• NTT - Nutrient Tracking Tool (Version 26-05)
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Frequently Asked Questions


General
What is NTT?
The Nutrient Tracking Tool (NTT) is a free, online, user-friendly tool that quantitatively estimates the nitrogen, phosphorus and sediment losses from crop and pasture lands. It has been developed by the Texas Institute for Applied Environmental Research (TIAER) at Tarleton State University in cooperation with USDA’s Office of Environmental Markets (OCE), Natural Resource Conservation Service (NRCS), and Agricultural Research Service (ARS). While NTT has been around for several years (e.g., a version of NTT is used in the Chesapeake Bay, and another version is used in Arkansas), this version represents the first national version of the tool. NTT was developed by using the Agricultural Policy Environmental eXtender (APEX; Williams et al., 2000). Inclusion of APEX allows users to evaluate other farm level conservation practices such as filter strips, terraces, buffer strips, etc., that could not be evaluated using the Nitrogen Trading Tool. As a result of this effort, users also have access to various other relevant indicators (e.g., water quantity, sediment losses and crop yield changes) to help them make informed decisions about conservation practice implementation.
Is this tool national in scope?
Yes, this tool can be used anywhere in the continental United States (except in AK and HI). NTT has been validated using the regional information for majority of the U.S. States (Please refer to “validation” tab in NTT program). However, in most cases model parameters are generalized. TIAER is currently working with local collaborators to create region-specific parameters for areas of the country where measured data exist that can help refine estimates generated by NTT. The NTT tool currently includes region-specific parameters for the Great Lakes region as well as State of Ohio and Delta region off the Upper Mississippi. Revised parameters will be available in future releases of the tool as they become available.
Will my data be protected?
Yes, each entity using NTT is provided with a password, which is protected so no one else sees your data but you.
What crops are included?
Pastureland, as well as most major cultivated crops for each State, are included in the tool.
What conservation practices are included?
The tool simulates a variety of management and conservation practices including irrigation, tile drains, nutrient management (type, timing, placement, and rate), no till, conservation till, cover crops, ponds/water and sediment control basins, wetlands, buffers (forest and grass), grass waterways, contour buffer strips, terracing, manure treatment, and rotational grazing. Users can also simulate land conversion to perennial crops or forest.
What is the plan to improve/maintain NTT over time?
NTT is housed and maintained at Tarleton State University. USDA’s Office of Environmental Markets is committed to contributing to the update and maintenance of NTT as long as it is useful to stakeholders. NTT versions will be updated regularly with regional parameters provided by ARS, as well as with improved functionality and features as needed.
What is the engine behind NTT?
NTT uses the APEX model to simulate edge-of-field losses, as well as to simulate routing between fields. The Agricultural Policy Environmental eXtender (APEX; Williams et al., 2000). Inclusion of APEX allows users to evaluate other farm level conservation practices such as filter strips, terraces, buffer strips, etc., that could not be evaluated using the Nitrogen Trading Tool.
What type of environmental data and sources are used to simulate NTT?
NTT collects soil, slope, and weather information from national databases, based on the location of your field. Soil data come from the National Soil Survey database (SSRUGO). NTT simulates your field using only the three predominant soils in your field (by percent coverage). Weather is pulled from the national PRISM database. NTT simulates the crop management rotation using 35-years of recent historic weather. Finally, slope information is calculated based on the 30m resolution digital elevation model (DEM) map layer.
What do the nutrient and sediment losses estimated by NTT represent?
Because your rotation is simulated over 35 years of historic weather, the nitrogen (N), phosphorous (P), and sediment losses represent the average annual losses at the edge of the field for a given management scenario. Users can also view the results graphically by year in order to view inter-annual variability, or by month, to view average monthly variability.
Why did USDA support the development of NTT?
USDA’s interest in developing NTT was for water quality markets, which require methods and tools for quantitatively estimating nutrient and sediment losses from a variety of agricultural and best management practices. However, the tool can be used for a variety of applications, including farmer education and outreach, corporate sustainability, and academic or analytical applications.
How long does it take to prepare and run a baseline project in NTT program?
This depends on the user’s expertise in using the models. NTT has been developed to function in all the Continental US states and might take from 10-30 minutes to simulate a new scenario for selected farms, depending on the availability of data for the conservation and baseline scenario they want to run.
Is there a template for collecting data for projects?
Please use this template here to gather the required data to set up your project in NTT.
How do I know that NTT is a right tool for me?
Please refer to the information posted at NTT site, including the user and technical documents and presentations, to evaluate the capabilities and limitations of this tool for your use.
Why am I creating an account?
This is done for your own protection. Your projects are protected and you are the only user that can access, save, modify, delete, and/or copy your projects. Our programmers also have access to your projects for any technical issues that you might have. However, we respect your privacy and do not share your data with anyone without your official request.
At what scale can I use NTT?
NTT could be used at three major levels

