The NGWA Pillars of Groundwater Innovation Conference: Alphabetical Content Listing
Role of the Vadose Zone in Subsurface Hydrology
Shlomo P. Neuman
Flow Near Wells in a Partially Saturated Geologic Media
Phoolendra Mishra
Scale-dependent Spatial Variability of Pedologic and Hydraulic Vadose Zone Properties: The Maricopa Case Example
Shlomo P. Neuman
Uncertainty Quantification of Soil-Water Balance Predictions, Using Fuzzy-Probabilistic and Maximum Likelihood Bayesian Averaging
Boris Faybishenko
Role of the Vadose Zone in Subsurface Hydrology (cont.)
Shlomo P. Neuman
Heterogeneity Preserving Inversion Methods for Vadose Zone Flow Modeling
Marcel Schaap
In pursuit of the question “How much subsurface heterogeneity must be accounted for in vadose zone flow modeling?” we quantify the effectiveness of several methods for generating “fields” of subsurface hydraulic properties as needed for 1D to 3D numerical simulations. The main line of the presentation will deal with a detailed study carried out at Maricopa, Arizona. The study site is a 50×50 meter and 15 meter deep vadose zone at which a 28-day constant-rate infiltration experiment was conducted in 2001. Moisture content at this site was measured with neutron thermalization at 400 locations daily during the infiltration period, and at irregular intervals 100 and 200 days prior to and after infiltration, respectively. Our research shows that direct simulations based on PTF-estimated heterogeneous fields of hydraulic properties poorly represent the measured infiltration plume. However, several types of model inversions using different generalizations of heterogeneity present in the PTF estimates yield acceptable results and offer a potential means to limit the collection of site-specific data. In addition to the Maricopa site, we will also briefly outline surface soil-climate-deep vadose zone interactions for managed systems (a hypothetical golf course) and rangelands for long (10-25 year) time series. Much of this work is still ongoing, but presently these simulations indicate that the type of surface soil and the amount of winter rain strongly affects the amount of deep vadose zone infiltration. Conversely, surface soils as well as the amount of summer rain (the North American monsoon) have very limited effect on long-term nonriparian infiltration.
Unexpectedly Rapid Migration of Perchlorate Through a Thick Vadose Zone Under Low Rainfall Conditions
Daniel B. Stephens, Ph.D., PG
Water Flow and Solute Transport in Deep Vadose Zone—Implications from Direct Observations
Ofer Dahan
A vadose-zone monitoring system (VMS), which was developed recently, allows continuous monitoring of the hydrological and chemical properties of percolating water in the deep vadose zone. The data which is collected by the system allow direct measurements of the water percolation fluxes and detect the chemical evolution of the percolating water across the entire unsaturated domain. Up to date, the system has been successfully implemented in several studies on water flow and contaminant transport in various hydrological and geological setups. These include floodwater infiltration and groundwater recharge, agricultural impact on groundwater quality, evolution of landfill leaches, and control of remediation processes in contaminated sites.
Direct observations on flow and transport processes which were measured in a variety of natural deep vadose zones under various hydraulic conditions allowed evaluation of few assumptions that are commonly used in vadose zone modeling. For example, water percolation in a natural vadose zone occurs as wetting waves through a relatively narrow range of water content amplitudes that does not exceed field capacity values, even if land surface is flooded with high water head for long periods (weeks to months). This phenomenon greatly influences solute and contaminant transport in unsaturated conditions. Percolation under low water content that never reaches saturation does not allow complete leaching of solutes from the unsaturated zone. Moreover, it allows salinity/contaminant accumulation in sections of the porous domain that never gets fully saturated, even in relatively homogeneous domains such as sand dunes. The incomplete leaching creates major differences between the chemical composition of sediment sample extracts and mobile water phase. Evidences of this phenomenon were observed over a wide range of geological and hydrological scales. Apparently this phenomenon impacts flow and transport models that use chemical composition of sediment samples for calibration and validation process. Another example is related to transport in unsaturated clay sediments. Direct measurements of water percolation velocities showed that percolation rates in unsaturated clay are several orders of magnitude faster compared to any other natural sediment, such as sand or alluvium (natural gravel). It has been found that fast water percolation velocities were related directly to desiccation cracks that form naturally in unsaturated clay. Apparently these observations contradict the common notion that attributes lower sensitivity to aquifers underlying clay soils.
Satellite Imagery Applications for Hydrogeology
Errol L. Montgomery, Ph.D.
Satellite Imagery Applications for Hydrogeology
Errol L. Montgomery, Ph.D.
