SYSTEMS PROGRAMS FOR THE ANALYSIS OF NONURBAN, NONPOINT SOURCE POLLUTANTS IN THE MISSOURI BASIN REGION by A. Eugene Vandegrift Shen-yann Chiu Midwest Research Institute 425 Volker Boulevard Kansas City, Missouri 64110 for the Office of Water Programs U.S. Environmental Protection Agency Suite 906, Lincoln Towers 1860 Lincoln Street Denver, Colorado Attn: Mr. Keith Snyder EPA Contract No. 68-01-0159 MRI Project No. 3572-C 3 May 1973 ------- DISCLAIMER This report has been reviewed by the Office of Water Programs and approved for publication. Approval does not signify that the contents necessarily reflect the views and policies of the Office of Water Programs, nor does mention of trade names or commercial products constitute endorsement or recommenda- tion for use. ------- PREFACE This report was prepared and submitted in partial fulfillment of EPA Contract No. 68-01-0159 which was monitored by Mr. Keith Snyder. In the program, data related to nonurban, nonpoint sources of pollu- tants were collected, evaluated, compiled, and organized. The data are now available on computer tape and also in a data bank. In addition to this report, a User’s Manual has been prepared (and is being submitted as a separate document) for the computer programs which were developed to create, update, and use the data storage bank devel- oped during the project. Complete printouts of the data bank (COUNTY MASTER FILE and STATION MASTER FILE) have been forwarded to Mr. Snyder, Mr. Robert V. Brown, and Dr. Marshall Rose. Also, magnetic tapes of the COUNTY MASTER FILE and STATION MASTER FILE were sent to Mr. Snyder. The work was conducted in the Environmental Sciences Section of the Physical Sciences Division. The report was written by Dr. A. E. Vandegrift and Dr. S. Y. chiu with assistance from Mr. Richard Salmon, Mr. Duane Dieckman, and Mr. Evan Stewart, Approved for: MII 7EST RESEARCH INSTITUTE H. M. Hubbard, Director P ysical Sciences Division 3 May 1973 iii ------- No Page iv ------- TABLE OF CONTENTS Page Summary. . . . . . . . 1 Introduction 5 RelatedStudies 5 Physical Characteristics of the Missouri River Basin. 6 Approachtothe Study.. . . . . . . . . , . . . . . . . 8 ReportOrganization. 10 Identification of Data Sources and Collection of Data. 11 Evaluationof Data. . . . . . . . . . . . . . . . . . . . . . . 17 Organizationof Data 21 Data Files . . . 25 Co mnputerSoftware.......... 26 Methods for Updating the Data System 39 Identification of Data by Source 40 Conclusions 43 Recommendations . . . 45 Appendix A - Data Sources Investigated . . . . . . . . . . . . . 47 Appendix B - Individual Contacts . . . . . . . . . . 77 Appendix C - Water Quality Stations Selected . 85 Appendix D - Selection of Important Parameters . . . 93 Appendix E - MRI Station and River Codes. . 101 Appendix F - Maps Showing County-Watershed Relationships for Subbasins 31 through 42 . . . . . . . 111 V ------- SUMMARY A program for the analysis of nonurban, nonpoint source pollutants in the Missouri River Basin was conducted at Midwest Research Institute under the sponsorship of the EPA. The ultimate goal of the program is to develop system models that can be used by EPA to assess the impact of nonpoint source pollutants on the pollution of surface water, and to facilitate long-range planning for pollution control. EPA is deeply concerned about (a) the influence on water quality of • substances introduced into surface water courses from the agricultural sector, and (b) the associated policy decisions about their abatement. Specifically, questions are frequently asked about the contribution of fertilizers to nutrient level in waterways, and the value of treatment of waste from point sources for improving water quality if agricultural • pollution continues unabated; in both cases careful studies have to be conducted-before final answers can be given. MRI’s program has three phases. Phase I (the work conducted to date) involved efforts to (1) provide physical data in order to establish relationships that can be used to predict and assess water quality prob- lems, establish abatement priorities, and determine effects under various conditions; ‘and (2) provide economic base data that can be used for cost projections, economic analyses, incentive development, and EPA policy determination for the various components of nonpoint source pollution. Phase I and Phase III involve development of models, analytical tools, and computer programs that EPA can use in planning and implementing ef- fective pollution-control programs. These analytical tools will allow EPA to choose between various alternatives in carrying out its mandate to improve the water quarity in the basin. This report describes the results accomplished in Phase I of this pro- gram. The principal results are highlighted in the following paragraphs. Determination of Data Needs and Data Sources An extensive study was conducted to evaluate the types and sources of data affecting the quaiity of surface waters in the Missouri River Basin. The sources were eva?.uated with respect to the quantity and quality of the data as well as their accessibility. As a result of our information search, we concluded that data categories should include: water quality, hydrology, climatology, topography, soil classification, land use, live- stock distribution, fertilizer use, pesticide use, and demography. 1 ------- Personal communications were established with national, regional, and local agencies which compiled and/or analyzed these data. The sources explored by MRI include: EPA, USGS, Bureau of Census, USDA, NOAA, Corps of Engineers, and State Pollution, Health and Agriculture Agencies. We found that the majority of data needed are available in a computer- processible form, such as STORET (water quality and stream flow data), Census of Agriculture (land use and livestock data), Conservation Needs Inventory (land use and soil classification), and NOAA (precipitation data). Other necessary data not available on tapes were also collected, or estimated. Pesticide data were obtained through work with the county agents. Preliminary Data Evaluation This task was conducted concurrently with the collection of data, to establish our confidence that the collected data would be useful for model development. Several two-parameter correlations were prepared for this purpose. We also evaluated the various data parameters when- ever possible by comparing the same piece of data from different data sources. Data Compilation The significant achievement of this study has been the compilation of all pertinent data in a logical fashion, which allows easy access for whatever analysis might be desired. Data are collected and classified on the basis of three separate systems: data on water quality and hydrology come from the stream stations at which they are monitored; data for slope, soil classification, land use, livestock distribution, fertilizer use, and pesticides use are available by counties; and precipitation data are from each weather station. We related all data to a coon base--the watershed . To achieve this, the county-watershed relationships and county-weather station relationships were determined and utilized to transform data from counties or weather stations into the watershed. The data systems developed directly re- lates water quality parameters to all physical, economical and climato- logical parameters. The present file has water quality data and hydro- logical data for 1968, 1969, and 1970, and land use data for 1969. How- ever, provisions were made for updating when new data become available. 