i) Field and watershed (combination of fields) - The current NTT and NTT-RE versions provide the field and watershed scales.

ii) County - NTT have been simulated for major soils, cropping, conservation management practices, and weather at each county in the U.S. Also, a user interface (UI) program is written to access the results of these simulations. Currently 10 states (AL, AR, GA, IL, IN, IA, LA, MD, OH, PA) are being simulated. It is expected that the UI program be released to the public in January 2024. The “County” version of NTT will be free to the public when completed and released in September 2024.

iii) Project - This program addresses the request from user for simulating NTT for number of fields at one time. In this case users provide the fields’ data to us as batch files and we will provide the results in a batch files as well. This requires additional programming. This program is currently available. Due to the required programing, there might include a minimal fee to establish “project” program for users.

What are some examples of projects that are using NTT?
NTT is used by numerous producers, extension staff throughout the US. NTT is also used by many organizations and agencies such as Freshwater trust, Chesapeake Bay, Sustainable Environment Consultants, Soil Waters Outcomes Fund, Iowa Dept of Environmental Quality (DEQ), Pennsylvania DEQ, Soil and Water Outcomes Fund (SWOF), Maryland Water Trading Program & MD Dept of Agriculture).
Is NTT validated for my state?
NTT is validated in following four stages and the results are posted in NTT website
Stage 1. To obtain a general parameterization for each state/region, a series of NTT runs simulating common crop rotations, soils and, weather patterns for the region is done and the results are compared with expected crop yield and nutrient and sediment loss values obtained from National Agriculture Statistics Service, USDA (NASS 2017). (please see the list of States in validation tab in NTT program). If your state is not included, you still able to use NTT for the listed cropping system in the program. We are in process of completing stage 1 for all mainland States in US.
Stage 2. During this stage, the field-scale measured data from various sources (e.g., local measured studies and collaborators) are used to finalize the regional APEX parameters.
Stage 3. The final parameters obtained from stage 2 will be used to repeat the process described in stage 1. However, the various conservation practices, common to the local region, are also simulated and evaluated for all soils and weather conditions during this stage.
Stage 4. The final results are evaluated and presented to local stakeholders (if any) and collaborators. The results of the parameterization (for all stages) would become available on the NTT site.
Projects
How can I download a project file off NTT?
To download a NTT project, you need to navigate to the project dashboard (this is the initial page where you can see the list of projects you have created). Next to the name of each project, there is a group of icons under the column named "Actions". Clicking on the icon will allow you to download your project.
How to use NTT on a project scale?

If your project requires running multiple fields, NTT program staff will take the following steps to assist you accordingly:

  1. We will provide you an easy-to-use online platform (e.g., XML, Json file) to send us the required data for simulating NTT. This include the field data and any conservation management practices (scenarios).
  2. We will convert your submitted data to NTT format for simulations. This includes conversion of your existing data archived at any possible format.
  3. Our automated programs will simulate your project scenarios.
  4. We provide the results back to you in XML or Json formatted files upon completion of the simulation process.