Satellite Imaging for Tailings Impoundment Water Balance
Janis Blainer-Fleming
Tailings impoundments are disposal locations for sediments resulting from mineral processing at mining industry facilities. Tailings are commonly transported to impoundments as a water slurry. Evaporation loss is the single largest output component of tailing impoundment water balances for locations in the arid southwest of the United States. Previous estimates of evaporation loss for an example site were based on regional climate data and were in the range of 15 to 20 percent of water delivered. Satellite images obtained at approximate one month intervals were analyzed to estimate relative moisture of the tailings impoundment surface. The relative moisture results coupled with local-scale evaporation data were used to refine previously estimated evaporation loss. Results indicate that evaporation losses at the example site were larger than previously estimated and range from 30 to 40 percent of water delivered.
Satellite Imagery Applications for Hydrogeology (cont.)
Errol L. Montgomery, Ph.D.
CONUS-Wide Operational Landscape ET at 1 km for Drought and Hydrologic Applications
Gabriel Senay
Four Decades of Earth Observation Data Related to Mining Activity and Changing Hydrology in Mongolia
Donald Bills
Imaging Current and Ancient Subsurface Water and Ice on Mars
Victor Baker
A variety of satellite imagery is being applied to studies of the current and paleo-hydrogeology of the planet Mars. Gamma ray spectroscopy and radar sounding document extensive planetary-scale deposits of subsurface water ice. Visible and near-infrared imagery show evidence of very ancient outbursts of subsurface water, some of which generated megaflooding on early Mars that induced global climatic change. The University of Arizona’s High Resolution Imaging Science Experiment (HiRISE) has recently generated images showing ongoing seepage of what are probably brines on present-day Mars. It is now clear that Mars, like Earth, has had a dynamic hydrological cycle, operating on a planetary scale, over the entire history of the planet, and that this cycle involved complex interactions of both groundwater and surface water components interacting with an evolving atmosphere and cryosphere.
Successful and Efficient Groundwater Investigations and Remedial Work
Fletcher Driscoll, Ph.D., PG
Observations from 40 Years of Project Management
Al Quagliotti
This paper will present examples of “good project management” practices that resulted in unexpected and unfavorable consequences for the consultant, project manager, client or other stakeholders. The presentation will conclude with the description of a successful project involving decades of work and a long list of stakeholders.
Plume Mapping Requires Consideration of Unique Groundwater Conditions and Chemical Properties
James Mercer
Complex site hydrogeology results in variations in chemical distributions at hazardous waste sites. Different permeable units have different unique plumes due, in part, to different flow directions and properties. Plumes in these different hydrologic units should not be aggregated. Different chemical properties prevent uniform distribution of chemicals. The transport properties of chemicals such as sorption and degradation determine how rapidly and how far each individual chemical will migrate. Different chemical release locations and dates further contribute to unique chemical migration extent and distribution. Consequently, combining multiple chemicals with different properties and distributions a priori is technically inappropriate. Combining multiple measurements of different chemicals over an extended time period (1) prevents interpretation of individual chemical plumes, (2) can result in connecting outlier data points that would otherwise be excluded, (3) combines data of different quality, and (4) does not consider active or passive remediation that will have an effect on older data, often lowering concentrations. The selected contouring method also has an impact on the shape and size of plumes. Further, selection of the numerical value of the outer contour will determine the size of plumes and may incorporate uncertain data.
Successful and Efficient Groundwater Investigations and Remedial Work
Fletcher Driscoll, Ph.D., PG
A consultant’s technical and scientific expertise can only be effective at a contaminated site if the work is carefully and strategically managed throughout the life of the project. Managers on behalf of both the client and consultant must have the capability to identify the potential environmental liabilities, define and adopt strategies to address the risks, and focus the investigation and remedial work on the most important elements. It is vital that the client authorize sufficient monetary support to ensure that the data collected are adequate, technically defensible, and presented in a well-written and easily-understood report. The consultant must ensure that the investigation expenditures are focused on only the identified risks and then presents the data in a report that addresses these risks. Long experience in providing expert witness testimony and the review of thousands of consultant reports for contaminated sites indicates that the adoption of an effective project strategy, collection of an adequate and well-defined data base, and the installation of an effective remedial system will lead to an overall lower project cost, efficient site remediation, and fairer resolution during litigation.
Successful and Efficient Groundwater Investigations and Remedial Work
Fletcher Driscoll, Ph.D., PG
Ignore the Details and Varying Uncertainty of Well Data at Your Own Peril
Marvin F. Glotfelty, RG
Groundwater investigators can utilize indirect methods (such as geophysical surveys) for hydrologic data collection, and stochastic analyses or data management tools enable us to thoroughly organize and assess the hydrologic data. However, groundwater investigations inevitably rely on information derived from borings and/or wells. Too often, the considerations and limitations of information from drilling programs and wells are ignored by investigators. Wells should not be considered only as a set of data points to be plotted on a site map to represent hydrogeologic and water quality conditions at various locations. A flaw in this perspective is a disregard for the vertical dimension (well depth and perforated interval) of each well, the impact of the well’s annular seals (or the lack thereof), or the methods and materials used for well drilling, installation, and development. In addition to the construction attributes of wells, inappropriate hydrogeologic interpretations often result from failure of an investigator to embrace sound fundamental scientific principles, such as differentiating precision versus accuracy, validity of significant digits in reporting measured data, and recognition that conceptual models based on extrapolated or interpolated data cannot be assigned the same level of reliability as actual measured or observed values. Clarification of things we can measure and rely upon with certainty—versus the things we assume, interpret, or project with some degree of uncertainty—will enable us to avoid the pitfalls of hydrologic understanding/misunderstanding that can lead to misinterpretation of groundwater conditions and poor design of groundwater supply or remedial infrastructure.