2 ------- Two major computer files were produced for this program. The COIJNTY MASTER FILE has one record for each of the 438 counties in the Missc’uri River Basin. Records f or each county consist of data in their land use, fertilizer and pesticide application, soil classification, livestock distribution, topography, and climatology. The STATION MASTER FILE contains information unique to an individual station and the watershed which impacts that station. In this file, the station location, the water quality and hydrological data, the area and physical character- istics of the watershed, and all information available for counties in the watershed as recorded in the COUNTY MASTER FILE are compiled, Two hundred thirty-three water quality stations were selected in this pro- gram. These stations were chosen on the basis of their locations, and the type and frequency of their measurements. Report Organization The document submitted herein consists of two parts: the Final Report and the Data Bank. The Final Report describes the accomplishment of Phase I efforts, including the result of literature search and personal contact, and types and characters of data collected, evaluation of data, the methods of data compilation, and use of these data for development of analytical tools. The Data Bank consists of COUNTY MASTER FILE and STATION MASTER FILE, magnetic tapes containing the information of these two files, and the User’s Manual. Also included are the more extensive raw data files (magnetic tapes) from which the Master Files were com- piled. Conclusions and Recommendations Principal conclusions of Phase I are: - -Methodology developed to treat nonurban situations is unique and use- ful for similar studies in other areas of the nation. --Preliminary evaluation indicates that data collected are sufficient in their quality and quantity for the development of system models. --Available data are sufficient for economic project ons. On the basis of these conclusions, we recommend tI at Phases II and III of this program should be initiated to further evaluate the data and to 3 ------- develop system models which relate water quality and hydrologic parain- eters to physical, climatic, and economic factors. These models will allow EPA to make economic and planning decisions concerning nonurban, nonpoint pollution sources in the Missouri River Basin. 4 ------- INTRODUCTION EPA is deeply concerned about the amount and proportion of agricultur- ally generated pollution in running streams and rivers, and needs more factual information on these matters as a basis for policy decisions affecting, for example, the use of fertilizers or pesticides in a given area. As a result of this concern, EPA has sponsored an investigation by Midwest Research Institute (MRI) to determine if data exist which will supply the factual information EPA needs, and then (assuming the data exist) to compile and organize these data into a computer data bank. This report describes HRI’s effort to collect, analyze, and or- ganize data regarding nonurban nonpoint sources of pollutants in the Missouri Basin region. Background on why the study is needed, where it was done, and how it was done, as well as, how the report is organ- ized are presented in the remainder of the Introduction. Related Studies State and local officials as well as the GAO* have contended for some time that agriculture-related pollutants from natural runoff affect the water quality of the Missouri River to a far greater extent than do ef- fluents from primary-treated municipal and industrial waste along the main stem. Any expected enhancement in water quality from secondary treatment, they say, will be obscured by the magnitude of pollutants from agricultural sources. EPA has, therefore, initiated this study to obtain data that will allow it to relate, water quality to Land use practices or other economic and physical parameters. The objectives of the program discussed in this report were: 1. To provide economic base data that could be used for cost projections, economic analyses, incentives development, and Environmental Protection Agency policy determination of the various components of nonpoint source pollution. 2. To provide physical data regarding climate, topography, and land use practices in order to establish relationships that can be used to predict and assess water quality problems, establish abatement priorities, and determine effects under various conditions. * “Alternatives to Secondary Sewage Treatment Offer Greater Improvement in Missouri River Water Quality,” GAO Report B-l25042, 6 January 1972. .5 ------- 3. To combine (1) and (2) to provide guides regarding the likely ef- fects of changes in economic structure or land use practices on water quality. Several earlier studies were conducted elsewhere to develop models for urban runoff. However, only one or two attempts have been made to in- vestigate nonpoint, nonurban pollutant sources.* Studies have also been conducted to collect and organize certain of the data that were needed for the present study: for example, the Type I Comprehensive Framework Study of the Missouri River Basin conducted by the Missouri Basin Inter- Agency Committee (MBIAC). However, these data collections have not been extensive enough for the purposes of the present program, and have been used mainly as the basis of projections of water- and land-related re- source needs. EPA has also recently initiated a number of studies to apply existing detailed water quality models to Important stretches of various river basins around the country. Although such studies are being initiated for the upper South Platte River, the upper Mississippi River, the Iowa-Cedar River Basin, etc., they will not emphasize non- urban, noripoint pollution problems. We therefore believe that this program is the first step in the development of a methodology which will facilitate the evaluation of water quality management alternatives in cases where nonurban, nonpoint factors are significant. Physical Characteristics of the Missouri River Basin The land area which is drained by the Missouri River and its tributaries consists of approximately 530,000 sq miles with all except about 10,000 sq miles in the United States. This land area covers approximately one- sixth of the contiguous United States, and includes all or parts of 10 different states. The basin contains about 113 million acres of tillable cropland, about 175 million acres of grassland, approximately 45 million acres of woodlands and forest, and approximately 7 million acres which have been utilized for urban or nonurban development purposes. There are several different ways of subdividing the Missouri Basin, and we have chosen that used by the Office of Water Data Coordination (OWDC). The OWDC divides the basin into 13 subbasins designated subbasins 31 to 43. •These subbasins cover the northwestern portion of Missouri, the * “Agricultural Pollution of the Great Lakes Basin,” EPA/WQO, Report No. 13020-07/71. “DeterminatIon of Land Runoff Effects on Dissolved Oxygen by Mathematical Modeling,” “Douglass-Wallace, Ph.D. Thesis, Uni- versity of Iowa, August 1971. 6 ------- northern portion of Kansas, all of Nebraska, the western half of Iowa, the southwestern tip of Minnesota, most of North and South Dakota, the eastern portion of Montana, and the northwestern portions of Colorado and Wyoming. The Missouri River itself flows 2,315 miles from its formation at the junction of the Jefferson, Gallatin, and Madison rivers in Montana to its mouth just above St. Louis, Missouri. Seven major tributaries flow into the Missouri from the south and west. These are the Yellowstone, the Cheyenne, the Niobrara, the Platte, the Kansas, the Osage and the Gasconade rivers. Five tributaries flow in from the north and east. These are the Milk River, the James, the Big Sioux, the Grand and the Chariton. The Missouri, discharges an average of 83,000 cfs at its mouth, but its maximum record flow has been as great as 900,000 cfs and the minimum flow as low as 4,000 cfs. There are three major physiographic divisions within the Missouri River-- the interior highlands, the interior plains, and the Rocky Mounta Ln Sys- tem. Within the basin, the Rocky Mountain System division includes parts of the Northern Rocky Mountains, Middle Rocky Mountains, Wyoming Basin, and Southern Rocky Mountains provinces. The Interior Plains division includes parts of the Great Plains and the Central Lowlands. Distinct topographic features within the Great Plains provinces are the Black Hills of South Dakota and Wyoming and the Sand Hills of Nebraska. That portion of the Interior Highlands division within the basin is characterized by its Ozark Plateau provinces. In the Missouri River Basin, climate has a great influence on the liv- ing habits and socioeconomic structure of the people. Obviously, it has a strong influence upon the basic agricultural industry, primarily because of the seasonal and variable regimen of precipitation, temper- ature and wind. The cl.fmate within the, basin is determined largely by the interaction of three great air masses which have their origins over the Gulf of Mexico, the northern Pacific Ocean, and the northern polar regions. They regularly invade and pass over the basin throughout the year, with Gulf air tending to dominate