February 15 - 18 , 2005 Meeting Agenda
FIFRA SCIENTIFIC ADVISORY PANEL (SAP)
FIFRA SCIENTIFIC ADVISORY PANEL (SAP)
February 15 - 18, 2005
FIFRA SAP WEB SITE http://www.epa.gov/scipoly/sap/
OPP Docket Telephone: (703) 305-5805
Docket Number: OPP-2004-0405
FRIDAY, FEBRUARY 18, 2005
Holiday Inn - National Airport
2650 Jefferson Davis Highway
Telephone: (703) 684-7200
N-METHYL CARBAMATE PESTICIDE CUMULATIVE RISK ASSESSMENT: PILOT CUMULATIVE ANALYSIS
SESSION 4: N-methyl Carbamate Exposure Assessment: A Pilot Case Study
- 8:30 A.M. Introduction and Identification of Panel Members - Steven G. Heeringa, Ph.D. (FIFRA SAP Chair)
- 8:40 A.M. Administrative Procedures by Designated Federal Official -Joseph E. Bailey
- 8:45 A.M. Opening Remarks - Tina Levine, Ph.D. (Director, Health Effects Division, Office of Pesticide Programs, EPA)
- 9:00 A.M. Introduction and Background - Anna Lowit, Ph.D. and David Miller (Health Effects Division, Office of Pesticide Programs, EPA)
- 9:15 A.M. Cumulative Exposure from N-Methyl Carbamates Pilot Analysis: A Case Study
Dietary Assessment, David Hrdy
- 10:00 A.M. BREAK
- 10:15 A.M. Cumulative Exposure from N-Methyl Carbamates Pilot Analysis: A Case Study (continued)
Residential Exposure Inputs, Jeff Evans
Residential Pesticide Use Data & Aggregate Exposure, Steve Nako, Ph.D.
Cumulative Exposure Assessment , David Hrdy
Model Comparison, Steve Nako, Ph.D.
Summary, David Miller
12:00 P.M. LUNCH
1:00 P.M. Questions to the Panel
There are several key principles for conducting a cumulative risk assessment. One such principle concerns the time frame of both the exposure (e.g., When does exposure occur? What is the exposure duration?) and of the toxic effect (e.g., What are the time to peak effects and the time to recovery? How quickly is the effect reversed?). Both should be adequately considered when performing a cumulative risk assessment so that an individual's exposure is matched with relevant and appropriate toxicological values in terms of duration and timing. There are several important considerations with respect to the temporal characteristics of the exposures and of the cholinesterase inhibitory effects of N-methyl carbamate pesticides in estimating their cumulative risk. OPP used a Relative Potency Factor (RPF) approach in this case study which is based on cholinesterase inhibition data from acute dosing studies performed in the rat. A similar approach was used in the organophosphorus pesticide cumulative risk assessment several years ago. This RPF approach expresses toxicity of each chemical in terms of "index chemical equivalents". In this approach, all exposure events within a day are adjusted by their RPFs and summed. The three exposure models (DEEM/Calendex, LifeLine, and CARES) used in the case study express exposure as a distribution of 1 day (24 hour totals) exposures within a population. Since AChE inhibition caused by the NMCs recovers rapidly (minutes to hours), it might be important to consider the intra-day timing of exposure events. Specifically, if the exposure events within a day are distributed sufficiently far apart in time so that significant recovery of AChE inhibition occurs between any two exposure events, then summing exposures over 24 hours might overestimate the risk associated with AChE inhibition. For example, if an individual consumed 200 mL of apple juice in the early morning, an additional 200 mL during the afternoon, and another 200 mL late at night, this could present a very different risk picture than if the total 600 mL were presumed to be consumed at one time. The current FCID database and the DEEM/Calendex, LifeLine, and CARES models are set up to consider food consumption on a per day (rather than per eating occasion) manner. Thus, the exposures reported in this case study reflect daily (24 hour) exposures. To the extent that a day's eating occasion events leading to high (total) daily exposure are close together in time, the RPF approach described in the case study provides reasonable estimates of risk. To the extent that eating exposure events leading to high total daily exposures are widely separated in time such that recovery of AChE inhibition occurs, the risks under the RPF approach in this case study may be overstated and a more sophisticated approach which accounts for intra-day eating patterns might be more appropriate. OPP has investigated the degree to which high-end exposures can be attributed to specific eating occasions (within a day) that occur either closely spaced in time or widely