VZJ sign up for citetrack
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


Published online 20 November 2007
Published in Vadose Zone J 6:906-912 (2007)
DOI: 10.2136/vzj2006.0175
© 2007 Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
This Article
Right arrow Abstract Freely available
Right arrow Figures Only
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via HighWire
Right arrow Citing Articles via Web of Science (1)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Last, G. V.
Right arrow Articles by Bjornstad, B. N.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Last, G. V.
Right arrow Articles by Bjornstad, B. N.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Last, G. V.
Right arrow Articles by Bjornstad, B. N.
Related Collections
Right arrow Data Assimilation
Right arrow Geostatistics

SPECIAL SECTION: HANFORD SITE

Standardization of Borehole Data to Support Vadose Zone Flow and Transport Modeling

G. V. Lasta,*, C. J. Murraya, D. A. Bushb, E. C. Sullivana, M. L. Rockholda, R. D. Mackleya and B. N. Bjornstada

a Environmental Technology Division, Pacific Northwest National Lab., P.O. Box 999, Richland, WA 99352
b Geologic Consulting, Stevensville, MT 59870

* Corresponding author (george.last{at}pnl.gov)

All rights reserved. No part of this periodical may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopying, recording, or any information storage and retrieval system, without permission in writing from the publisher.


Received 7 December 2006.



    ABSTRACT
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and Methods
 Discussion
 REFERENCES
 
Numerical representation of the geologic framework and its hydrologic and geochemical properties is an integral part of all vadose zone flow-and-transport modeling. Historically, the geologic framework has been represented by simple homogeneous and horizontally stratified hydrogeologic units. However, as computer-processing capabilities have become more advanced, there has been more emphasis on improving spatial resolution and quantifying uncertainty in key model parameters. One of the more popular approaches has focused on geostatistical simulation of the flow-and-transport properties themselves, with little regard to the geologic strata and sedimentary sequences. Newer approaches are focusing more on geostatistical simulation of the sequence-stratigraphic relations of lithofacies and the geostatistical distributions of flow-and-transport properties within those facies. These approaches require more rigorous quantitative treatment of geologic data than is normally supported by the mostly qualitative nature of borehole geologic information. At the USDOE Hanford Site, efforts are being made to standardize borehole geologic data so they can be used in a systematic and quantitative way to define the spatial distribution of flow-and-transport properties in support of vadose zone flow-and-transport simulations. New detailed procedures translate qualitative descriptive information into categorical data and inconsistent quantitative and semiquantitative data into common parametric data sets. A geologic data-management system is being developed to manage and integrate these standardized categorical data sets with other existing databases to support synergistic analysis and to improve numerical representation of the hydrogeologic architecture. These standardized data sets were used to develop lithofacies-based geostatistical representations of hydraulic conductivity beneath one of Hanford's more complex waste sites.

Abbreviations: HBGIS, Hanford Borehole Geologic Information System


    INTRODUCTION
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and Methods
 Discussion
 REFERENCES
 
The vadose zone beneath the USDOE's Hanford Site in southeastern Washington State (Fig. 1 ) received approximately 1 trillion liters (450 billion gallons) of liquid waste, some contaminated with radioactive and hazardous contaminants. Today, Hanford is engaged in the world's largest environmental-cleanup project, and a variety of conceptual and mathematical vadose zone models have been developed to support individual cleanup objectives. Traditional approaches to modeling the stratigraphic framework at Hanford have used simple homogeneous and horizontally stratified hydrogeologic units. However, as computer-processing capabilities have advanced, more emphasis has been placed on improving spatial resolution and quantifying uncertainty in representing the geologic framework and its key model parameters. Newer approaches are focusing on geostatistical simulation of the sequence-stratigraphic relations of lithofacies and on the geostatistical distributions of flow-and-transport properties within those facies. These newer approaches require more rigorous quantitative treatment of geologic data than are normally supported by the mostly qualitative nature of borehole geologic information. Thus, efforts are being made to standardize borehole geologic data so they can be used in a systematic and quantitative way to define the spatial distribution of flow-and-transport properties in support of vadose zone modeling.


Figure 1
View larger version (120K):
[in this window]
[in a new window]

 
FIG. 1. Location of the Hanford Site and geologic elements of the Pasco Basin in eastern Washington (from Cannon et al., 2005).