the weather in the sunmier and polar air dominating 1.n the winter. This seasonal domination of the air masses, and the frontal activity caused by their colliding with each other, produce the general weather regimens found within the basin. Primar- ily because of its midcontinental location, the basin experiences weather that is known for its fluctuations and extremes. Also, there 7 ------- are variations between areas within the basin. Winters are relatively long and cold over much of the basin, while sununers are fair and hot. Spring is cool, moist and windy; autumn is cool, dry and sunny. Aver- ages are misleading, for seldom does “average weather” actually occur. Instead, weather tends to fluctuate widely around the annual averages, with the occurrences and degrees of fluctuation being unpredictable. The average annual precipitation varies from about 40 in. in parts of the Rocky Mountains and in southeastern parts of the basin, to as low as 6-12 in. inunediately east of the Rocky Mountains . Complicating the annual variations, there is a wide variation in the basin pattern of monthly precipitation. Winds in the basin are the rule rather than the exception, particularly in the plains area. Average wind velocities at 10 miles/hr are preva- lent over much of the basin. In the plains area, strong winds accom- panied by snow sometimes create blizzard conditions, dangerous to both man and livestock. High winds that occasionally prevail during periods of high temperature, decrease the moisture, destroy crops, and desiccate range land within a few days. Parts of the basin, particularly the southeast, are subject to cyclonic and tornadic winds that occasionally do considerable damage. Approach to the Study To meet the program objectives, the following data categories were investigated: water quality, climatology, hydrology, land use, topog- raphy, soil classification, livestock distribution, pesticide use , and fertilizer use . (We also have demographic data available if they are needed.) In developing a logical plan of attack, this program was orig- inally divided into five tasks: 1. Determination of available data sources; 2. Collection of available data; 3. Compilation and cross-correlation of data; 4. Evaluation of data; and 5. Preparation of data bank. The steps necessary to accomplish these tasks are presented in Figure 1. 8 ------- county— Weather Station Relation Matrix Figure 1 - Phase 1 Program Flow Sheet 9 ------- After the first 8 weeks of the program, it was apparent that substan- tially more data existed on magnetic tapes than had previously been supposed. Therefore, in conference with the Project Officer, it was decided that the most effective use of available resources would be to concentrate on development of the data base and a data storage for- mating system. Using this approach, it was felt that we would have substantial quantities and types of data on automatic data processing tapes in an easily accessible format that could then be analyzed with ADP systems on a much more sophisticated scale than the originally anticipated two-parameter correlations. The effect of this action was to set Tasks 3 and 4 at a later point in the system following Task 5. Although the ultimate impact on resources in terms of this contract was not known at that time, it was decided that if parts of Tasks 3 and 4 could not be completed with available resources, the resulting ability to upgrade and extend the analyses more than offset any reductions in these two tasks. One of the significant problems with the data that we found available was that physical data, such as water quality parameters, were measured on the basis of the water quality station location, land use parameters such as livestock distribution, fertilizer use, and soil types, are all on the county basis; while climatological data, such as rainfall amount, are available on the basis of weather stations. For the purpose of data correlation it was necessary to relate all data to a single base . The data storage system we developed is based on watersheds . This system will be explained more fully in “Organization of Data” of this report. Report Organization In the subsequent sections of this report, we discuss how the needed data sources were identified and the methods of data collection that we used; the method of organizing the data; the data-storage techniques; the conclusions that we have reached; and our recommendations. 10 ------- IDENTIFICATION OF DATA SOURCES AND COLLECTION OF DATA The data categories selected for this program, as given in the Intro- duction, were selected on the basis of needs for the development of empirical models or correlations. Such correlations can be used to develop a systematic methodology, which, in turn, will facilitate the evaluation of water quality management alternatives in cases where non- urban, nonpoint factors are significant. In other words, the data needs were based on requirements to develop appropriate models, analyt- ical tools, and computer programs to be used by EPA in planning and implementing effective pollution control programs. Information was gathered from a search of literature, both published and unpublished, and by telephone contact, and personal visits with knowledgeable persons in government agencies including EPA, USGS, NOAA, USDA (SCS, ASCS), OWDC, Corps of Engineers, Bureau of Reclamation, Bureau of Census, Missouri Basin Inter-Agency Committee (MBIAC), and state and local health, pollution, and agriculture agencies, and in universities. From this extensive search, we found a large number of data sources including inventories which contained data pertinent to this program. For each inventory or other information source, we con- ducted a thorough investigation into the types of data available, method of data storage, techniques that could be used to retrieve the data, and, if possible, methods by which the data were obtained (i.e., sam- pling and analysis techniques). Information resulting from these in- vestigations was subsequently used in selecting the data sources for input to our data system. We identified numerous sources of water quality data for the Missouri River Basin. Among these were the EPA, the MBIAC, USGS, the Army Corps of Engineers, the Bureau of Reclamation, state water pollution control agencies, water- and waste-treatment plantS, etc. At each of these sources, we interviewed persons in charge, studied their data, and evaluated its utility and availability for this program. We found, for example, that treatment plant data are generally stored in state files or by the treatment plants themselves, and that these data are generally not published and must be copied manually from their files. On the other hand, the EPA’s STORET system is in computer-processible form and collects data from many (although not all) of these sources and is the single most comprehensive source of water quality data avail- able. We, therefore, elected to use STORET as the primary source of water quality data for this program. 11 ------- An extensive investigation was also made of land-use data sources in- cluding the Bureau of Census, the Bureau of Reclamation, U.S. Depart- merit of Agriculture--the Statistical Research Service, the Agricul- tural Stabilization and Conservation Service, the Forest Service and the Soil Conservation Service, and state departments of agriculture. Again appropriate persons in each agency were contacted and samples of data from each of these sources were investigated. Based on the accessibility, estimated accuracy, and completeness of the data, we selected the Census of Agriculture (1969) (the Bureau of Census), and Conservation Needs Inventory (1958 and 1967) (the Soil Conservation Service), as the primary sources of land-use data for this program. We found that some data needed in this study had not been collected or were still in the form of maps, tables, graphs, etc. In these cases, special efforts were made: (1) to contact people who might have, or be able to estimate, the needed data; and (2) to search the literature for information from which the needed data could be generated using various estimating techniques. From the type of storage and availability, we classified data avail- ability into three different categories. The first category includes those which are available ‘on magnetic tapes, such as NOAA (precipita- tion), Conservation Needs Inventory (1958 and 1967), Census of Agri- culture (1969), and STORET. Magnetic tapes of these inventories were obtained, from which, the needed data retrieved. Data in the second category are those available in published literature in the form of tables, graphs, maps, etc., from which the needed data were tabulated and transformed into computer processible form. Data included in this category are stream channel slope--from topographic maps and river profiles; rainfall intensity--from NOAA’s Rainfall Frequency Atlas; Soil Infiltration Rate--from soil maps; and county fertilizer use data (for the states: Colorado, Iowa, Kansas, Missouri, and Nebraska)-- from materials published by each state department of agriculture. The third category of data includes thosewhich did not exist in any reposi- tory, such as county pesticide use data, and fertilizer use data for counties in North and South Dakota, Wyoming, Montana, and Minnesota. In these cases, we contacted county agents and other knowledgeable persons to obtain their estimates of pesticide or fertilizer usage. We also developed methods to estimate these data to check results ob- tained from county agents, etc., or to use when no other estimate was available. 