User:Debra Tabron/sandbox

The Training Range Environmental Evaluation and Characterization System (TREECS™) was developed for the Army to forecast the fate of and risk from munitions constituents (MC), such as high explosives (HE) and metals. TREECS™ is general enough that it can also be used for other types of contaminants and (non-Department of Defense) sites. TREECS™ has been validated as a valuable resource for predicting contaminant exposure in soil, groundwater, and surface water. This capability will allow stakeholders to forecast exposure risks as well as evaluate various management alternatives and best management practices (BMPs) to avoid or reduce such risks.

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CONTRIBUTOR(S): Dr. Mark S. Dortch, PE, D.WRE and Dr. Billy E. Johnson

Key Resource(s): Dortch, M.S., and B.E. Johnson. 2016 Draft. Field Demonstration and Validation of TREECS™ for the Risk Assessment of Contaminants on DoD Ranges, ESTCP, 2016.

Introduction

There is a need to sustain training and firing ranges while complying with requirements to protect the environment from MC residue that can pose health concerns to human and ecological receptors outside of installations. Models are required for predicting the fate of MC so that environmental specialists can estimate if and when MC residue could pose a concern and to evaluate alternatives for managing MC exposure.

TREECS™ is a client-based modeling software system developed for personal computers. Figure 1 is a home screen shot of the software with application to Ft. Leonard Wood, MO. TREECS™ that includes time-varying contaminant fate/transport models for soil, vadose zone, groundwater, and surface water to forecast MC (or other contaminants) export from ranges (or other source areas) and resulting exposure concentrations in each medium. TREECS™ is a system of numerical models that allows environmental specialists to readily assess migration of MC, as well as other contaminants, to determine if and when there could be risks to human and ecological receptors down-gradient of ranges and source areas. Additionally, TREECS™ can be used to evaluate BMP alternatives where concentrations presently exceed (or are predicted in the future to exceed) protective action limits (PALs) for human and ecological health.

A detailed description of TREECS™, as well as its performance, is provided by Dortch et al., 2013. Furthermore, its development is documented in a series of technical reports. Development of BMP capabilities is documented by Dortch et al., 2013. There is also a user’s.

Figure 1. TREECS main screen as it appears for an application involving GIS data.

TREECS™ Capability Levels

TREECS™ was developed with three levels of capability:

1. Tier 1 consists of screening-level methods that assume conservative, steady state contaminant loading and fate. It requires minimal input data requirements and can be quickly applied by environmental specialists to assess the potential for contaminant migration into surface water and groundwater. If predicted surface or groundwater concentrations exceed PALs at receptor locations, then further evaluation with Tier 2 is recommended to obtain more definitive results.
2. Tier 2 provides time-varying analyses and solves mass balance equations for both solid and water-dissolved phases. Additionally, MC or contaminant loadings to the soil or source area can vary from year-to-year based on site use. Media concentrations computed should be closer to those expected under actual conditions and lower than those computed with Tier 1 due to attenuation.
3. Advanced Tier 2 is the third capability level. It uses a visual, object-oriented user interface for setting up more complex contaminant environmental media pathways, such as runoff to a surface water stream that recharges an aquifer, such as at Marin Base Camp Pendleton, CA. The conceptual site model (CSM) and the Advanced Tier 2 setup at Marin Base Camps are shown in Figures 2 and 3, respectively.

Figure 2. Conceptual Site Model used with TREECS™ Advanced Tier 2 for the Zulu Impact Area (ZIA) and receiving waters, Camp Pendleton, CA. The area of interest (AOI) is the ZIA.

Figure 3. CSM as modeled in TREECS™ with Advanced Tier 2 option for Camp Pendleton, CA.

TREECS™ Additional Features

TREECS™ contains fate models for soil, vadose zone, groundwater, and surface water that can be connected in various manners to represent a variety of exposure pathways. The system and its models have graphical user interfaces (GUIs) for expediting model setup, and there is a Geographic Information System (GIS) to facilitate site applications and input development. There are three databases for providing physicochemical properties. There is a health benchmark database to provide PALs based on recommendations by the Department of Defense (DoD) Range Munitions Use Subcommittee (RMUS). There is also an MC residual mass loadings module and munitions database for estimating MC loadings onto ranges based on types and number of munitions fired. BMP modules can be used for evaluating strategies to reduce or avoid future contaminant exposure and risk.

TREECS™ Applications

TREECS™ was initially validated for sites at Fort A. P. Hill (VA), U.S. Military Academy (West Point, NY), Ft. Jackson (SC), and Camp Edwards, Massachusetts Military Reservation (MMR). Additional validation work was performed as part of ESTCP Project ER-201435 that included additional applications at West Point and MMR as well as Marine Base Camp Pendleton (CA). Example validation results for the high explosive RDX in groundwater at MMR are compared with observed RDX concentrations in Figure 4. The model’s 95% confidence limits due to uncertainty of the RDX degradation rate are also shown.

Figure 4. Computed and measured groundwater concentrations of RDX at MW161 down gradient of Demolition Area 2, MMR, with upper (UCL) and lower (LCL) confidence limits for uncertainty of RDX degradation rate.

Utility of TREECS™

It has been estimated that the use of TREECS™ as part of the Army’s Operational Range Assessment Program (ORAP) Phase II analyses can save the Army approximately three million dollars every five years. However, the benefits of using TREECS™ go far beyond these cost savings. Modeling can be used to forecast not only if, but when PALs will be exceeded. Additionally, the modeling system can be used to assess BMP strategies for avoiding future PAL exceedances and to evaluate the carrying capacity of existing and future training/firing ranges. Modeling can provide insight for improved sample design and monitoring. It also allows the assessment of “what if” scenarios without the risks and costs associated with trial-and-error field implementation. Moreover, TREECS™ usage can be an integral part of the successful administration of ORAP and related range sustainment programs, which avoid substantial amounts of money being lost if operational ranges are closed due to compliance failure. It was shown that TREECS™ could be rapidly applied (in less than 80 labor hours), using readily available data, and providing accurate results (rated highly successful according to the ESTCP project objectives) .

TREECS™ version 5 can be downloaded from the World Wide Web (to be provided later, as still being migrated to new Web site). Version 6, which includes the BMP modules, will be available near the end of 2016.