This procedure will enable you to simulate hundreds of fields and associated management practices without any need to input individual fields or scenarios in the NTT program. In order to use our services to use NTT at this scale, please contact us directly by sending an e-mail to saleh@tarleton.edu or call us at 254-968-9799 or 254-592-1975.

Fields
How can I download a project file off NTT?
The first time when you click on fields, it may take longer because the system is loading all the necessary soils information and initializing the field details. After that, since the data is cached, subsequent accesses are faster.
Soils
Are the estimated water quality outcomes (i.e., N, P, sediment loading) in the model are a function of soil properties?
Yes. APEX in NTT is a physical-based model. That means water quality and soil properties are directly related.
When I submit my map, I get an error that no soils were selected. Why?
The are two possible reasons for this:
1) The USDA-NRCS soil survey map data may not be complete for that specific location.
2) The soil data is incomplete. For example, the soil data returned from SSURGO might be missing the soil bulk density. We are continuously evaluating and resolving soils issues when they arise. If you encounter any issue, please contact us and let us fix the problem.
Does the NTT model reflect/estimate changes in soil properties that may occur due to adoption of soil health practices (e.g., no-till/reduced till, cover crops, nutrient management, & conservation crop rotation, etc.)? If so, which soil properties?
The answer is “yes”. We define soil properties as both the physical (e.g., soil texture or bulk density, etc.) and chemical (e.g., pH or cation exchange capacity, etc.) characteristics.

The following list of soil properties are among the majority of soil properties that change with adoption of soils health practices calculated by NTT program. However, most of these parameters are not presented in the result page at this time. We are working on a report to display some of these properties. In the meantime, please contact us if you are interested in these variables and we can help summarize them from your NTT project.

       Soil pH

       Soil Electrical Conductivity (EC)

       Cation Exchange Capacity (CEC)

       Soil Nitrogen ()

       Soil Phosphorous (organic and soluble)

       Soil Organic Carbon (SOC)

       Soil Texture

       Available Water Holding Capacity

       Bulk Density (BD)

       Saturated Hydraulic Conductivity

       Crop Yield
How is the slope for each soil determined?
NTT uses the 30m resolution Digital Elevation Model (DEM) data to calculate slope for each soil selected for your field. Note that the estimated slope used by NTT will likely vary from the slope as estimated by the SSURGO soils database.
How does my soil P test influence my results?
The soil P test results help NTT understand the phosphorus content of your soil. For example, if you have high soil P, your management scenarios may reflect reduced phosphorus applications. NTT will set the starting soil P value for year 1 of the simulation equivalent to your soil P test value. In this manner, the model will know that P is available in the soil even if it is not being applied in the scenario. NTT simulates each rotation over 35 years by looping the scenario continuously over the time period. The NTT simulation will re-set the soil P value to the user-supplied value each time the rotation is repeated. For example, if you have a 5-year rotation, the soil P value will be set to the user-supplied value on years 1, 5, 10, 15, 20, 25, 30 and 35 of the simulation. Thus, your soil P losses will be a function of your starting soil P value and the phosphorus management practices on your field, averaged over the period of simulation.
What if I don’t have a soil P test?
If you don’t have a soil P test, select “none” from the drop-down list. NTT will use a default starting soil P value. Soil P will be influenced by the user-supplied fertilizer and manure management practices reflected in the scenarios.
Operations
Can I plant multiple crops at the same time?
Yes. APEX, the model that underlies NTT, can simulate up to 10 crops at once. The most common application for this is early planted cover crops that are seeded into the main crop before harvest. To simulate a scenario like this, simply choose a plant date for your cover crop that is prior to the harvest of your main crop. You will want to select a seeding method such as aerial seeding of no-till drill that will result in minimal disturbance of the main crop.
How do I simulate a multi-species cover crop?
We are working on implementing a short cut for multi-species cover crops. In the meantime, to add a multi-species cover crop you will want to add a crop to your rotation (instead of using the cover crop function), select the first plant in the cover crop mix, planting date and end of season date (which is usually prior to planting date of the spring crop). Next, add a new crop to your rotation with a planting date one day after the first species in the cover crop mix (this minimizes confusion in the model), a kill date (the next day after). Another consideration is the seeding rate (an input in the planting operation). You will want to adjust the seeding rate of each species in the mix to represent its relative proportion in the mix. Please see the tips for adding a commercial cover crop/winter crop for how to properly place the end of season date within your rotation if the cover crop is planted in the last year of the rotation.
What is End of Crop Season?
The End of Crop Season operation tells the model that the crop is terminated. Without this operation, the model will assume that the crop will re-grow in the next crop season. Perennial crops such as hay, grapes, almonds, etc., will not have an end of season operation as they will re-grow after harvests. For annual crops, however, there should always be an end of crop season operation placed the day after the final harvest to indicate to the model that the crop is terminated.
How do I add a commercial cover crop/winter crop?
A commercial cover crop should be added as a normal crop, not using the “add cover crop” feature. By adding the crop manually, you will be able to specify fertilizer applications, tillage, and harvest operations, whereas the cover crop feature has a limited crop selection, and assumes that crop is not fertilized, tilled, or harvested.