 
Borehole geologic data provide the foundation for interpreting the subsurface framework and spatial distribution of the flow-and-transport properties. Surface geophysical data can be useful for extrapolating between boreholes; however, they too depend on borehole geologic data for calibration and validation of the geophysical responses. Borehole data are composed of various types and quality of data, from qualitative field observations (driller's logs) to quantitative laboratory analyses of borehole samples (e.g., grain-size distributions) and borehole geophysical logs. Many of these data are collected in nonstandardized formats that are difficult to incorporate into numerical simulation.

Efforts are being made at the Hanford Site to standardize, manage, and analyze borehole geologic data to produce both regional sequence-stratigraphic hydrogeologic models and site-specific geostatistical representations of spatial distributions of lithofacies and their hydrogeologic and geochemical properties. Although the regional stratigraphic units for the Hanford Site are well documented, the differentiation of smaller-scale depositional elements and inherent flow-and-transport properties has been limited and difficult to quantify. Collecting new subsurface data is time consuming and expensive. Thus, it is important to extract as much information as possible from existing borehole data. This has led to the development of data standardization and translation techniques and methods for data integration, as well as the design and construction of a prototype, Web-based data extraction and management system.

This paper describes these data-standardization and translation techniques and the data-management system and presents an example of how these newly developed data sets are being used to develop a site-specific lithofacies and hydrofacies model for the vadose zone beneath one of Hanford's more complex waste sites.


    Materials and Methods
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and Methods
 Discussion
 REFERENCES
 
Background
Grain-size distribution and the texture, fabric, and mineralogical changes in the sediments of the unsaturated zone profoundly influence vadose zone flow-and-transport processes (Ward et al., 2006). These changes are often linked in predictable ways to small-scale lithofacies heterogeneity and larger-scale stratigraphic packaging (Anderson, 1990; Fogg et al., 1989). Heinz et al. (2003) recognized three levels of heterogeneity: lithofacies (third order), depositional sedimentary sequences or packages (second order), and the architectural scale of stacked depositional elements (first order). Differentiation of the subsurface into first- or second-order architectural elements generally coincides with major unconformity-bounded sedimentary sequences. Further subdivision into third-order elements is achieved by unraveling the distribution of discrete lithofacies within the larger-scale sedimentary sequences. Lithofacies are the most basic stratigraphic element and are defined as sediments that have a group of physical, chemical, textural, or other characteristics that imply a certain origin, depositional environment, or history (Heinz et al., 2003). Other smaller-scale (fourth order and higher) heterogeneities occur within lithofacies. The heterogeneities within and between lithofacies and the depositional elements they are formed in, for example, point bars or overbank deposits, strongly influence contaminant transport and fate.

Three general approaches are commonly used to produce realistic simulations of the subsurface for application in vadose and groundwater models: (i) process-imitating, (ii) structure-imitating, and (iii) descriptive approaches (Koltermann and Gorelick, 1996). Hybrid approaches (Koltermann and Gorelick, 1996) minimize the influence of individual approach limitations. An example of a hybrid approach is given by Weissmann and Fogg (1999), wherein they combine descriptive sequence stratigraphic characterization, which provides stratigraphic framework and facies architecture, with transition probability geostatistics (a structure-imitating approach) to generate spatial variability for high-resolution three-dimensional realizations of the heterogeneity in an alluvial fan.

One of the most important elements of developing a lithofacies-based representation of the subsurface is the verification of facies geometries, lengths, and juxtapositions present within each depositional element or facies assemblage. Computer visualization technology, in combination with analysis of data from multiple boreholes, outcrop studies, and basinwide geologic studies, provides the basis for estimating the geometries and spatial distribution of lithofacies within the major stratigraphic units (Last et al., 2005b). Previous work at Hanford has focused on understanding vertical stratigraphic relationships because there has seldom been sufficient data to address the lateral facies changes and facies dimensions required to more accurately define geostatistical models of the subsurface characteristics.

The recognition and mapping of genetically linked lithofacies packages provide a framework for predicting textural and diagenetic changes and quantitative variations in contaminant distribution. A three-dimensional stratigraphic framework with unconformity-bounded sequences, combined with lithofacies modeling and even finer scale analyses of heterogeneity and supported with borehole geologic data, provides an improved quantitative method to represent the spatial distribution of flow-and-transport parameters and associated uncertainty.

