Source: UNIVERSITY OF KENTUCKY submitted to NRP
MODELING FOR TMDL DEVELOPMENT, AND WATERSHED BASED PLANNING, MANAGEMENT AND ASSESSMENT
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0216841
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
S-1042
Project Start Date
Oct 1, 2008
Project End Date
Sep 30, 2013
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
UNIVERSITY OF KENTUCKY
500 S LIMESTONE 109 KINKEAD HALL
LEXINGTON,KY 40526-0001
Performing Department
Biosystems & Agricultural Engineering
Non Technical Summary
The Clean Water Act (CWA) employs regulatory and nonregulatory tools to reduce direct pollutant discharges into waterways, finance wastewater treatment facilities, and manage polluted runoff. These tools are used to restore and maintain the chemical, physical, and biological integrity of the nation's waters. Starting in the late 1980s, efforts to address polluted runoff have increased significantly. For "nonpoint" runoff, voluntary programs, including cost-sharing with landowners, have been used as the key tools. Evolution of CWA programs over the last decade has included a shift to more holistic watershed-based strategies, with equal emphasis placed on protecting healthy waters and restoring impaired ones. Involvement of stakeholder groups is another hallmark of this approach. The CWA Section 303(d) fact sheet indicates a total of 38,698 impaired waters. Due to the immensity of the stream miles, lakes and estuaries involved and the jurisdictional differences within impaired watersheds, tools are needed to better understand the causes and processes that can be used to restore and protect these water bodies. Total Maximum Daily Loads (TMDLs) are quantitative objectives and strategies to achieve water quality standards. The water quality standards constitute the goals required to fully support designated uses of streams, lakes, and wetlands. In general terms, the TMDL development process involves assessing the causes and amounts of pollution, identifying the best corrective actions and a monitoring strategy to ensure effectiveness. There is a need to evaluate existing tools and to develop new ones based on the best science available. This project will develop tools to guide the use of these policies so stakeholders can understand what practices are available and why they should implement them. An important outcome of the project will be increased knowledge of the appropriateness of various TMDL development tools for application in agricultural watersheds. In addition, existing TMDL development tools will be enhanced and some new tools may be developed. This outcome will improve models used for TMDL development. Another important outcome of the projects is improved software interfaces. This outcome will employ advances in information technology to allow data to be entered more easily in models and to aid in the interpretation of results. Another outcome of the project is the collection of data for TMDL model evaluation and for BMP effectiveness assessment. Available data will be utilized where possible, but some additional data collection will be required. The overall outcome of the project will be the evaluation and development of watershed models, economic, and social analysis tools that can be used for TMDL development and implementation in agricultural watersheds. Project accomplishment will ensure that techniques used for TMDL development and implementation in agricultural watersheds are based on the best science available and that proposed TMDLs are feasible. The ultimate beneficiaries will be the agricultural community, land users, home owners and other stakeholders who will be impacted by the TMDL program.
Animal Health Component
(N/A)
Research Effort Categories
Basic
(N/A)
Applied
(N/A)
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1330320202040%
1120210205040%
1120320205020%
Goals / Objectives
Develop, improve and evaluate process based models and geospatial tools for watershed based planning and management. Develop tools (standards, framework, or protocol) to link the physical modeling with the economic aspects of watershed planning and management. Develop tools with social scientists and other project partners to help accelerate implementation of watershed planning and management through behavior change. Facilitate usability of watershed management planning models.
Project Methods
The goal of this objective is to improve the ability of models to assess the impact of agricultural practices on in-stream water quality. Needs for specific data, parameters and criteria, and computer-compatible data formats will be mutually developed. As the result of this objective, model evaluation and development and data collection responsibilities for the participating states/locations will be established. Results will be shared as the research progresses. These activities will be summarized with all project participants at the annual technical committee meeting. Task 1. Hold regional forums to assess needs of local stakeholder groups in understanding the TMDL process and our ability to furnish information that they can understand. Task 2. Hold forums for model users to share their experiences and facilitate the use of these models on regional scales. Task 3. Critical reviews of existing models in relation to the scale of the TMDL impairment and the regional differences in climate, crops grown, field practices used to grow these crops and the attitudes of the farmer and ranchers relating to the models inputs and outputs for their region. Task 4. Review, evaluate and improve how the models simulate Best Management Practices (BMPs). Task 5. Develop models and approaches that generate specific locations for BMP implementation in a watershed that meet environmental targets at the least cost. This task will include the development of ranking systems that relate the risk of pollutant delivery from source areas to the sink capacity of watersheds. Task 6. Develop relationships between BMP efficiencies and the economics of BMP implementation and maintenance. Task 7. Conduct a literature review of BMP effectiveness and models ability to simulate that effectiveness. Task 8. Expand existing models to handle the fate and transport of emerging contaminants. Task 9. Identify where the uncertainty exists in current models. Task 10. Identify which uncertainties are important to address the functionality of models and in improving their results. Task 11. Improving the understanding of model parameter and data uncertainty and incorporate this understanding in model predictions.

Progress 10/01/08 to 09/30/13

Outputs
Target Audience: Colleagues who will be potential collaborators in similar and related subsequent studies, professionals who use similar monitoring and analysis techniques. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided? Yes. A minimum of three students working in closely-related areas were awarded graduate degrees during the course of the project. How have the results been disseminated to communities of interest? Scientific articles, presentations at professional meetings. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? Substantial progress was made regarding quantification of uncertainty, in both space and time, as it relates to key hydrologic and water quality parameters that affect both experimental and modeling results. As a result, there is a much more detailed and practical understanding of the degree to which runoff-generating characteristics can change in time and space, as well as how soil sampling strategies can influence the characterization of nutrient availability, which is in turn propogated throughout both observed and modeled nutrient concentrations in runoff.