Please note that when manually entering a winter crop you should be careful about the “end of season date”. If planting a commercial cover crop in last year of the rotation (e.g., year 3 of a 3-year rotation), then any operations that happen after December 31, including harvest and end of season, should be placed in year 1. Similarly, if you have only a single year rotation your plant and harvest date should both be in year 1. This is because the model runs the simulation on a continuous loop.

Below is an example of a one-year rotation with a cover crop/winter crop:

Year 1, May 1, Plant -- Corn
Year 1, October 15, Harvest -- Corn
Year 1, October 16, End of Season – corn (indicates to model that corn crop is terminated)
Year 1, October 17, Plant -- cover crop
Year 1 April 15, end of season -- cover crop (indicates that cover crop is terminated)
Why do operations dates only specify “year 1”, “year 2”, etc. and not an actual year?
APEX uses year one as the start of the simulation but translate it into real years according to the parameters set up in the Apexcont.dat file. In NTT, year 1 corresponds to 1990 and it will run for 35 years (until 2024 at this moment).
What happens if I do not enter the plant population in my planting operation for the crop?
NTT provides a default plant population from its existing databases if this field is left blank.
The composition for commercial fertilizer is defined as Element-N and Element-P. Does this mean pure N and pure P?
Yes. When applying commercial fertilizer, the user has the option of selecting “element-N” and/or “element-P”. These options allow the user to specify the total N and total P applied without specifying the form. However, users also have the option of specifying the type of commercial fertilizer applied. For these fertilizers, NTT shows the default fraction of N (which represents soluble N), and the fraction of P2O5 (not total P). NTT will convert P2O5 to total soluble P on the back end by multiplying it by 0.45. It is highly recommended that user select the commercial fertilizer from the provided list. This is because the specific ammonia fraction is associated with each specific fertilizer.
What is the nutrient content of manure fertilizer?
Manure fertilizer includes four major nutrients: organic N and P, soluble P and N. Also, the fraction of organic matter in manure is considered in NTT simulations. For each manure type, NTT has set defaults for the nutrient content of manure. Users have the option of editing the manure nutrient composition to more closely reflect the content of manure applied to their field.
In grazing operation, why does NTT ask for total animal units instead of total animals and what does that mean?
Animal Units are a standard unit of measurement where 1AU is equal to 1000 lbs. of animal live weight. For example, one beef cow corresponds to 1AU (1000 lbs.), one dairy cow is considered equal to 1.4AUs (1,400 lbs. each), and 1 sheep is considered equal to .2AUs (200 lbs. each). For example, sheep conversion unit is 0.2. That means 5 heads of sheep is equal to one head of beef.
What planting date should I use for permanent pasture (or orchard/grape crops)?
NTT requests a planting date for all crops. However, with perennial crops or pasture the planting date can be confusing since the crop is not planted every year. To reduce confusion, NTT supplies a default planting date for perennial crops. Users should know that the plant date for permanent/perennial crops is not influential in the model simulations (as planting occurs only once over the simulation) and thus should not impact your results significantly.
Management Scenarios
Why did my nitrogen/phosphorus/sediment loads go up after I applied conservation practices?
If your nutrient losses do not seem to match your expectations, you should take a look at the following:

1) Check your management files. Make sure that your dates are correct. Often when editing dates, users make mistakes with the dates of operations. For example, a tillage operation after planting. The order of operations will affect the model simulation. Please ensure that your dates correct.

2) If your management files are correct, you may be seeing one of the following phenomena
       a. I reduced nitrogen, but my nitrogen loads went up. Nitrogen reductions that cause a significant drop in yield may result in increased nitrogen losses from the field because crop uptake is reduced and more nitrogen is available to be lost to the environment.
       b. I put in a cover crop but my nitrogen loads went up or stayed almost the same. When you have tile drains on your field, cover crops may have the effect of reducing surface nitrogen losses but increasing nitrogen losses to tile drains. Or it’s possible that if you put in a commercial winter crop or manually added a cover crop you inadvertently simulated a year of fallow which usually causes increases in nutrient and sediment loads. This happens if the winter crop comes at the end of the rotation and you did not specify the harvest/end of season operation to occur in year 1. Please see “how do I add a commercial cover crop” for tips on manually adding a cover crop.
What does the Start and Stop Month and Year in Autoirrigation/Autofertigation Conservation Practice mean?
This allows you to specify the months when the irrigation or fertigation is applied in the field. Otherwise, the irrigation/fertigation event will not be triggered.
On the Conservation Practices page, under the Grass Buffer/Forest Buffer section, the following question is displayed: “Is the buffer area included in your AOI (area of interest)?” What does this mean?
This answer is asking of the area which is being designated as a buffer was included in the field boundary that you drew or whether the buffer assumed to be adjacent to the field boundary. If the answer is “YES”, NTT will subtract the area of the buffer from the field and consequently reduces the total annual yield for whole field. If your answer is “NO”, NTT will simulate a buffer that is adjacent to the field and would not affect the total yield.
What is meant by "Fraction of field controlled by pond/WASCB”?
This question is asked when you select the pond/WASCB option from the list of structural conservation practices. The question is asking for the fraction of the drainage area within the field that flows into the pond. This allows the program to determine how much water, sediment, and nutrients are trapped in the pond.
Why are the number of crops available limited and different in some states?
There are 120+ crops available in NTT databases. However, we included crops available for each state using two criteria: A) crops that are most cultivated in each individual state, and B) the crop has been validated based on local crop information.
I plant my cover crop after terminating my corn and/or soybean in fall and terminate my cover crop in March of next year. However, I do not see any effect of my cover crop on sediment and nutrient losses. Why?
When the cover crop is harvested early in late winter/early spring, it likely did not have enough time to grow to be effective. Try postponing your cover crop termination date to resolve the issue.
How do I simulate a land use change on my crop/pasture?
NTT is able to simulate the impacts of changes in land use. Users should create scenarios on the same field that represent the different land uses. For example, one scenario might represent a corn-soy rotation, and another scenario might represent pasture (or hay or trees). Comparing the simulation results from running these two scenarios will allow users to evaluate water quality/quantity changes when converting from one land use to another.
How do I simulate conservation cover/alley cropping?
In order to simulate conservation cover with crops such as trees/grapes, simply add your tree/grape crop to the rotation as usual. Next click “add another crop” and select “pasture” (to simulate grass planted between the rows). The conservation cover/pasture crop can be planted in same year as the primary crop. NTT will simulate both of these crops over the simulation period.
Results
What impact does the soil P test have on my results?
When you enter the soil P test, we use the P value as the starting value for the phosphorus in your soil. If you do not have a P test you may leave it blank and we will use default values. Because phosphorus is a stock in the soil and the simulation for the model is over a period of 35 years, the phosphorus stocks are influenced more by fertilizer and manure management on the field. The simulation of Soil P has been addresses in the recent version of NTT. Soil P value is “refreshed” at the beginning of the rotation throughout the simulation. This new routine provides better evaluation of the Soil P on water quality and crop yield in particular for those who may have reduced phosphorus applications on their field due to high soil P.
How do I interpret my tabular water quality report?
The tabular report shows the average annual nutrient losses and yields over the period of simulation. Your scenarios are simulated in the APEX model over a period of 30 years using historic weather and soils data from the SSURGO database. The tabular report shows the average losses/yields. You may customize this report by specifying the years of simulation that you wish to include, or by selecting “wet years” or “dry years” options which will show the average of the top quartile of wet or dry weather years, respectively. Users may also select which scenarios they would like to view and/or compare.
Is it possible to download my project results?
Yes. Please use the PDF download function in the results page to download a PDF copy of your project results.
What does Confidence Interval represent for the results?
The confidence interval (CI) represents the variation of weather and yearly changes in soil properties within the 35-year of simulation period. However, the CI value is most affected by variation in weather.
What to dry and wet years tabular reports represent?
To calculate the dry and wet year’s reports, NTT takes the annual averages of the 25% driest years over the period of the simulation (35 years). The same calculation is applied for wet years by taking the 25% wettest years and averaging them. These reports are meant to show trends in nutrient and sediment losses over wet and dry conditions for your region.
Weather
How often is the weather file updated?
The weather used for simulations in NTT is updated (expanded every year) with the information obtained from the (updated) PRISM site. The last update was completed in Dec. 2024.
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Frequently Asked Questions