12 ------- Data from all sources were retrieved, transformed, developed, or esti- mated, and subsequently organized and stored in a data bank which con- sists, on one hand, of information on natural factors and man’s activ- ities which contribute nonpoint source pollution, and, on the other hand, of water quality and hydrologic information, of the entire 10- state Missouri River Basin. This data bank which will facilities the analysis of cause-and-effect relationship is described in detail in- cluding its organization and format in the section, “Organization of Data.” Table I presents a list of the major sources from which we obtained the data. This table also indicates which parameters were obtained from which data source. Details describing the literature we searched, people and agencies that we contacted, data inventories that we have investigated, contacting methods for county agents, and methods that we developed to estimate data are given in Appendices A and B. Of the several data sources listed in Appendix A, we used those where the information was most accessible, complete, accurate or was the only source available. Important points concerning the data collected in this program are: 1. The data collected, including water quality, stream flow, land use, precipitation, etc., are primarily for the year of 1969. Selection of this year was made based on the fact that: (a) considerably more water quality data are available for this year than any of the previous years, and (b) it is the year when the most recent Census of Agriculture was made. 2. We selected a total of 233 water quality stations which collected suitable data for this program. The majority of these stations mea- sured streatnf low in addition to the water quality. 3. There are 438 counties in the basin. For each of them we were able to collect or estimate data for land use, soil type, ground slope, rain- fall intensity, livestock distribution, fertilizer use, and pesticides use. 4. There are 2,448 climatological stations in the 10 states in the basin which have precipitation data available for this program. 13 ------- TABLE I - TYPES AND MAJOR SOURCES OF DATA Data Source Date Category Agency Format Parameters Water Quality EPA STORETA’ Sediment, Nutrient, Organic, Pesticides, and Microorganism Concentrations Hydrology EPA STORET. ’ Streainf low Rate Climatology NOAA Precipitation J Seasonal and Yearly Precipitation Data Tape NOAA Rainfall Frequency Rainfall Intensity Atlas of the U.S. Topography SCS Conservation Needs Land Slope Percent Class Inventory, l967. i USGS Topographic Map Main channel Slope Corps of River Profile Main Channel Slope Engineers Soil Classification SCS Conservation Needs Soil Capability Class, Soil Erosion Inventory, l967 ’ Class, and Soil Name SCS Hydrologic Soil Group Soil Index Missouri Basin Infiltration Data Soil Infiltration Rate Inter-Agency Commit tee Land Use Bureau of Census Census of Agriculture, Crop Acreage l 969 .W ------- TABLE I (Concluded) Data Source Data Category Agency Format Parameters Livestock Bureau of Census Census of Agriculture, Cattle, Hogs, Sheep, Horses, Chickens, l969. 1 and Commercial Feedlots Fertilizer Use Bureau of Census Census of Agriculture, Lime Usage l969. ’ State Fertilizer Tonnage Nitrogen, Phosphoric Pentoxide, and Department of Report, 1969 Potash Usages Agriculture Pesticides Use County Agent NRI Questionnaire Insecticides and HerbLctdes Usages a/ Available in computer-processible form. ------- No Page 16 ------- EVALUATION OF DATh The data obtained in this program were evaluated by two methods: (1) a comparative evaluation of the same data from different data sources; and (2) an evaluation based on simple, two-parameter correlations of data collected. We evaluated the various data parameters whenever possible by comparing the same piece of data from different data sources. The crop acreage and number of livestock, which constitutes one of the most important data categories in this program, were repotted independently by the state departments of Agriculture and the Bureau of Census. Data from these two sources were compiled and compared, and did not show signifi- cant deviation. This comparison increases our confidence in the relia- bility of the land use data available. We have randomly selected data from nine counties in the basin, which are shown in Table II. For those data which could not be obtained from multiple sources, re- gression methods combined with physical judgment were used to assess the quality of available data. As an example of those regression techniques, correlation between BOD in the streams (lb/day) and number of cattle per county were success- fully developed. The equation for this relation is: BOD 4.19 x iO ’ (Number of Cattle)L 45 The coefficient of correlation for this relation is quite high at 0.86. Several other correlations were also satisfactorily developed: Nitrate Concentration versus Fertilizer Use Sediment Yield versus Land Use Fertilizer Use versus Crop Value Pasture Land versus Herbicide Use Pesticide Use versus Fertilizer Use Details of these correlations have been presented in the Phase IA report of this program. 17 ------- TABLE II County State Logan Colorado Source State (1966) Census Corn 51 54 Sorghuns 13 6 Wheat 244 210 Soybean NA 0 Hay Cattle 93 162.800 86 185,955 flogs 7,200 12,482 chickens NA 1.4,859 Sheep 4,400 5,355 Buena Vista Iowa State ( 1969) Census 194 207 0.3 0 0 0 144 142 20 19 NA 67,635 NA 162,768 NA 96,364 NA 1.3,318 AP ACRICULTURE (1969) DATh OF StATE DATA WITH Clay Vernon Powder River Kanass Missouri Montana State State State ( 1970) Census ( 1968) Census ( 1969) Census 26 21 61 72 0.5 0 101 91. 28 29 NA 0 125 129 50 35 41 35 8 8 97 85 NA 0 45 35 57 48 87 82 58,000 52,202 62,800 63,527 70,000 73,842 39,000 33,713 22,800 31,097 400 471. 166,000 124,054 NA 24,468 6,500 3,027 1,500 1,922 NA 1,826 56,000 53,1.22 Antelope Enz ns Nebraska N Dakota State State ( 1969) Census ( 1970) Census 227 207 44 34 11 8 NA 1 2 2 167 169 23 19 0 0 105 80 190 1.35 90,000 94,560 69,000 66,834 82,970 78,510 12,000 6,358 105,000 61,571. 38,000 35,540 5,300 5,080 1,020 1,710 Kingsbury ( 1970 ) 153 3.5 5 34 29 NA 0 83 74 80,000 67,629 44,300 38,802 75,000 40,104 32,400 29,990 Niobrara Wyoeing State ( 1968J Census 0.8 1 NA 0 14 13 - NA 0 63 54 56, 827 1,478 2,279 61,058 Unit. Crop - square mile, NA. Not Available NA NA livestock - head. ------- Pertinent correlations developed by other researchers were also located. Streamf low equations* developed by USGS for each state in the basin have been obtained. These equations are the result of multiregression analy- sis of the type required to develop models relating water quality to other physical and economic parameters. The existence of these equations, plus the correlations obtained in the program, raises the probability that we will be able to use available data to develop meaningful models for the Missouri River Basin. * See Appendix D. 19 ------- No Page 20 ------- ORGANIZATION OF DATA Data collected in this program can be classified on the basis of three separate systems: data on water quality, and hydrology come from the stream station at which they were monitored; data for slope, soil clas- sification, land use, livestock distribution, fertilizer use, and pesti- cides use are available by counties ; and precipitation data are from each weather station . For the purpose of data correlation, it is neces- sary to relate all data to a conunon base. The base we chose was the watershed. Consequently, data which are based on county or weather sta- tion must be transformed into watershed data. The data transformation was accomplished in six steps: 1. Identification of the weather stations in each county. 