Publications

  • Type: Journal Articles Status: Published Year Published: 2013 Citation: Maupin, T.P., C.T. Agouridis, D.R. Edwards, C.D. Barton, R.C. Warner, and M.P. Sama. Specific Conductivity Sensor Performance: II. Field Evaluation. International Journal of Mining, Reclamation and Environment. Early View. doi: 10.1080/17480930.2013.764702 (jif: 0.392)
  • Type: Journal Articles Status: Under Review Year Published: 2013 Citation: D.J. Stamper, C.T. Agouridis, D.R. Edwards, and M.A. Purschwitz. Effect of Soil Sampling Density and Landscape Characteristics on Soil Test Phosphorus.


Progress 01/01/11 to 12/31/11

Outputs
OUTPUTS: Work during the previous calendar year has transitioned from primarily model-oriented to experimental/data collection as our experimental runoff plots and rainfall simulators have been refurbished in preparation for studies to assess the runoff transport of antibiotics in various animal manures. Experimental protocols are still in development with data collection anticipated for Summer 2012, but our anticipation is to include some or all of the following categories: fluoroquinolones, tetracyclines, sulfonamides, and trimethoprim. At a minimum, we will be investigating swine and poultry manure as the waste sources. One graduate student is currently training under this activity. PARTICIPANTS: Participant: Carmen Agouridis, Assistant Professor, Biosystems and Agricultural Engineering Department, University of Kentucky. We expect to collaborate with Carl Bolster, USDA-ARS, Bowling Green, Kentucky. TARGET AUDIENCES: Preliminary target will be professional scientists and academics, anticipating dissemination to outreach professionals. PROJECT MODIFICATIONS: Nothing significant to report during this reporting period.

Impacts
No outcomes of the current major activity are presently available; however, given the relatively sparse information available on the topic, the findings can quickly become relevant in the context of acquired antibiotic resistance in waterborne pathogenic organisms.

Publications

  • No publications reported this period


Progress 01/01/10 to 12/31/10

Outputs
OUTPUTS: Previously reported work has been extended to quantify and demonstrate the amounts of and interactions between hydrologic/water quality model uncertainty and model parameter uncertainty, both of which are related to Tasks 9 and 10 of Objective 1. These results have been presented and discussed, thus far, at professional seminars and invited presentations. Presentation is scheduled for the next professional meeting with preparation of a peer-reviewed publication to follow. PARTICIPANTS: Not relevant to this project. TARGET AUDIENCES: Nothing significant to report during this reporting period. PROJECT MODIFICATIONS: Not relevant to this project.

Impacts
In contrast to earlier work, which examined model and parameter uncertainty conditioned on particular existing data sets, recent work has investigated whether it is possible to make inferences under conditions of no data or very limited data. These findings are much more site-specific and context-specific than previous findings, since at least some data (even if from a different site and/or context) are required to extend results to a situation of no data. The basic conclusion is that uncertainty inferences, similar to accuracy of the models themselves, depend on the similarity between the situation to be modeled and situations that have already been modeled. Furthermore, more analyses of a comparable nature will have to be completed before uncertainty statements prior to data collection can be made with appreciable precision. The effect of small data sets on uncertainty appears to be highly complex; in the case of very simple models, small data sets enable parameter uncertainty to be determined nearly completely, with little marginal reduction in uncertainty associated with additional data. In the case of relatively complex models, the effect of additional data appears to depend on the model's intrinsic capability to model the situation, with the ultimately more accurate models demonstrating parameter uncertainty reductions but with little (if any) reduction in the cases of less accurate models. With models being used increasingly in litigation situations, the findings can be of assistance in both selecting models of choice and in interpreting the results, most notably in the context of what can be inferred from the results.

Publications

  • No publications reported this period


Progress 01/01/09 to 12/31/09

Outputs
OUTPUTS: Near the end of the study period, a study was completed that investigated total uncertainty, its components of model and parameter uncertainty, and how all types of uncertainty are influenced by model selection. These topics are specifically related to Tasks 9 and 10 of Objective 1. This study being largely a work in progress through the calendar year, dissemination of the findings has been largely informal, though communications with colleagues at other institutions. The technical outputs (probability distributions of model predictions, model parameters, and model correctness for different candidate models), however, are scheduled for presentation at upcoming professional meetings followed by publication. PARTICIPANTS: Nothing significant to report during this reporting period. TARGET AUDIENCES: Nothing significant to report during this reporting period. PROJECT MODIFICATIONS: Nothing significant to report during this reporting period.

Impacts
Work to date indicates that, at under at least some conditions, there are some advantages to using relatively complex hydrologic/water quality models in terms of lesser prediction uncertainty. The relationships between parameter and model uncertainty are more subtle, however, depending greatly on the amount of model calibration data available and the number of parameters present in the model. The findings additionally indicate that prediction uncertainty is highly dependent on uncertainty in only a few key model parameters, depending on model structure and subsequent calculations involving those parameters, a result that is consistent with sensitivity analysis. Given the very limited duration of the project, impacts are necessarily limited; however, the results will most naturally find their application in litigation involving hydrologic/water quality models and in the design of data collection projects having the goal of calibrating hydrologic/water quality models.

Publications

  • No publications reported this period