The first critical element in developing a subsurface model for a given site is to gather and integrate all available borehole, outcrop, and geophysical data available for that site (Fig. 2 ). At the Hanford Site, by far the largest data set is borehole geologic data—there are over 7500 boreholes on site. In contrast, geologic outcrops are sparse and generally limited to shallow excavations. Surface geophysical data are also scarce and of limited value due to the great thickness (up to >100 m) of the vadose zone, the very dry and unconsolidated nature of the subsurface sediments, and the abundance of cultural features (e.g., fence lines, power lines, steel-cased boreholes). Thus, efforts are being made to increase the usefulness and value of information that can be extracted from the large amount of available borehole data.


Figure 2
View larger version (52K):
[in this window]
[in a new window]

 
FIG. 2. Site-specific lithofacies and hydrofacies construction (after Bush et al., 2005).

 
Standardization of Borehole Geologic Data
Hanford borehole geologic data are of variable quality and include qualitative descriptions of the geologic materials encountered during drilling (driller's logs and geologist's logs), laboratory analyses of borehole samples, and borehole geophysical logs (Horton et al., 2005). These data have been collected over several decades by numerous organizations using a wide range of procedures and protocols. Procedures and field guides, such as those by Last and Bjornstad (1990), have been used by well-site geologists since the mid-1970s to produce fairly consistent sets of descriptive geologic observations of borehole cuttings and samples. However, older driller's logs vary widely in the detail and quality of their descriptions of borehole cuttings. Thus, this descriptive information has been difficult to compare and analyze between boreholes, leading to multiple subjective interpretations.

Standardization of these descriptive observations results in an internally consistent set of data that can be integrated with other borehole geologic data sets (e.g., geophysical logs) and used to generate more quantitative, reproducible, and traceable interpretations of the subsurface framework. The majority of recent laboratory and borehole geophysical data already exists in a quantitative form and is located in various electronic and hard-copy sources. In contrast, driller's and geologist's logs are traditionally recorded on handwritten log sheets and vary widely in the quality and detail of their lithologic descriptions. To standardize these observations and to convert them into an electronic semiquantitative form, a series of logic rules and peer-reviewed procedures were developed. Based on these rules, the descriptive text information contained in log records is parsed and translated into a unified set of categorical data classes (e.g., particle size classes, color, clast lithology) on a standardized electronic template. Throughout the translation and standardization process, all data sets are carefully reviewed for completeness and traceability to original records and for compliance to translation and standardization procedures and are then entered into a relational database.

A prototype borehole geologic data-management system was developed to manage and integrate the newly interpreted categorical data sets with existing electronic raw databases (Fig. 2). The Hanford Borehole Geologic Information System (HBGIS) is a relational database management system consisting of a Microsoft Structured Query Language (SQL) Server back-end database that is accessed by end users via a Web-based graphical user interface (Last et al., 2005a). It is designed to be a completely extensible, multi-user system with multi-access that directly interfaces with existing databases at the Hanford Site to import "snapshots" of relevant data sets. This system is capable of direct data entry, automated data import, data query, and data export in the form of spreadsheet reports and graphical log plots (Fig. 2). Additional data analysis and visualization capabilities are being developed in parallel with other fluid flow and contaminant transport parameter databases, such as the Vadose Zone Hydraulic Property database (Freeman et al., 2002; Freeman and Last 2003) and the Hanford Contaminant Coefficient Database (Cantrell et al., 2003).

The HBGIS also provides traceability and documentation of changes (change control) for interpreted stratigraphic contacts. Thus, in addition to the raw borehole geologic data and the standardized borehole geologic data sets, the HBGIS also manages a database of interpreted stratigraphic contact depths for each borehole.

Ideally, the development of a regional stratigraphic contacts database should be tied explicitly and unambiguously to the raw geologic data. The raw data are being translated into electronic data sets, and interpretation and translation tools are being developed that can use these electronic data to identify and define the stratigraphic contacts in a reproducible and defensible way. To facilitate the development of these tools and to provide a benchmark for the development and refinement of a regional contacts database, an initial contacts database was assembled for the most extensively studied, central portion of the Hanford Site (Bjornstad, 2004). This initial contacts database was compiled from published and unpublished contact data sets that were then transposed to standardized stratigraphic nomenclature based on that defined by USDOE (2002) and Lindsey (1995). The resulting database identified many discrepancies between contacts subjectively picked by different geologists. The stratigraphic contacts are maintained within and are accessible through the HBGIS. Multiple contacts are stored for any given stratigraphic unit and borehole, providing traceability back to the individual interpretations.