2. Selection of the water quality stations. 3. Definition of the boundary and area of watersheds which directly influence the measurement of the selected water quality stations. 4. Location of the counties and the portions of the counties covered by the watershed. 5. Allocation of the county data into the county-watershed intersections (hereafter called “zones”), and 6. Summation or averaging of the data for each zone in the watershed to form the data base for that watershed. Step 1 was done by referring to the NOAA’s publications* which show the locations of all weather stations in the basin. Information obtained at this step was subsequently used to determine the county precipitation data by averaging those from the stations in the county. Steps 2, 3, and 4 were carried out as follows: An inventory of water quality stations in the basin was retrieved from the STORET. Selection of stations was made based on their locations, and the type and frequency of their measurements. As a result, 233 sta- tions were selected. * For example, “Climatological Data” Annual Summary for Colorado, 1969. U.S. Department of Commerce, National Oceanic and Atmospheric Administra- tion, Environmental Data Service. 21 ------- Each of these selected stations was located on the maps prepared by the OWDC.* From the maps, the boundary of watershed which related to the selected station, and the boundaries of zone in the watershed, were determined. The OWDC divides the Missouri River Basin into 13 subbasins and desi- nates them 31 to 43. Naps were available for each of these subbasins. Figure 2 presents the map for subbasin 43, which was subdivided as de- scribed. The dots indicate the particular water quality stations. The watershed boundaries and county lines are also indicated. Maps for sub- basins 31 to 42 are presented in Appendix F. The watershed and zone areas were determined by tracing a planimeter on the OWDC watershed maps. In addition to the area, average distances from centroid of zone to the respective monitoring station were also determined. The distance information will be used when the effect of river self-purification is to be investigated . For example, the BOD monitored at a water quality station is more strongly influenced by the zones that are closer to the station. For each of these stations, the identification code given by MRI (de- tails of which are discussed in Appendix E) and codes used by different agencies, the location, the area, and the composition of the watershed in terms of zones, have been determined and recorded. Table III shows an example of these records. The selected station, 5720006 , is in subbasin 32 and is on the Smokey Hill River near Russell, Kansas. The watershed for this station includes 100 square miles of Russell County, 330 square miles of Ellis County, 200 square miles of Rush County, and 57 square miles of Ness County. The drainage basin for this station has an area of 6945 square miles which includes the above described watershed and the watersheds for the im- mediate upstream stations 5720001 (on the Smokey Hill River) and 5723001 (on the Big Creek), respectively. The code and the distance to the next downstream station (5720011) are also recorded. All this information was stored in computer and subsequently used to construct our data system. The approach we took to allocate county data into the zones (Step 5) is based on the assumption that these data are uniformly distributed in * “Catalog of Information on Water Data - Naps Showing Locations of - Water Quality Stations,” Edition 1970, U.S. Department of Interi9r, Geological Survey, Office of Water Data Coordination. 22 ------- 1% ii l’ IJ Figure 2 - Station-Watershed-County Relationships for Subbasin 43 ii / -1 I \ ) ) iç’ S / 23 ------- TABLE III STATION INFORNAT ION RECORD County-Basin Records MRI Station Code: 5720006 Tributary Rank: 3 STORET Station No.: 06864000 OWDC W.Q.S. No.: 50232 X4DC S.W.S. No.: 5770 S.W.S. No.: 0686400 Sub-Subbasin: 32-C Total Tributary Area: 6.965 Stream: Smoky Hill River Location: Russell, Kansas Lat. -Long.: 38 46 36 - 98 51 16 • Agency Code: L12WRD • Agency Code: 112WRD Square Miles (including immediate water- shed area and watershed area of next upstream sta- tions) Immediate Watershed Area: County Stats Cods Zone Area (ss milss Distance (mi1es tussell Kansas 20167 100 8 llis Kansas 20051 330 30 tush Kansas 20165 200 36 ‘ess Kansas 20135 57 The Next Upstream Selected Stations • 62 MRI Code Agency Code and Number Stream Distance (miles) 5720001 112WRD 06862700 Smoky Hill River 46 5723001 1I2WRD 06863500 Big Creek he Next Downstream Selected Station 34 MRI Code Agency Code and Number Stream Distance (miles) 5720011 112wRD 06864500 Smoky Hill River 36 24 ------- each county.* Data such as crop acreage, number of cattle, fertilizer use, etc., for each zone were calculated through multiplication of each parameter value by the percentage of zone area in the county. Data for watershed were then obtained by summing zone data of all zones located in the watershed (Step 6). For data such as ground slope, soil erosion class, precipitation amount, etc., we assumed that each zone in the same county has the same data value. A weighted average (with respect to area) of these data types for all zones in the watershed was then determined to arrive at the data for the watershed (Step 6). Data Files Based on the need for development of a data system in this phase, and for use in subsequent statistical and system analysis, two major com- puter files were produced, and these constitute our data report. COUNTY MASTER FILE : The first file, called the COUNTY MASTER FILE, consists of 728 characters per county record, with one record for each county in the Missouri Basin. The information in the county record includes location, land characteristics, land use (crops, fertilizer, livestock and poultry, etc.). For this report, the COUNTY MASTER FILE will contain data for 1 year, 1969. It is anticipated that county records for years other than 1969 could be developed in the same format. There are four major sources for the data in the COUNTY MASTER FILE. The first data source is from manual input. Information relating to location, identification, fertilizer use, herbicide-insecticide-fungi- cide use, for example, was obtained from various sources, coded on the data sheets, and keypunched into cards for use in generating those data elements in the county record. The second data source is the Conservation Needs Inventory tapes. These tapes were carefully reviewed to identify their unique data contents, and selected data elements will be extracted from them to provide county * We felt that for overall planning purposes on a large segment of the country such as the Missouri River Basin, the accuracy of this apportion- ment technique may be sufficient. As future work on correlations proceeds, this assumption should be critically evaluated. In localized areas it can have substantial impact and should be corrected before decisions are made on that local area. Adequacy of the apportionment technique and correction can be assessed and made by consulting individuals in each county who have the best knowledge of their county in this regard; e.g., the county agent or county assessor. 