"Ah, at last, the perfect
                                              spot to review my VL &
                                              VU reports!"
                                                                ICR Update
                                                             Jim Walasek, Editor
                                                          Technical Support Center
                                                                    May 1998
Here  Comes  Summer!
ICR Update ISSUe Number 11 - This information sheet, the ICR Update,
is the eleventh one to be issued by the Technical Support Center (TSC) of the Office of Ground
Water and Drinking Water (OGWDW).  Future issues will be distributed as needed to maintain
information flow related to the ICR.
          Editor's Note: April 30th marked the end of the A-Team's involement in the ICR.
          A message will remain on their 800 number until May 31st directing people with
          questions about the ICR to the Safe Drinking Water Hotline at 800-426-4791.  The
          hotline will be able to help you or direct you to people who can.
                            A Tip Of the Old Hat - The A-Team was
                            instrumental in getting the ICR off the ground. Composed
                            of a group of drinking water experts, they helped with the
                            development of the sampling schematics, Initial Sampling
                            Plans, and provided technical assistance to utilities as they
                            got involved with the sampling phase of the ICR. However,
                            effective April 30th the A-Team ceased operation. The
                            Technical Support Center staff thanks the entire A-Team
                            staff for a job well done. The A-Team was made up of the
following individuals: Michael J. McGuire, Louis A. Briganti, David A. Cornwell, Kevin Dixon,
Ellen P. Flanagan, Judy Musgrove, Eva Nieminski, Douglas Owen, Jeffrey Rosen, Charlotte D.
Smith, Barbara Spade, and Anne M. Sandvig. Thanks again, we couldn't have done it without
your help!

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 Chemistry PE Study ReSUltS -Laboratories that are approved to perform
 disinfection byproduct (DBF) and/or surrogate (TOC, UV, Br, and TOX) analyses for the ICR
 must successfully participate in six quarterly PE studies. PE Study 7, the fourth of the six
 "required" PE studies, was sent to 203 participating laboratories the week of March 30*.
 Analytical results are due at EPA on or before May 5th.


 Data Upload Begins! - All laboratory quality control (QC) diskettes for the July
 and August  1997 sampling periods were uploaded to the ICR Federal database (ICR FED).
 Laboratory QC validation was successfully run and QC failure (VL) reports were printed and
 mailed to laboratories. They have been instructed to review the printed reports, correct any data
 entry errors, but to not resubmit data until water utility data is uploaded, QC failure (VA) reports
 are printed, distributed and reviewed. Utilities will then receive a set of "VU-" reports after
 laboratories have an opportunity to resubmit data disks to EPA.  Thank you.


 V U   C_> A U 1 J.OJN ! - Quality assurance procedures were developed for the ICR
 monthly sample data which include validation of the data that are submitted to EPA on the
 monthly diskettes from laboratories and utilities.  (NOTE: Validation is the term that EPA uses
 to describe the application of computer algorithms to the data reported to EPA to ensure data
 meets the QC criteria that are detailed in the ICR.manuals. - see ICRUpdate.7, Reports, Reports,
 Reports.)

    When you start to receive reports from EPA, you will notice that "cautionary" language is
 included above the header of some of the VU reports indicating the data in the report has not
 undergone final validation by EPA.  Remember, the ICR data is only considered validated once
 EPA has processed the resubmitted data from the laboratories and utilities. The validated data
 will reside on the EPA computer and the public will have access to the  ICR validated data as
 soon as possible.  Be assurred that any data approved by ICR FED during final lab/utility
 validation will not be changed without your prior notification. Of course, EPA encourages each
 water system to inform its customers of its ICR results , especially data that may be considered
 "controversial."

    EPA added the cautionary language to the VU reports so anyone reviewing the reports will
 be made aware that the data can "change" as a result of laboratories or  utilities correcting data up
 until final validation by EPA. If requested, EPA must provide copies of the VU reports when the
reports are available, and prior to EPA processing resubmitted data from utilities and
 laboratories. We understand that some stakeholders are very interested in reviewing whatever
 ICR data are available, even if the data have not been through the validation process.
Furthermore, in the current climate of open communication with the stakeholders, EPA is
 obligated to provide the requested data. Therefore, it is very important  that utilities provide their
ICR results to their customers as soon as possible so customers are not "surprised" by
preliminary ICR results from other stakeholders. However, as agreed upon with the
stakeholders, EPA will not release summaries of data before final validation because EPA is
committed to following the QA procedures laid out in the ICR regulation.