This page provides the user frequently asked questions and answers about this website. The user can learn about more about NTT and its common questions regarding the usage of NTT by clicking on various topics listed in the page.

Listed below are sections about specific parts of NTT that are regularly asked about and that we, the Texas Institute for Applied Environmental Research, will answer your questions about these specific parts in NTT.

  • General: Questions and answers in general about NTT.
  • Projects: NTT projects and their features.
  • Soils: The usage of soils in NTT and other soil related topics.
  • Operations: NTT operations and operations that affect APEX results.
  • Management Scenarios: NTT scenarios and their usage on the NTT platform.
  • Results: NTT results and how they may be affected by different factors or variables set by the user.
  • Weather: NTT and the usage of weather data.
NTT References

Gassman, P. W., Williams, J. R., Wang, X., Saleh, A., Osei, E., Hauck, L. M., Izaurralde, R. C., Flowers, J. D. (2010). The Agricultural Policy/Environmental eXtender (APEX) model: An emerging tool for landscape and watershed environmental analyses. Transactions of the ASABE.


Tuppad, P., Santhi, C., Wang, X., Williams, J. R., Srinivasan, R., & Gowda, P. H. (2010). Simulation of conservation practices using the APEX model. Applied Engineering in Agriculture


Saleh, A., Gallego, O., Osei, E., Lai, H., Gross, C., & McKinney, S. (2010). Development and Application of a Modified NTT Tool for Water Quality Trading. In 21st Century Watershed Technology: Improving Water Quality and Environment Conference Proceedings, 21-24 February 2010, Universidad EARTH, Costa Rica (p. 1). American Society of Agricultural and Biological Engineers.


Saleh, A., Gallego, O., Osei, E., Lal, H., Gross, C., McKinney, S., & Cover, H. (2011). Nutrient Tracking Tool—a user-friendly tool for calculating nutrient reductions for water quality trading. Journal of Soil and Water Conservation, 66(6), 400-410.


Saleh, A., Osei, E., & Gallego, O. (2012). Evaluating Nutrient Tracking Tool(NTT) and simulated conservation practices. In 21st Century Watershed Technology: Improving Water Quality and Environment Conference Proceedings, May 27-June 1, 2012, Bari, Italy (p. 1). American Society of Agricultural and Biological Engineers.