25 ------- record information. Examples of these data are soil classes, land re- source area and region, soil names, watershed, and slope and erosion classes. The third data source is the Census of Agriculture tapes. These files provided data relating to land use such as crops grown and livestock. The last data source is the NOAA tapes, providing precipitatiQn data. STATION MASTER FILE : The second file to be developed for this project is the STATION MASTER FILE. This file, consisting of 1,196 characters per station record, contains information unique to an individual station and the area which impacts that station. There are three data sources for this file. The first, manual input, consists of data elements relating to station identification and loca- tion, area, channel slope, etc. Data sheets were designed, data ex- tracted from various sources, keypunched, and a card file containing these intermediate data developed. The second data source is the STORET system. This source is used to provide water quality data, hydrologic data, and statistics relative to these data, for each of the stations which have been selected. The third data source is the COUNTY MASTER FILE described previously. The STATION MASTER FILE will contain data for each of the COUNTY MASTER FILE records which impact the station area, and in proportion to the percentage of the county area within the watershed. Both of these master files are developed by means of COBOL routines, due to the data manipulation and sorting required in file construction. However, the data element values are expressed in formats which will permit their use in FORTRAN routines. This capability will enable a much broader use of these files for future correlation and other statisti- cal activity. The complete software developed in this program to generate the two master files is discussed in the next section. Computer Software The computer programs required for this study consist largely of pro- grants designed to create a unique data bank from various data sources. For the preparation of reports from the created data bank, only two 26 ------- programs are used: (1) NPSPSTMD, which writes the station master re- port, and (2) NPSPCTYD, which writes the county master report. The programs used with appropriate data sources are as follows: Manual Input: NPSPaIF1 NPSPCAL1 NP SPGSM1 NP SPG M1 NPSPFPC1 Census of Agriculture: NPSP OA1 Conservation Needs Inventory: NPSP NI2 NOAA: NPSPNOA1 STORF : NPSPSTR1 Utility Programs: NPSPCOA3 NPSPCNI4 NPSPGAL4 NP SPGAL6 NPSPC&LI NP SPGSM3 NPSPCTS2 NPSPCrS3 NP SPNOA3 NPSPFPC3 NPSPSTR3 NPSPCOA4 Sort Programs: NPSPCOA2 NP SPCNI1 NPSPCNI3 NP SPNOA2 NPSPFPC2 NP SPGAL2 NP SPGAL3 NPSPGAL5 NPSPGAL7 NP SPGSM2 NPSPSTR2 NPSPCTS1 27 ------- An abstract of each program is presented in the following sections. NPSPSTMD : This program reads the STATION MASTER FILE and creates a report for each MRI station in the Missouri River Basin. The report reflects the pertinent data within the following major categories: I. Location 2. Land characteristics 3. Land use (acres) 4. Water quality data (averages) 5. Crop data 6. Fertilizer and pesticide data (tons) 7. Livestock and poultry 8. Contributing counties (up to 100) The data furnished within each of the above categories are as follows: 1. Location a. Stream name b. Location c. County d. State e. Latitude f. Longitude g. Downstream station h. Distance to downstream station i. MRI station number j. STORET station and agency number k. USAS station and agency number 1. 4DC WQ station number m. OWDC SW station number ii. OWDC sub-subbasin number o. Total watershed area 28 ------- 2. Land characteristics a. Main channel slope b. Slope percent class c. Soil erosion class d. Soil infilatration e. Soil index f. Rainfall intensity g. Total precipitation in inches for each season and the year h. Soil capability classes for the eight types 3. Land use (square miles) a. Land area b. Total cropland c. Pasture/grazing d. Woodlands e. Irrigated 4. Water quality data (averages) for each season and the year a. Temperature (°C) b. Dissolved oxygen (mg/liter) c. Biochemical oxygen demand d. Nitrogen e. Dissolved solids f. Nitrate g. Phosphate h. Suspended solids i Sulfate j. Chloride k. Herbicides 1. Insecticides m. Fungicides n. Streamf low o. Total coliform p. Fecal coliforni q. Dissolved oxygen (percent saturation) r. Temperature (°F) a. Turbidity (Jackson units) t. Turbidity (ppm as silicon dioxide) u. Phosphoru8, wet method (mg/Liter as P) (for details, see Table A-i in Appendix A). 29 ------- 5. Crop data a. Corn b. Sorghums c, Wheat d. Other grains e. Soybeans f. Hay g. Cotton h. Peanuts i. Tobacco j. Potatoes k. Vegetables 1. Berries m. Orchards n. Other crops o. Greenhouses 6. Chemical fertilizer data (tons) - by half year and pesticide data (tons) - by year a. Total nitrogen b. Total P 2 0 5 c. Total 1(20 d. Lime e. Herbicides f. Insecticides g. Fungicides 7. Livestock and poultry a. Cattle and calves - total - feedlots - stock in lots b. Hogs - total - hog lots - hogs in lots c. Chickens - total - chicken houses - chickens in houses d. Sheep e. Horses and ponies 8. Contributing counties a. Each county that shares in the watershed of this station is listed, showing the county area, and percent of the county area in the watershed, and the distance to the station. 30 ------- NPSPCTYD : This program reads the COUNTY MASTER FILE and creates a re- port for each county in each state within the Missouri River Basin. Th report reflects the pertinent data within the following major categories: 1. Location 2. Land characteristics 3. Land use 4. Crop data 5. Fertilizer data and pesticide data 6. Livestock and poultry The data furnished within each of the above categories are as follow: 1. Location a. County b. State c. Watershed d. Land resource area e. Land resource region 2. Land characteristics a. Slope percent class b. Soil erosion class c. Rainfall intensity d. Total precipitation (all seasons and the year) e. Soil name f. Soil capability classes 3. Land use a. Land area b. Total cropland c. Pasture and grazing d. Woodlands e. Irrigated 31 ------- 4. Crop data a. Corn b. Sorghums c. Wheat d. Other grain e. Soybeans f. Hay g. Cotton h. Peanuts i. Tobacco J. Potatoes k. Vegetables 1. Berries m. Orchards n. Other crops o. Greenhouses 5. Fertilizer data by half year and pesticide data by year a. Total nitrogen b. Total P 2 0 5 c. Total K 2 0 d. Lime e. Herbicides f. Insecticides g. Fungicides 6. Livestock and poultry a. Cattle and calves - total - feedlots - stock in lots b. Hogs - total - hog lots - hogs in lots c. Chickens - total - chicken houses - chickens in houses d. Sheep e. Horses and ponies NPSPQff 1 : This program will read the various cards created manually and write them onto a magnetic tape. This provides data to the STATION MASTER FILE and the COUNTY MASTER FILE that are not available from other sources. The purpose is to provide all card input for the system from a central file in an easily accessible form, There are 10 different input types defined as follows: 32 ------- Type Number Description 1. State name and state number 2. County data a. State and county codes b. Maximum 30 mm rainfalls c. Soil type d. County area e. County name 3. Station location and identification a. MRI station number b. State and county code c. Latitude of station d. Longitude of station e. Stream name f. Location 4. Station cross-reference list a. MRI station number b, STORE station number c. STORET agency number d. OWDC water quality station num- ber e. OWDC surface water station number f. USGS station number g. USGS agency number 5. Zone definition a. MRI station number b. County - (up to 100 entries) 1. State and county code 2. County area 3. County - distance to station 33 ------- Type Number Description 6. Hydrological sequence a. MRI station number b. Downstream MRI station number c. Mileage to downstream station 7. Watershed slope and soil characteris- tics a. MRI station number b. Main channel slope c. Soil infiltration rate d. Soil index e. Map number and location 8. Applied fertilizer by county by half year a. State and county code b. Half year code c Total nitrogen d. Total P 2 0 5 e. Total K 2 0 9. Pesticide data a. State and county code b, Insecticide c. Herbicides d. Fungicides 10. NOAA station - state county cross- ref erence a. State and county code b. NOAA stations (up to 30) NPSPGAL1 : This program reads the tape created in NPSP F1 and extracts the data Types 2 and 5 onto intermediate data files for sorting. The sorted files will be used by NPSPGAL4 for county allocation data. NPSPGSM2 will sort Type 5 records and NPSPGAL3 will sort Type 2 records. 