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     The general cautionary language for the VU reports is stated below:

     CAUTION: This data has not been validated by EPA and, therefore, could change upon final
     validation. It has not undergone the rigorous quality assurance review and validation procedures
     established for the ICR. This data should not be used for site specific compliance or public health
     assessments. The validated data will be used for rule development and research purposes only.

     Additional cautionary language for the VU reports containing disinfection byproduct
results is:

     Please note that TTHM, HAA, and bromate proposed regulatory standards are calculated quarterly
     based on a running average of 4 quarterly sampling events.  Therefore, even future compliance
     assessments cannot be determined based upon this report alone.

     The additional language for VU reports containing microbial results is:

     The current ICR method for detecting Giardia and Cryptosporidium has significant technical
     limitations. The primary limitation is the method's low and variable recovery. In addition, the ICR
     method cannot determine whether these organisms are alive or dead or could cause illness.

What do our protozoa and virus data  mean?  -utilityand
EPA Regional personnel have contacted.us.ivitkjquestions about howio.interpret the data they
will be receiving from the ICR for protozoa and virus.  Questions primarily center on method
recovery and precision and how they impact data interpretation and what can be inferred about
health risk to utility customers.

     The ICR was designed to support national regulatory impact analysis. The data were not
intended to provide informational value regarding occurrence or treatment effectiveness at
individual sites. EPA recognizes that determinations may represent overestimates at some sites
and underestimates at others. However, EPA believes that with regard to overall national
estimates these will average-out. Great care must be taken when trying to interpret individual
results.

PROTOZOA

•    Cryptosporidium parvum and Giardia lamblia are protozoan pathogens (disease-causing
    organisms) found in most surface waters.

•   If infectious protozoans are ingested, they may cause diarrhea and abdominal cramps.

•   Although Giardia cysts and Cryptosporidium oocysts are usually removed by filtration,
    some cysts may pass through the filtration process. Disinfection will often effectively kill
    Giardia cysts depending on the type, dosage and contact time of the disinfectant, and the
    water temperature. Cryptosporidium, however, is very resistant to disinfection and even a
    well-operated plant cannot ensure that drinking water will be completely free of this

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      parasite.

      The ICR protozoan method measures the approximate concentrations of Giardia and
      Cryptosporidium cysts and oocysts.  However, the method cannot determine if the
      organisms are alive and possibly harmful or dead and harmless. Therefore, caution must be
      used when interpreting results.

 •    Due to limitations of the method, if cysts and oocysts are not detected, one cannot conclude
      that they were not present and therefore, negative ICR protozoan data do not provide
      assurance that the source water is clean.

      Positive results can indicate that cysts and oocysts may be present in the water. However,
      they do not indicate the particular species of Giardia or Cryptosporidium, nor do they
      indicate whether they are alive or harmful.

 •    Limitations of the method are such that comparisons between individual samples are
     unreliable. Thus, comparisons between sampling dates or between raw and finished water
     samples are highly uncertain. Because microorganisms are not evenly distributed in water,
     representation of water quality for a given site is only possible with large numbers of
     samples.

     EPA, in partnership with the Centers  for Disease Control and Prevention, has prepared
 optional public notice language for systems that detect Cryptosporidium in their finished water
 and wish to notify the public. This information is posted on the OGWDW homepage at
 http://www.epa.gov/OGWDW/icrjnot.html.

      For more  information, please refer to "Cryptosporidium and Water: A Public Health
 Handbook" and "Cryptosporidium: Answers to Questions Commonly Asked by Drinking Water
 Professionals,"  which are available from the American Water Works Association for $35-$40.

 VIRUS

      Viruses which infect humans may be present in waters as a result of fecal contamination
      and may cause a variety of symptoms including diarrhea, vomiting and nausea. In rare
      cases, exposure may lead to more serious diseases.  Most viruses should be easily killed by
     chlorine and other disinfectants.

•    The ICR virus method does not detect all viruses, and not all detected viruses are
     pathogenic to humans. Although a positive result may indicate that fecal contamination is
     likely, it does not necessarily signify  that pathogens are present. As with the protozoa, a
     negative result does not necessarily mean that viruses are absent. Therefore, caution must
     be used in interpreting results.

     The results are expressed as MPN (most probable number)/! 00 L which is a statistical
     estimate of the concentration. MPN assays, inherently have a high degree of variability.