separated by time by looking at the actual individual consumption events as reported in the CSFII. Specifically, OPP has looked at the CSFII -based dietary records for individuals at several locations in the upper end of the exposure distribution to determine the extent to which these daily high-end exposures can be attributed to a single eating event, several eating events spaced closely in time (over several hours), or eating events widely separated by time (more than several hours). As described in Section IV.H of the case study document, OPP found that that a sizable fraction of daily records contributing to the upper tail of the food exposure distribution represent single eating occasions. Assuming that subsequent, more detailed and extensive analyses provide confirmation of these preliminary observations and analyses, OPP believes and that it is unlikely that any more sophisticated, temporal-based approach which better accounts for temporal separation of eating/exposure events will result in substantial or significant changes in OPP's risk estimates. Part A. EPA requests the SAP provide comments on this exploratory analysis with respect to its adequacy and appropriateness. Please also provide suggestions for future, more detailed analyses. Part B. Given the results of the initial exploratory analysis, EPA believes that a more sophisticated time-based intra-day model (e.g., PBPK in which the timing of intra-day eating events is explicitly incorporated) for exposures through the food pathway would not substantially change the assessment of potential risks through this pathway compared to the results produced using the RPF methodology used in the case study in which 24 hour food consumption data is used. Please explain why you agree or disagree.
3:00 P.M. BREAK
3:15 P.M. Questions to the Panel (continued)
A key concept that is unique to cumulative risk assessments is the concept of co- occurrence of residues (and thus co- or simultaneous exposure) to members of the Common Assessment Group (CAG). Specifically, a cumulative assessment must appropriately consider residues which co-occur in time and space since these exposures must by combined and considered jointly. This is true for exposures through the food pathway, the drinking water pathway, and the residential pathway. The USDA's PDP data program uses multi-analyte methods and thus simultaneously measures co-occurrent residues in samples. The generated drinking water concentrations from the PRZM-EXAMS model considered regional NMC use and usage practices and thus implicitly considered co-occuring residues.
Exposures through the residential pathways can also co-occur. One of the unique aspects of the NMC cumulative exposure assessment is the use of the Residential Exposure Joint Venture (REJV) data provides current information on co-occurrent use patterns for residential exposure. The US EPA National Home and Garden Pesticide Use Survey (NHGPUS) can also be used to develop residential use profiles. The PDP, PRZM-EXAMS, and REJV/NHGPUS data were used, to varying degrees, in this case study.
Please comment on the use of the pesticide use/usage data (e.g., REJV and NHGPUS) to account for co-occurring use patterns in assessing residential exposures.
The data sources and methodologies used in the N-methyl carbamate case study are similar in many respects to the data sources and methodologies used in the Cumulative Risk Assessment for the OP pesticides. For example, in both assessments the evaluation of exposure of the food pathway relied to a great extent on the USDA's PDP data, the evaluation of exposure through the water pathway used PRZM-EXAMS modeling data, and the evaluation of exposure through the residential pathway used standard SOP algorithms along with label information, professional judgments, literature values, and survey data (REJV, NHGPUS). Please comment on the data sources used in the cumulative exposure assessment and on how EPA has considered and incorporated the data. Does the SAP have any suggestions or recommendations regarding additional available data sources that EPA may wish to investigate?
5:30 P.M. ADJOURNMENT
Please be advised that agenda times are approximate. Because this is one 4-day meeting with four separate sessions, sessions will begin as the preceding session is completed, which could be the same day. For further information, please contact the Designated Federal Official for this meeting, Joseph E. Bailey, via telephone: (202) 564-8450; fax: (202) 564-8382; or email: email@example.com