24. 24 Source Water Sampling Location for Bank Filtration Processes
25. 25 Source Water Sampling for Raw Water Storage or Presedimentation Processes
26. 26 Source Water Sampling for Multiple Sources Must sample where the sources are combined, if sample tap is available
If combined source tap is not available then sample each source separately and determine a weighted average concentration using one of two methods (see next slide)
27. 27 Sampling for Multiple Sources Separately
28. 28 Grandfathering Monitoring Data for Bin Classification Existing Cryptosporidium data may be used for bin classification if approved by EPA
Data must meet same conditions as data collected under LT2ESWTR (i.e., same method, sampling frequency, sampling location, volume analyzed)
Systems with less than 2 years of existing data may use these data for bin classification but must conduct additional monitoring until they have a total of 2 years of data
29. 29 Implementation Support Large systems will report initial sampling schedule and monitoring results to EPA
Data system for electronic reporting and review of monitoring results
States will have full access to their systems’ data
Guidance manuals and help line will address sampling and analysis questions
Draft guidance available with proposal
Results from small system and from 2nd round of monitoring will be reported to States
Ongoing EPA laboratory certification program for Cryptosporidium analysis
30. 30 Related State Requirements Records Kept by States
Monitoring results and bin classification
Cryptosporidium treatment measures
Reports by States to EPA
Bin classification for each system
Special Primacy Conditions
How States will assess significant changes in source water as part of sanitary survey
31. 31 Requests for Comment Monitoring requirements for systems that use surface water for only part of the year
Grandfathering monitoring data that do not meet acceptance criteria
Monitoring for systems recycling filter backwash
Monitoring for new plants and sources
Treatment requirements for unfiltered systems with higher Cryptosporidium levels
See proposal for details and other issues
32. Questions?
33. Microbial Toolbox
34. 34
35. 35 Source Toolbox Options
36. 36 Pre-Filtration Toolbox Options
37. 37 Treatment Performance Toolbox Options
38. 38 Additional Filtration Toolbox Options
39. 39 Additional Filtration Toolbox Options (cont.)
40. 40 Inactivation Toolbox Options
41. 41 Additional Requirements for Unfiltered Systems Systems using chlorine dioxide or ozone may not fail to achieve required Cryptosporidium inactivation more than one day a month
Systems using UV must meet required Cryptosporidium inactivation for at least 95 percent of water delivered to public each month
42. Other Rule Requirements
43. 43 Uncovered Finished Water Reservoirs Compliance options (to be in place 36 months after promulgation)
Cover
Treat to achieve at least 4 log virus inactivation
Implement State-approved risk mitigation plan addressing access and site security, surface water runoff, animal waste, and ongoing water quality assessment
44. 44 Disinfection Profiling and Benchmarking Systems must monitor weekly for 12 months during peak hourly flow to determine Giardia and virus inactivation profiles
Existing profiles and historical operational data may be used if disinfection practices have not changed
Transient noncommunity systems are exempt
Small systems may be exempt based on disinfection byproduct levels and E. coli monitoring
45. 45 Disinfection Profiling and Benchmarking (cont.) Systems that plan to make a significant change in their disinfection practice must calculate a disinfection benchmark (from data collected during profiling) and notify State
Benchmarks are defined as the lowest mean monthly values of Giardia and virus inactivation
46. 46 Related State Requirements Records Kept by States
Systems required to cover or treat uncovered finished water reservoirs and systems with risk mitigation plans
Special Primacy Conditions
Approval of watershed control programs
Approval of “demonstration of performance” protocols
Approval of risk mitigation plans
47. 47 Related Requests for Comments For each microbial toolbox option: (1) Whether data support proposed credit and design/implementation criteria and (2) additional data on treatment effectiveness
For uncovered finished water reservoirs: alternatives to covering, including Cryptosporidium and Giardia inactivation, and how to define a finished water reservoir
48. 48 How to Submit Comments See the proposal (68 FR 47640, August 11, 2003) for directions on submitting comments electronically, by mail, or by hand delivery.
Comments must be submitted to EPA’s Docket
Supporting technical analyses can be acquired through EPA’s Docket
see http://www.epa.gov/edocket/
The 150 day public comment period for the LT2ESWTR ends January 9, 2004.
49. Questions?