| Introduction
to RISC WorkBench
RISC WorkBench 4.0 is an easy-to-use software package
designed for performing fate and transport modeling and
human health risk assessments for contaminated sites.
RISC WorkBench follows standard procedures outlined in
the US EPA's Risk Assessment Guidance for Superfund (US
EPA, 1989) to calculate exposure assessment, toxicity
assessment, and risk assessment. RISC WorkBench also
includes EnviroBrowser Pro, a completely customizable
database for common environmental parameters used when
conducting risk assessments. No other RISK package
offers all this!

RISC WorkBench
Interface
The RISC WorkBench follows a
logical menu structure that takes you through the
necessary steps to produce your risk analysis or
contaminant transport model run. Simply complete the 6
steps outlined in RISC WorkBench to obtain results
quickly. If you're not sure of an input parameter,
simply launch the chemicals or environmental parameters
database for a selection of common 'risk'
parameters!

Step 1: Select Chemicals of
Concern
| RISC WorkBench allows you to select
from over 86 common chemicals providing physical,
chemical, and toxicity values or add new
compounds. |
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| Chemical
Parameters |
Toxicity
Parameters |
• CAS Number • Molecular Weight •
Density • Vapor Pressure • Solubility •
Henry's Law • Log Kow • Koc • Kd •
Diffusion in Air • Diffusion in Water •
Vegetable Uptake Factor • Degradation
(high-end) • Degradation (low-end) |
• EPA Carcinogenic
Classification • Ingestion Slope Factor •
Inhalation Slope Factor • Dermal Slope
Factor • Oral Reference Dose • Inhalation
Reference Dose • Dermal Reference Dose •
Oral-Soil Abs. Adjust. Factor • Oral-Water Abs.
Adjust. Factor • Dermal-Water Abs. Adjust.
Factor • Inhalation Abs. Adjust. Factor •
Skin Permeability Coefficient • Maximum
Contaminant Level (MCL) |
Step 2: Define Exposure
Pathways
| In Step 2, the user may define the
exposure scenario by selecting contaminated
media(s), fate and transport models (if any), and
associated exposure pathways. RISC WorkBench is
set up so that in any single analysis, either
human health exposure pathways can be evaluated or
ecological/water quality concerns can be
evaluated. |
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Built-in Fate &
Transport Models include:
- Leaching from vadose zone to groundwater
- Dispersion, advection, retardation and degradation
of groundwater as it moves in an aquifer
- Saturated soil source at the water table impacting
groundwater
- Biodegradation of vapors in soil migrating to
indoor/outdoor air
- Emissions from groundwater to indoor air
- Surface water mixing and sediment partitioning
models that can be linked with groundwater
model
Step 3: Determine Receptor Point
Concentrations
| The third step is to determine
receptor point concentrations for the various
media of concern specified in Step 2. There are
two methods for determining receptor point
concentrations; the user can enter receptor point
concentrations directly into RISC WorkBench or
enter source zone concentrations and then utilize
chemical fate and transport models to estimate the
receptor point concentrations. The method(s) to be
used in Step 3 are determined by the choices made
in Step 2 |
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Step 4: Enter Surface Water
& Sediment Criteria
| In Step 4, the receptor(s) of
concern are chosen and the receptor-specific
intake parameters are entered. RISC WorkBench
contains both deterministic and stochastic (Monte
Carlo input) default data on exposure for many
different types of receptors. The user is free to
use the default data provided or to change the
intake parameters to reflect actual site-specific
values. |
 |
Step 5: Calculate Risk &
Cleanup Levels
| The potential carcinogenic risk and
non-carcinogenic hazard are calculated using
equations presented in EPA's Risk Assessment
Guidance for Superfund (EPA, 1989a). The following
exposure routes are considered in the software: |
 |
- Dermal contact with contaminated soil
- Ingestion of contaminated soil
- Ingestion of contaminated groundwater
- Dermal contact with contaminated groundwater
(while showering)
- Inhalation while showering
- Inhalation of outdoor air (either from soil or
groundwater emissions)
- Inhalation of indoor air (either from soil or
groundwater emissions)
- Ingestion of surface water (e.g., while
swimming)
- Dermal contact with surface water
- Ingestion of home-grown vegetables grown in
contaminated soil
- Ingestion of home-grown vegetables irrigated with
contaminated groundwater
- Ingestion of irrigation water (groundwater used
outdoors)
- Dermal contact with irrigation water.
- Inhalation of irrigation water spray (from
sprinklers, etc.)
Pathways 1-3 and 6-7 represent some of the more
common exposure pathways for many petroleum contaminated
sites (e.g., former gas stations). If surface water
bodies are present on the site, exposure pathways 8 and
9 may be important. Pathways 11-14 represent the
potential pathways associated with irrigation water and
will usually only be of concern if the house has its own
well while drinking water used in the house is provided
by a municipality.
Step 6: View the
Results
| When the "Calculate Clean-up
Levels" option is chosen from Step 5, RISC
WorkBench can be used to "back-calculate" clean-up
levels using the models and assumptions selected
in the current analysis. In the "forward risk"
assessment, risk is calculated from input or
estimated receptor point concentrations and
receptor input parameters. In the
back-calculation, the user specifies target risks
or concentrations (e.g., MCLs) and then the
software calculates "allowable" source
concentrations (clean-up levels). The clean-up
levels represent source and/or receptor point
concentrations for the chemicals of concern such
that the risk levels are not exceeded for the
scenario outlined. |
 |
There are several options for selecting targets in
Step 5. The user may specify a target risk or hazard
index either for individual chemicals or for a
cumulative scenario where the risks are summed across
all chemicals of concern. If groundwater or surface
water is a receptor media, the user may enter target
concentrations (e.g., MCLs in groundwater) for these
media.

RISC WorkBench
Output
RISC WorkBench Compared to the
RBCA ToolKit
While slightly similar to the
RBCA Toolkit, RISC WorkBench is more functional,
flexible and user-friendly. The major differences
are:
- RISC WorkBench is developed as a stand-alone
program with an intuitive graphical interface that
follows a step-by-step procedure. (Microsoft Excel is
only required when using the bonus Tier 1 spreadsheet
and Surface Water Quality database.)
- RISC WorkBench allows for pathway, compound, and
receptor additivity.
- The fate and transport models in RISC WorkBench
can be used in the presence of phase-separated
product.
- There is a vadose zone model in RISC
WorkBench.
- The groundwater models are transient.
- Probabilistic (Monte Carlo) exposure capabilities
are provided in RISC WorkBench.
- RISC WorkBench includes a critical pathway -
indoor showering - missing in the RBCA Toolkit.
- RISC WorkBench includes a customizable
environmental parameters database with references.

Risk
WorkBench Documentation
RISC WorkBench
includes a comprehensive user's manual containing three
in-depth example problems. Technical support is provided
by phone, fax or e-mail.

Risk
WorkBench Hardware Requirements
- IBM 486 or compatible (or a PowerMac)
- 8 MB RAM
- 12 MB hard disk space
- Microsoft Windows 95, 98, 2000 or NT
- Microsoft Excel 5.0 or 7.0 (for optional
spreadsheets only)
RISC WorkBench can be run without Excel, however,
this will prevent the user from displaying the bonus
RBCA Tier 1 table or accessing the full surface water
and sediment criteria databases.

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