The Ethics of Scoping and Pricing
Tyler Gass
Although most clients are aware of the challenges faced by environmental consultants who have been asked to develop a scope of work for an environmental site characterization program or the remediation of a contaminated site, clients will often request, even their most favored consultants, to competitively bid on work. In most circumstances price becomes one of the primary factors driving the selection of the environmental consultant to perform the work. Therefore, to compete, consultants are faced with a decision to trim the scope of work below what may be necessary to achieve the client’s needs, or come up with an imaginative low-cost proposal, knowing that any loss of profit will be made up with subsequent changes in scope. Alternatively, some consultants will deliberately prepare a realistic scope of services and cost proposal for those services, believing that it is the consultant’s ethical obligation to provide the client with a program that has the best chance of achieving the client’s needs, without significant changes to the original proposed scope of service and price.
The issue of ethics in the environmental consulting field is subject to a range of opinions. While a code of professional ethics is generally inherent in the culture of any professional services firm, for the individual professional scientist and engineer, the ethical challenge of pricing and scoping becomes more complex. Frequently the individual must demonstrate his/her ability to bring in new project work, while at the same time address the question of whether to provide the client with the information and services they truly need versus a scope of work and price the client would find more palatable.
This presentation will illustrate the challenges faced by consultants, and the dilemmas faced by clients in selecting consultants, using several case studies based on the author’s observations and experience during 40 years of providing environmental and hydrogeologic services.
The Influence of Black Swans on the Effectiveness of Remediating Groundwater Contamination
Donald Siegel, Ph.D.
What’s New in Groundwater Modeling?
Mary P. Anderson, Ph.D.
A Revolution in Progress
Mary P. Anderson, Ph.D.
Groundwater modeling is undergoing a revolution driven by the need to incorporate uncertainty in the conceptual model, numerical model, and in model calibration. Additionally, new GIS packages and new ways of modeling (e.g., with unstructured grids) provide powerful tools to improve how we model. In this session, we will explore some of these exciting new developments in groundwater modeling. In the past, groundwater modelers focused on simulating a single version of reality. However, modelers now acknowledge that unavoidable gaps in hydrogeological field data mean that there is uncertainty in the conceptual model that underlies every numerical groundwater model. Moreover, modelers are gradually accepting that inverse (parameter estimation) codes, which incorporate uncertainty analysis as part of the calibration, provide a better way to calibrate models. Furthermore, new GIS tools help in formulating the conceptual model while unstructured grids allow much needed flexibility in constructing the numerical model. New codes are available for complex problems involving saltwater intrusion in coastal aquifers and advances are being made in representing heterogeneities in subsurface properties, which is critical in delineating contaminant pathways. Ongoing research is also yielding a suite of codes for analyzing transport of contaminants with efforts toward aquifer remediation.
Developing the Conceptual Model
Neven Kresic, Ph.D., PG
Conceptual site models (CSMs) are now increasingly developed in a quantitative manner from the beginning of most commercial projects and are ready to be translated into numeric models effortlessly, at any stage of the project. Using a quantitative CSM and a numeric model simultaneously is invaluable for assessing uncertainties in both, and provides a very much needed feedback for their improvement. Notwithstanding that a professional hydrogeologic judgment is irreplaceable at the end, this presentation focuses on application of geostatistical, probabilistic, and visualization programs for CSM development and includes discussion on various interactions between conceptual and numeric models, as well as their potential misuse.
Uncertainty and Parameter Estimation
Randall Hunt, Ph.D., PH
What’s New in Groundwater Modeling? (cont.)
Mary P. Anderson, Ph.D.
Effects of Small-Scale Preferential Flow Paths on Solute Transport: Observation and Modeling
Chunmiao Zheng
Understanding Saltwater Intrusion Processes: New Insights Learned from Laboratory Observations Coupled to Numerical Predictions
T. Prabhakar Clement, Ph.D.
Sea level rise and reductions in groundwater flow due to droughts are the two important climate change-induced hydrological variables that can severely aggravate freshwater management problems in coastal aquifers. In this presentation we will present several laboratory and numerical datasets to illustrate the impacts of these two climate change-induced hydrological variables on saltwater intrusion processes. We will summarize the results of recent research efforts where we have tested three counterintuitive hypotheses related to the saltwater intrusion problem. In this presentation we will provide laboratory and/or numerical data to verify these hypotheses, and also discuss the new insights learned from these research studies.