Development of a Sequence-Specific Lithofacies Model for the 216-Z-1A Tile Field
First-order spatial distributions of flow-and-transport parameters generally adhere to the major stratigraphic units (represented by geologic formations and/or members). The internal structure of these major stratigraphic units can be further subdivided into discrete sedimentary packages or sequences, which allows a second-order distribution of flow-and-transport parameters to be defined.

Although the geology of the Hanford Site has been studied for more than 60 years, developing a regional stratigraphic contacts database and sequence stratigraphic model has been challenging. Besides the very heterogeneous nature of the sediments, many other ancillary sources of uncertainty are associated with the borehole data and interpretation of the geologic units, their lateral continuity, and their thicknesses (Oostrom et al., 2006a). These uncertainties include the spacing and accuracy of depth-discrete observations and analyses, ground-surface elevation at the time of measurement, and the geometric shape of the geologic units, particularly in the chaotic catastrophic Ice Age flood deposits of the Hanford formation. These inherent uncertainties, together with project-specific subjective interpretations, have led to multiple (often conflicting) stratigraphic interpretations and data sets within and between different projects.

Spatial delineation of the lithofacies within discrete stratigraphic units begins with a synergistic analysis of all borehole data, including field-derived drill logs, geological descriptions, and geophysical logs, along with laboratory-derived analyses of physical and geochemical properties (Fig. 2). Standardized geologic data residing in the HBGIS provide an easily retrievable and internally consistent data set for quantitative analysis. We have used these data to generate individual one-dimensional graphical well logs of all relevant geologic and petrophysical data (Last et al., 2006b) and have used logic rules to identify individual lithofacies in a traceable and reproducible way (Bush et al., 2005). We have also developed integrated interpretations of the sequence stratigraphy and facies architecture by constructing two-dimensional multi-well stratigraphic cross-sections and three-dimensional solid model interpretations (Oostrom et al., 2006a, b).

To develop a subsurface model for one of Hanford's more complex waste sites (the 216-Z-1A tile field), we combined descriptive stratigraphic characterization and facies architecture with indicator or transition probability geostatistics (a structure-imitating approach). Using these techniques, populated with standardized borehole geologic data, we generated multiple high-resolution three-dimensional realizations of the lithofacies-scale heterogeneity beneath the 216-Z-1A tile field (Bush et al., 2005). The geostatistical realizations were constrained to a physical domain located within the Hanford formation so that no major stratigraphic boundaries were crossed.

Minor stratigraphic units have been identified locally within the Hanford formation (Lindsey et al., 1994a, b) with the designation, from top to bottom, of the H1a, H1, H2, H3, and H4 units. However, these units are primarily based on variations in the amount of gravel present, and no well-defined markers separate those units. The units also tend to be laterally variable, so we elected to simulate the distribution of lithofacies within the Hanford formation as a whole (Bush et al., 2005), using ordinary kriging to account for changes in the proportions of the lithofacies (Journel and Rossi, 1989).

We grouped the flood deposits of the Hanford formation into five general facies types at the 216-Z-1A site with standardized geologic data that were entered and then integrated using the HBGIS database. The five general facies types (silty sand, fine sand, coarse sand, gravelly sand, and sandy gravel) were selected to represent sedimentary bodies that could be easily distinguished with the standardized data and that were expected to have similar hydrologic properties (based on grain-size similarity). The standardized borehole data included sediment classifications of driller's log data from 46 wells. These classifications, based on the Folk (1968) classification of clastic sediments, were assigned on the basis of the order in which the driller listed the sediments. For example, if the driller documented the sediment as sand, silt (mud), and gravel, it was assumed that the first type of sediment was the greatest percentage of the sample and decreased in the order it was listed. Laboratory-measured particle-size distributions were also used in this study for 16 wells where data were available in the HBGIS database. The laboratory-measured particle-size data were also used to classify the sediments using the Folk (1968) system. It was assumed that the laboratory-measured particle-size data were a better representation of the true classification of the sediment at each location than the driller's log data, so if both were available, the particle-size data were used. However, there were a number of wells with both types of data. A cross-calibration was performed, and the frequency with which driller's log data were associated with the different sediment classes identified by particle-size data was used to estimate the probability for a given sediment class to be present, given only the drill-log data. For example, for the fine sand facies, the drill-log data classified samples the same as the particle-size data 35% of the time (Table 1). Although the classification of fine sand from the drill-log data was often incorrect, the calibration still provides valuable information about the correct classification that was incorporated in the soft-data file generated for the geostatistical simulations. For example, if the drill log at a particular location suggested that fine sand was present, then the soft probabilities associated with that data were 56% that the location was actually muddy sand, 35% that it was actually fine sand, 6.7% that it was gravelly sand, and 2.5% that the sediment at the location was actually sandy gravel. Similar soft probabilities were derived from the cross-calibration for the classification of each facies by the drill log. The calibration results allow the use of the drill-log data as "soft data" with a measurable degree of confidence.


