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PRESTO

PRESTO  (Prediction of Radiological Effects Due to Shallow Trench Operations) is a computer model for evaluating radiation exposure from contaminated soil layers, including waste disposal, soil cleanup, agricultural land application, and land reclamation.

Download Information

The table below allows you to download both the programs and the user guides for Version 4.2 of  PRESTO-EPA-CPG /POP Operation System. The PRESTO-EPA-CPG/POP Operation System contains a family of PRESTO multimedia models:

  • PRESTO-EPA-CPG (Critical Population Group)
  • PRESTO-EPA-POP (Population) 

These documents are continuously being improved and we encourage you to comment on the effectiveness and applicability of this operation system. 

FILE
SIZE
DESCRIPTION
prestov4_2_m.exe 13.5MB PRESTO-EPA-CPG/POP Operating System Version 4.2, setup package
userguide1.pdf 647Kb PRESTO-EPA-CPG/POP Operating System Version 4.2, users's guide, main text
userguide2.pdf 647Kb PRESTO-EPA-CPG/POP Operating System Version 4.2, users's guide, appendices
dcom98.exe 1.17MB Microsoft patches for Windows 95 and 98
mdac_typ.exe 7.51MB Microsoft data access components 2.5 setup software for Windows 95 and 98 patches
readme.wpd 2.2KB PRESTO-EPA-CPG-POP Operation System installation instructions
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Background

These models are intended to support the development of EPA's environmental standards and criteria.  The initial models, published in 1987, were developed for a mainframe computer.  Subsequent versions were modified to operate on a personal computer in a DOS environment.  

  • PRESTO-EPA-CPG Operation System 
    • Version 2.0  published in 1993
    • Version 2.1 published in 1996
  • PRESTO-EPA-POP Operation System
    • Version 2.1 published in 1995 

The current Version 4.2 of the PRESTO-EPA-CPG/POP Operation System combines these two systems and operates in a Windows environment.  It also incorporates new features, including the addition of soil cleanup, agricultural land application, and land reclamation to the waste trench operation scenarios.  

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Application Niche

The models are designed to calculate the maximum annual committed effective dose to a critical population group and cumulative fatal health effects and genetic effects to the general population in several scenarios: 

  1. near surface disposal trench containing low-level radioactive waste  and/or naturally occurring or accelerator produced radioactive material (NARM) 
  2. residual radionuclides remaining in soil layers after cleanup 
  3. agricultural land application of technologically enhanced naturally occurring radioactive materials (TENORM) waste 
  4. stripped land reclamation with applied TENORM waste 

The models simulate the transport of radionuclides in air, surface water, and groundwater pathways, and evaluate exposures through ingestion, inhalation, immersion and external exposure pathways.

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Regulatory Context

EPA has used the PRESTO-EPA-CPG/POP Operation Systems extensively to generate dose and risk estimates to support the following EPA rules and reports:

  • Proposed Low-Level Radioactive Waste and NARM Rule submitted to OMB (1987)
  • Draft Naturally Occurring Radioactive Materials Report (1998)
  • Criteria to Evaluate Risk Assessment for Land Application of Alternative Uses of Phosphogypsum (1999)
  • Risk Assessment Modeling Analyses for the Land Application of Uranium TENORM (2000)
  • Proposed Low-Activity Mixed Waste Rule (2000)
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Strengths and Limitations

To avoid overly conservative results, EPA employed the following approaches:

  • a dynamic approach for the infiltration sub-model; 
  • a multi-phase leaching concept for the release sub-model;
  • realistic transition flow from vertical transport reach to horizontal transport reach for the groundwater sub-model; and
  • plausible scenario assumptions for the well mechanics sub-model.

Theoretically, a one-dimensional model can produce a significant amount of error relative to a three dimensional model; however, the magnitude of this error depends largely on the conditions of the application. A recent study indicated that under normal applications, this relative error may range from zero to 10 percent for the PRESTO-EPA-CPG and virtually zero error for PRESTO-EPA-POP.

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Verification, Validation And Peer Review

PRESTO-EPA-CPG and PRESTO-EPA-POP have been subjected to extensive quality assurance and peer reviews: 

  • extensive quality assurance review of the conceptual model, computational algorithms, computer coding, documentation, analysis scenario, and calculations results. (Inter System, Inc. -1983)
  • expert review of the PRESTO model focused on the conceptual model, the results of sample analysis, and documentation.  (42 experts from various institutions, including national labs, academic entities, industry, and international organizations -1984)
  • validation of dynamic infiltration sub-model against field study data collected for the Barnwell, South Carolina low-level radioactive waste disposal site by the U.S. Geological Survey (USGS) and the U.S. Nuclear Regulatory Commission (NRC)-1983
Results
Source
Inches/year
PRESTO analyses 13.8-17.7
USGS field data 14-17
NRC field data 14
  • analysis of the unique nature of the one-dimensional groundwater transport model, using Hung's correction factor to compensate the error induced from the diffusion term (published by "Nuclear and Chemical Waste Management" -1986)
  • review of several models proposed for use in regulatory analyses: PRESTO only model recommended for various types of analyses that supported licensing of low-level radioactive waste sites (Compacts Host State Technical Coordinating Committee-1989)
  • validation of the unique one-dimensional groundwater transport model, including the vertical transport reach, below contaminated site collection reach, and horizontal transport reach, against the three-dimensional MODFLOW-SURFACT model.  The relative errors for the peak concentration at the off-site well between the two models were less than 10 percent, with a best case reduced to 3 percent. (2000)
  • extensive test runs and subsequent reviews of conceptual model, numerical analysis algorithms, computer coding, and documentation, which resulted in several minor modifications.(EPA staff-2000) 

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Hardware Requirements
  • IBM-compatible personal computer
  • Pentium or equivalent capacity
  • 16 megabytes of RAM
  • 10 megabytes available hard disk space 
  • upgraded Windows 95, B version or newer, or 98, using: 
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Links to related information:
First of three links to related information Model Software Second of three links to related information CAP88 Third of three links to related information PRESTO

 


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