34 ------- NPSPGSM1 : This program reads the tape created in NPSPQIP1 and ex- tracts the data Types 3, 4, 5, 6, and 7 onto intermediate data files for sorting. The sorted files are used by NPSPGSM3 in the creation of the STATION MASTER FILE. NPSPGAL2 sorts the selected records into station sequence. NPSPGcM1 : This program reads the tape created in NPSPG F1 and selects data Types 1 and 2 for the creation of the COUNTY MASTER FILE. NPSPFPC1 : This program reads the tape created in NPSPGMF1 and extracts the data Type 8 onto an intermediate data file for sorting. The sorted file is based in NPSPFPC3 to add the fertilizer data into the COUNTY MASTER FILE. NPSPFPC2 sorts the selected tecords into state and county sequence. NPSPCOA1 : This program reads the Census of Agriculture tape (1969) and selects the following data which will be sorted by NPSPCOA2 for inclusion onto the COUNTY MASTER FILE in NPSPCOA3: 1. State 2. County 3. Data year 4. Land area 5. Total crop area 6. Pasture grazing 7. Woodlands 8. Irrigated 9. Total cattle (including dairy cattle) 10. Total hogs 11. Corn 12. Sorghum 13. Ray 14. Cotton 15. Peanuts 16. Tobacco 17. Potatoes 18. Sheep 19. Horses 20. Total chickens 21. Chicken houses 22. Chickens in houses 23. Wheat 35 ------- 24. Other grain 25. Soybeans 26. Greenhouses 27. Vegetables 28. Berries 29. Orchards 30. Other crops 31. Cattle feedlots 32. Cattle in feedlots 33. Hog lots 34. Hogs in lots NPSPCNI2 : This program reads the Conservation Needs Inventory file sorted by NPSPCNI2 and selects the following data which will be sorted in NPSPCNI3 for inclusion with the COUNTY MASTER FILE in NPSPCNS4: 1. Land resource area 2. Land resource region 3. Soil name 4. Watershed 5. Soil classes 6. Slope percent class 7. Soil erosion class NPSPNOA1 : This program reads the NOAA. tape and selects the following data which will be sorted by NPSPNOA2 and added to the COUNTY MASTER in NPSPNOA3: Precipitation data for each season and the total for the years 1968, 1969, and 1970. NPSPSTR1 : This program will read a print image tape created by STORET and reformats the data onto an intermediate data file for sorting by NPSPSTR2. The sorted file will be read by NPSP1 R3 for updating the STATION MASTER FILE. The following data and others will be selected from the STORET print image tape: 36 ------- 1. Temperature °C and °F 2. Dissolved oxygen (mg/liter) and (percent saturation) 3. Biochemical oxygen demand (5 days, mg/liter) 4. Total dissolved solids 5. Total suspended solids 6. Turbidity (Jackson units) and (ppm as silicon dioxide) 7. Total nitrogen 8. Nitrate 9. Total phosphate 10. Total phosphorus 11. Chloride 12. Total coliform 13. Fecal coliforin 14. Insecticides 15. Herbicides 16. Fungicides 17. Streamf low (for details see Table A-i in Appendix A) NPSPCOA3 : This program reads the file created by NPSPCOA1, sorted by NPSPCOA2, and updates the COUNTY MASTER FILE. The fields specified under NPSPCOA1 are the only fields affected. For consistency of units and be- cause the large areas involved lead to extremely large numbers if the areas are given in acres, the data reported on the Census of Agriculture file in acres were converted to square miles in NPSPCOAI. 37 ------- NPSPCNI4 : This program reads the files created in NPSPCNI2, sorted by NPSPcNI3, and updates the COUNTY MASTER FILE with the apposite data. The data fields affected are defined in NPSPcNI2. An error report will be printed to reflect c NI data for counties which do not exist on the COUNTY MASTER FILE. NPSPGAL4 : This program reads the files created by NPSPCAL1, sorted by NPSPGAL2, NPSPGAL3 and allocates county area, county area for the station and percent of county area for the station and writes the allocation data onto a magnetic tape which is sorted by NPSPGAL5 and used by NPSPGAL6. A report will be written reflecting the data generated with an “*“ flagging any fields in error. NPSPGAL6 : This program reads the zone master created in NPSPGAL4 sorted into station sequence by NPSPGAL5 and accumulates the zone areas in each record. The sum of the zone areas by station will be the station area which will be written into each record. The output file will be a disk file to be sorted by NPSPGAL7 into county, state sequence. NPSPGAL1 : This program reads the allocation file created by NPSPGAL6, sorted by NPSPGAL7, and the COUNTY MASTER FILE. The allocation data for each county are used in generating the zone master file. An error report is written reflecting: 1. No allocations for county records and/or 2. No counties for allocation records. NPSPGSM3 : This program reads the file created in NPSP F1 and the sorted file created by, NPSPGSM2 and generates the STATION MASTER FILE. An error report is written for each station which does not have the necessary data. NPSPCJ S2 : This program reads the zone master file created by NPSPCAL1, sorted by NPSPCTS1, and accumulates the zone records by station and writes the apposite county data to an intermediate data file used in NPSPCTS3. NPSP TS3 : This program reads the intermediate file created in NPSPCTS2 and updates the STATION MASTER FILE created in NPSPGSM3. An error report is written, reflecting: (a) data for which a station master record does not exist; and (b) station master records without county data. NPSPNOA3 : This program reads the intermediate file created by NOSPNOA1, sorted by NPSPNOA2, and updates the COUNTY MASTER FILE. An error re- port is written to show records selected for which a county master record does not exist. 38 ------- NPSPFPC3 : This program reads the intermediate file created in NPSPFPC1, sorted by NPSPFPC2, and updates the COUNTY MASTER FILE. An error report is written reflecting the data selected for which a county master record does not exist. NPSPSTR3 : This program reads the intermediate file created by NPSPSTR1, sorted by NPSPSTR2 and updates the STATION MASTER FILE. An error report is written for the data records for which no station master record exists. NPSPCOA4 : This program reads the Census of Agriculture tape and creates a report showing the amount of fertilizer (in tons) used by county in Minnesota and Montana (while fertilizer use data for counties in other states were obtained from other data sources, see Appendix A). This will be used to manually input these data with the fertilizer data. Methods for Updating the Data System To insure the utility of the data system which has been developed during this program, it has been designed to facilitate the updating of the many parameters in the system. A description of the step-by-step procedure to be followed in updating the system is given below. The detailed operating procedures for this updating will accompany the computer cards and tapes when they are submitted to EPA. The 4ata necessary to complete the COUNTY MASTER FILE come from four unique sources. The data necessary to complete the STATION MASTER FILE come from one unique source in addition to the complete COUNTY MASTER. Creation of the COUNTY MASTER FILE: Manual data : The initial phase of creating the COUNTY MASTER FILE is done by one program which reads manually prepared data writing onto a magnetic tape which is the original County Master. The information loaded during this step is fixed and normally will never change. Conservation Needs Inventory : The data rea4 from the Conservation Needs Inventory files normally will remain static and therefore they are not kept by year. The data from CNI are merged with the COUNTY MASTER. Census of Agriculture : The Census of Agriculture’ files provide data to the COUNTY MASTER for the year 1969. Space is available so that when data become available up to five census from the Census of Agriculture data may be saved. The data read from COA files aremerged into the COUNTY MASTER for the appropriate year. 39 ------- NOAA : The NOAA provides data to the COUNTY MASTER for the years 1968, 1969, and 1970. Space is available for two more years of the NOAA data. The data read from the NOAA file are merged into the COUNTY MASTER for the appropriate year. Updating : Steps for creation of COUNTY MASTER FILE may be run any time new data become available and the program will update the most recent COUNTY MASTER FILE. Creation of the STATION MASTER FILE: Manual data : The original STATION MASTER is created from manually pre- pared data most of which are constant and will be permanent. STORET : These data are in the same form as a report using STOR.ET except that they are available on magnetic tape. The tape is converted back into valid data which are added to the STATION MASTER FILE for the cor- rect year. The present file has data for 1968, 1969, and 1970 by season and year. COUNTY MASTER : The data available on the COUNTY MASTER FILE are spread to each watershed region based on the proportion of the county allocated to the region. With the exception of rainfall data, slope percent class and soil erosion class, all data are spread to the watershed based on a county-to-zone area ratio. Updating : If