View this table:
[in this window]
[in a new window]

 
TABLE 1. Cross-calibration between the sediment classes defined using the driller's log information versus those defined using particle-size data. Sediment classes are defined as silty sand (mS), fine sand (fS), coarse sand (cS), gravelly sand (gS), and sandy gravel (sG), and N is the number of samples. The italicized cells indicate the cross-calibration for each sediment class. For example, for the fS facies, the drill-log based sediment class and the particle-size data based class were identical only 35% of the time.

 
Standardized borehole data from the 216-Z-1A site provided relatively good (1.5 m) vertical resolution on the lithofacies-scale heterogeneity. However, even with 46 boreholes located within or adjacent to this 0.7-ha facility (Last et al., 2006b), there is limited information on the lateral heterogeneity, given that the average spacing between boreholes is approximately 10 m.

Excavation sites near the study area provided a qualitative assessment of the lateral extent and heterogeneity of the facies (Fig. 3 ). At Pit 30, located near the center of the Hanford Site, three primary lithofacies types occur within three distinct sedimentary packages. These include (i) massive silt to fine sand (Fm) at the top of the lower most gravel-dominated sediment package, (ii) horizontally laminated medium to coarse sand to pebbly sand [Sh(c)] making up the middle-sand–dominated sediment package, and (iii) large-scale, planar-tabular (foreset) bedded silty-sandy pebble to boulder gravel (Gp) making up the upper and lower gravel-dominated sediment packages. The lithofacies designations used here are from USDOE (2002). Note the lateral extent, heterogeneity, and apparent anisotropy within each of these facies, as well as the erosional unconformity at the top of the sand-dominated sediment package.


Figure 3
View larger version (85K):
[in this window]
[in a new window]

 
FIG. 3. Outcrop studies (such as this one at Pit 30, near the center of the Hanford Site) provide information on inter- and intrafacies heterogeneity, including the lateral continuity of lithofacies, and lithofacies associations within and between sedimentary packages.

 
We developed indicator variogram models to characterize the spatial continuity of each facies. The vertical variogram models were based primarily on the more accurate particle-size data. Horizontal variogram models for each lithofacies were developed from the driller's log data because the 16 wells with laboratory-measured particle-size data did not provide enough sample locations to develop a valid horizontal variogram model. The ranges of the vertical variograms for the vertical lithofacies were from 4.5 to 8 m, in line with the average thickness of those units. As expected, the horizontal ranges were longer, varying from 7 to 45 m. The fine-grained lithofacies tended to have longer ranges than the coarser lithofacies.

We used the conditional indicator simulation program sisim (Deutsch and Journel, 1998) to produce 100 realizations of the distribution of our five lithofacies. Uncertainty in the spatial distribution of the lithofacies was quantitatively assessed by analyzing the suite of realizations. The realizations that included the maximum amounts of silty sand and sandy gravel were chosen to represent the extreme distributions of facies likely to affect flow and transport, and the modal value at each node was used to identify the most likely distribution of lithofacies (Fig. 4 ). This set of realizations can be used as input for flow-and-transport modeling and should capture the range of behavior in flow-and-transport predictions.


Figure 4
View larger version (64K):
[in this window]
[in a new window]

 
FIG. 4. Example of three-dimensional geostatistical models representing site-specific lithofacies models. (A) Lithofacies simulation with maximum sandy gravel facies; (B) simulation with maximum silty sand facies; and (C) most probable lithofacies, based on mode of 100 simulations. (sG, sandy gravel; gS, gravelly sand; cS, coarse sand; fS, fine sand; mS, silty sand.)

 
Hydraulic conductivities were assigned to each lithofacies based on frequency distributions of measured hydraulic conductivity data from each lithofacies reported in Last et al. (2006a). The resulting three-dimensional geostatistical models of hydraulic conductivity provide more refined representations of the heterogeneity of Hanford formation sediments (over those of traditional layer-cake representations) while at the same time honoring geologically plausible constraints on the flow-and-transport properties of the study area.