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     In summary, ICR monitoring will result in a large body of microbial data which will be
considered on a national basis to develop future regulations. ICR protozoa and virus monitoring
was not designed to determine individual treatment plant efficiencies or product water safety.

     In responding to inquiries from their customers, utilities which are members of the
Partnership for Safe Water may wish to point out that they are taking steps toward continuous
performance improvement and improved protection of their customers from waterborne diseases
through their Partership activities.

     I hope this information helps you to appropriately interpret your ICR protozoa and virus
results.  If you have additional questions, please call the Safe Drinking Water Hotline at
800-426-4791 or refer to the fact sheets on the Internet at http://www.epa.gov/OGWDW/
icr_hotl.html and the joint EPA/CDC "Guidance for People with Severely Weakened Immune
Systems" at http://www.epa.gov/OGWDW/crypto.html.


And They're Off! - The deadline to start the ICR treatment studies was April
14th, and all utilities required to conduct these studies have submitted study plans which have
been approved by EPA. Thanks for your timely submissions! In general, the study plans
showed a good understanding of the treatment study requirements.  Now the real fun starts as the
studies get underway! As you get started with these studies, remember to consult the two
documents that outline the treatment study protocols and reporting requirements: The ICR
Manual for Bench- and Pilot-Scale Treatment Studies (EPA 814-B-96-003, April 1996) and the
ICR Treatment Studies Data Collection Spreadsheets User's Guide (EPA 815-B-97-002, April
1997) Also, technical assistance is available through the Safe Drinking Water Hotline,
800-426-4791.


Treatment Studies/SDS  Testing - in past issues of the ICR update, we
have discussed the importance of the simulated distribution system (SDS) test during the ICR
treatment studies; however, there  still seems to be some confusion  regarding the use of free
chlorine vs. chloramines. The solution to this issue is very straightforward: only free chlorine is
to be used during SDS tests conducted during treatment studies, regardless of the disinfectant
that is used in full-scale treatment! A free chlorine residual must be present at the end of the
SDS incubation period, and there  should not be a combined residual present. If ammonia is
present in the water, breakpoint chlorination must be practiced to completely satisfy the ammonia
demand and achieve a free chlorine residual. Plants that use chloramines in the full-scale plant
should target a free chlorine residual of 0.5 to 1.0 mg/L at the end of the SDS incubation period.

     The objective of the treatment studies is to evaluate the ability of GAC and membranes to
control DBP formation by removing the precursors, and the SDS test is used to assess the
concentration of precursors in the influent and effluent from the advanced treatment process.
Specifically, the influent and effluent samples will be chlorinated under SDS conditions and
trihalomethanes (THMs), haloacetic acids (HAAs) and total organic halides (TOX) will be

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       measured at the end of the incubation period. Since, these DBFs to not form at appreciable
       levels when natural organic matter is reacted with chloramines, it is necessary to use free
       chlorine in the SDS test to accurately assess the precursor concentrations for THMs, HAAs and
       TOX. Furthermore, the use of free chlorine in the SDS test will result in a "worst case"
       assessment of DBF formation relative to the use of chloramines.  Finally, comparison of DBF
       formation and precursor removal will be more straightforward since all utilities conducting
       treatment studies are using free chlorine in the SDS test.

             Additional information regarding SDS testing conducted during treatment studies can be
       found in Section 4.6, Part 1 of the ICR Manual for Bench- and Pilot-Scale Treatment Studies
       (EPA 814-B-96-003, April 1996) and in the ICR Treatment Study Fact Sheet: The Simulated
       Distribution System Test (EPA 815-F-97-002, November 1997). This fact sheet can be found on
       the Internet at http://www.epa.gov/OGWDW/ficr_sds.html.


       •M-,-K. JL/Hui AHalySlS  - Data extraction joint requirements planning (JRP) meetings
       were held at the EPA Systems Development Center (SDC) in Arlington, Virginia on February
       20,1998 and on April  14-16,1998. Participants at these JRPs were from the EPA, the drinking
       water industry and SDC staff. The objective of these meetings-was to define all data extractions
       needed to facilitate ICR data analysis to support the M/DBP rule development process. The data
       will be extracted in an  organized manner to facilitate data analysis using Microsoft Access
       software. The participants agreed on the data elements that needed to be extracted and on the
       organization of the data elements in auxiliary databases.  SDC staff are finalizing the
       requirements documents prior to the design phase of the auxiliary databases which will be held
       June 15-18,1998.  We will periodically report on the ICR data analysis process in future issues
       of the ICR Update.
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