Lal, H. (2014). The Nutrient Tracking Tool--A Historical Perspective and a Look to the Future. Resource Magazine, 21(3), 20-23.


Saleh, A., Gallego, O., & Osei, E. (2015). Evaluating nutrient tracking tool and simulated conservation practices. Journal of Soil and Water Conservation. https://doi.org/10.2489/jswc.70.5.115A.


Saleh, A., Osei, E., & Gallego, O. (2015). Evaluating Nutrient Tracking Tool and simulated conservation practices. Journal of Soil and Water Conservation. 115AJULY/AUGUST 2015 —VOL. 70, NO. 4


Burnett, J. R. (2015). Validation and verification of the Nutrient Tracking Tool for Yakima County, Washington. Tarleton State University.


Saleh, A., Niraula, R., Gallego, O., Osei, E., & Kannan, N. (2017, December). Nutrient Tracking Tool-A user-friendly tool for evaluating the water and air quality and quantity as affected by various agricultural management practices. In AGU Fall Meeting Abstracts.


Saleh A. and Edward Osei. 2018. Precision and water quality markets. Book chapter. Precision conservation. Agronomy Monograph. Pp.313-339.


Saleh, A., Niraula, R., Marek, G.W., Gowda, P.H., Brauer, D.K., Howell, T.A. 2018. Lysimetric evaluation of the APEX Model to simulate daily ET for irrigated crops in the Texas High Plains. Transactions of the ASABE. 61(1):65-74. https://doi.org/10.13031/trans.11938.


Nelson, A. M., Moriasi, D. N., Talebizadeh, M., Tadesse, H. K., Steiner, J. L., Gowda, P. H., & Starks, P. J. (2019). Comparing the Effects of Inputs for NTT and ArcAPEX Interfaces on Model Outputs and Simulation Performance. Journal of Water Resource and Protection, 11(5), 554-580.


Guo, T., Confesor Jr, R., Saleh, A., & King, K. (2020). Crop growth, hydrology, and water quality dynamics in agricultural fields across the Western Lake Erie Basin: Multi-site verification of the Nutrient Tracking Tool (NTT). Science of The Total Environment, 138485.

User Manuals and Technical Documentation


NTT/User Manual

NTT Technical Documentation

Economic Technical Documentation

APEX User Manual
  • Site Validation Experimental (Farm)

    Verification of APEX Parameters and NTT for Minnesota
    NTT Comparison to COBS Iowa
    Crop growth, hydrology, and water quality dynamics in agricultural fields across the Western Lake Erie Basin: Multi-site verification of the Nutrient Tracking Tool (NTT)

  • State Level Validation

    Alabama
    Arizona
    Arkansas
    California
    Colorado
    Delaware
    Georgia
    Idaho
    Illinois
    Indiana
    Iowa
    Kentucky
    Michigan
    Minnesota
    Mississippi
    Missouri
    Montana
    Nevada
    New Hampshire
    New Mexico
    New York
    North Carolina
    Ohio
    Oklahoma
    Oregon
    Pennsylvania
    Rhode Island
    South Carolina
    South Dakota
    Tennessee
    Texas
    Utah
    Vermont
    Virginia
    West Virginia
    Wisconsin
    Wyoming

Contact Information

For questions or comments regarding the Nutrient Tracking Tool (NTT), please contact:

  • Ali Saleh
  • Executive Director
    P.O. Box T410
    Tarleton State University
    Stephenville, TX 76402
    (254)-968-9079 (Phone)
    (254)-968-9790 (Fax)
    saleh@tarleton.edu

For technical questions or comments regarding the Nutrient Tracking Tool (NTT), please contact:

  • Oscar Gallego
  • IT Manager II
    P.O. Box T410
    Tarleton State University
    Stephenville, TX 76402
    (254)-968-9787 (Phone)
    (254)-968-9790 (Fax)
    gallego@tarleton.edu