    Discussion
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and Methods
 Discussion
 REFERENCES
 
Borehole data are the cornerstone of subsurface characterization, monitoring, and performance assessment, yet these data are often generated and managed in an ad hoc fashion using a variety of formats scattered across individual project records. Standardization of borehole data is particularly critical at the Hanford Site, with more than 7500 borehole penetrations into the subsurface sediments. The utility of this wealth of information depends on standardization of the various vintages of qualitative and quantitative data.

Vadose zone flow-and-transport processes are profoundly influenced by textural and mineralogical changes in the sediments of the unsaturated zone. These changes are often linked in predictable ways to small-scale lithofacies heterogeneity and larger-scale stratigraphic packaging. In addressing the standardization and integration of borehole data, we recognize the need to provide data for analyses and process simulations that go beyond homogeneous, layered geohydrologic models populated with static parameters.

Contaminant transport and fate in the vadose zone are highly controlled by inter- and intralithofacies-scale heterogeneity, and thus, the spatial distribution of lithofacies is essential to mapping the distribution and heterogeneity of key subsurface properties that control vadose zone contaminant-transport processes (Last et al., 2005b). The effects of lithofacies heterogeneity are generally thought to enhance lateral spreading and impede downward migration of contaminants (Last et al., 2006a) but may also promote funneled or fingered flow.

Difficulties in developing lithofacies models include adequately imaging and predicting the shapes and sizes of geometrical facies (particularly thin stringers), assessing the juxtaposition of highly permeable beds, assigning values and boundary conditions to features such as cross-cutting clastic dikes in glacio-fluvial sediments, and assessing biogeochemical properties of intra-unit unconformities. Challenges also remain in properly scaling physical properties (e.g., effective permeability, porosity, moisture-retention characteristics, anisotropy, dispersivity) to larger modeled units and assessing the effects of small-scale structures on larger-scale effective flow-and-transport parameters (Ward et al., 2006; Oostrom et al., 2006a, b).

We anticipate improving our ability to represent the spatial distribution of effective hydrologic and geochemical properties by systematically evaluating available borehole geologic data to develop stratigraphic and lithofacies models and provide soft data for pedotransfer functions and upscaling approaches. This will enhance the resolution and defensibility of numerical flow-and-transport predictions in the vadose zone.


    ACKNOWLEDGMENTS
 
The development of systematization techniques and the Hanford Borehole Geologic Information System (HBGIS), as well as the development of standardized stratigraphic and lithofacies definitions, has been funded by the USDOE, Richland Operations Office, and the Groundwater Remediation Project managed by Flour Hanford, Inc. (FH). The authors are particularly indebted to Dr. Thomas W. Fogwell (FH) for his support. V. R. Saripalli and C. H. Allwardt (Pacific Northwest National Laboratory; PNNL) were instrumental in the development and programming of the HBGIS. A number of PNNL staff and interns have handled the arduous task of translation and standardization and entered borehole geologic data into the HBGIS. Among those that deserve special mention are D. C. Lanigan (PNNL), R. E. Taylor, J. D. Reider, and S. W. Forrester.


    REFERENCES
 TOP
 ABSTRACT
 INTRODUCTION
 Materials and Methods
 Discussion
 REFERENCES
 




This article has been cited by other articles:


Home page
Vadose Zone JHome page
G. W. Gee, M. Oostrom, M. D. Freshley, M. L. Rockhold, and J. M. Zachara
Hanford Site Vadose Zone Studies: An Overview
Vadose Zone J., November 20, 2007; 6(4): 899 - 905.
[Abstract] [Full Text] [PDF]


This Article
Right arrow Abstract Freely available
Right arrow Figures Only
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via HighWire
Right arrow Citing Articles via Web of Science (1)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Last, G. V.
Right arrow Articles by Bjornstad, B. N.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Last, G. V.
Right arrow Articles by Bjornstad, B. N.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Last, G. V.
Right arrow Articles by Bjornstad, B. N.
Related Collections
Right arrow Data Assimilation
Right arrow Geostatistics


HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Journal of Natural Resources
and Life Sciences Education
Soil Science Society of America Journal
Journal of Plant Registrations Journal of
Environmental Quality
The Plant Genome