data in the COUNTY MASTER or STORET have been updated, it must be assured that a proper dispersion of the data to each watershed is maintained. Each change in data for the COUNTY MASTER will necessitate the updating of the STATION MASTER. Identification of Data by Source Source Field Name Description Manual Data MEl Station Code’ Card Type 3 OWDC Map and Basin card Type 7 State and County Card Type 3 State Name Card Type 1 County Name Card Type 2 Latitude and Longitude Card Type 3 Stream Name Card Type 3 Location Card Type 3 STORET Station and Agency Codes Card Type 4 JDC Water QuaLity Station Number Card Type 4 OWDC Surface Water Station Number Card Type 4 USGS Station Code Card Type 4 40 ------- Source Field Name Description Census of Agriculture (1969) Downstream Station Distance to Downstream Station Main Channel Slope Soil Infiltration Rate Soil Index County Code-Each Couri in Watershed County Total Area-Each County in Watershed County Distance to Station-Each County in Watershed Rainfall Intensity Land Area Total Farmland Total Crop Area Total Other Land Pasture Grazing Harvested Cropland Wood lands Other Crop land Irrigated Other Farmland Corn Sorghum Wheat Other Grain Soybeans Hay Cotton Peanuts Tobacco Potatoes Vegetables Berries Orchards Other Crops Card Type 6 Card Type 6 Card Type 7 Card Type 7 Card Type 7 Card Type 5 Card Type 5 Card Type 5 Card Type 2 41 ------- Source Field Name Description Greenhouses Total Cattle Cattle Feedlots Cattle in Feedlots Total Hogs Hog Lots Hogs in Lots Sheep Horses Total Chickens Chicken Houses Chickens in Houses Lime Conservation Needs Inventory (1969) Soil Name Slope Percent Class Erosion Class Soil Class Area by Class and Subclass Watershed Resource Area Resource Region STORET Parameters Listed in Table A-l of Appendix A Manual Data Nitrogen P205 1 (20 Herbicides Insecticides Fungicides NOAA (1968, 1969, Rainfall Amount for quar- and 1970) ters and year 42 ------- CONCLUSIONS The objectives of Phase I of this study (that portion of the overall program covered by this report) were to collect, evaluate, and compile the physical and economic base data for the analysis of nonurban, non- point, source pollutants in the Missouri River Basin. The results of our study lead to the following major conclusions: (1) we have developed a unique and extremely useful data allocation methodology that is par- ticularly useful for nonurban situations in all parts of the country. We have also catalogued the types and sources of relevant data as well as èompiling the data in a form which will be amenable to analysis of all types; (2) the amount of data available for the Missouri River Basin on physical and economic parameters that we investigated are sufficiently large that it should be possible to develop systems models relating non- urban, nonpoint source pollutants to water quality parameters; however, additional evaluation of the collected data should be conducted. In addition to these major conclusions from the study, there are several other conclusions that can be drawn: (1) the computerized data-storage system developed during this program logically relates county segments to watersheds and should be useful to other government ageiicies such as USDA and USD1. (2) It is possible to correlate average water quality parameters with land use and other nonwater quality parameters. (This was demonstrated by several two-parameter correlations which were de- veloped in the early stages of the program.) (3) Streamf low equations for all the states in the basin developed by the USGS as a result of multiregression analysis can serve as the basis for the development of basin runoff models. Furthermore, the existence of these equations and of the two-parameter correlations developed in this program, raise the probability that the available data can be used to build useful water quality models for the Missouri River Basin. (4) Relationships between nonwater quality parameters can be developed with the data compiled in this program to make economic projections. For example, fertilizer and pesticide use can be related to land use, agricultural practices to soil type, rainfall amount, and ground slope, etc. (5) For the purpose of obtaining more useful information for improving water quality manage- ment planning in the basin, further development of the water quality monitoring network--in terms of station distribution, and types and frequency of measurements at the stations--is needed. The data collected during the present program definitely reflect this need. 43 ------- No Page 44 ------- RECO1 ,1ENDATIONS On the basis of the conclusions presented in the previous section, several recommendations can be developed. The major recommendation, based on the two major conclusions, is that Phases II and III of this program should be initiated to carry out an in-depth evaluation of both the quan- tity and quality of data available in the existing data bank. The fol- lowing analyses are recommended: 1. Assessment of the quality of land use and soil data, e.g., by com- paring data from independent sources, and by consulting with knowledge- able individuals (e.g., county agents); 2. Assessment of the quality of hydrological and water quality data, e.g., by statistical comparison among related parameters, and by corn- parison of existing STORET data with other data which were not available in STORET (e.g., from water and wastewater treatment plants); 3. Identification of interrelationships among different types of vari- ables, e.g., correlation of water quality data with land use data; and 4. Assessment of significance of missing data and use appropriate methods for obtaining or estimating such. If the results of these analyses show that the amount and quality of both physical and economic data are sufficient, analytical tools should be developed which will allow EPA to make economic and planning deci- sions concerning nonurban, nonpoint pollutant sources. In addition to the major recommendation, other recommendations that can be made based on the previous conclusions are: (1) the present data file should be updated whenever new data become available. Updating of the data will provide a base for time series analysis of nonpoint source pollution, as well as allow EPA to update their economic and planning decisions concerning nonurban, nonpoint pollutant sources. (2) The water quality monitoring network in the basin should be improved- - for example, the location of stations should be changed so that they are more uniformly distributed in the basin and the types of water quality parameter measured at each station should be reevaluated so that all important data such as pesticide concentrations are measured. This will require a joint effort on national, regional and local pollution control agencies, but this effort should lead to the availability of better in- formation for basin-wide water quality management planning. 45 ------- No Page 46 ------- APPENDIX A DATA SOURCES INVESTIGATED 47 ------- This Appendix presents a discussion of the major data sources that were investigated during the course of this program. The data sources that were actually used in compiling our data bank are presented in “Iden- tification of Data and Collection of Data” of this report. Tables A-2 through A-il list all organizations that were contacted to obtain information. Personal contacts that were made are presented in Appendix B. Water Quality Data We identified numerous sources of water qualtty data for the Missouri River Basin. Among these were the Environmental Protection Agency, the U.S. Geological Survey, the Army Corps of Engineers, the Bureau of Recla- mation, State Water Pollution Control Agencies, Water-Treatment and Sewage- Treatment plants, etc. Most of the information collected by the treat- ment plants are stored in state files or by the treatment plants them- selves, and not in the computer-processibie form. Furthermore, these data are generally not published and must be copied manually from their files. Because we found applicable information from other sources, we did not obtain data from these plants. The EPA’s STORET system collects data from many agencies. It is the most comprehensive source of water quality data and, furthermore, it is in computer-processible form which permits easy access. We, therefore, elected to use it as the primary source of water quality data for this program. The STORET system has the data for approximately 1,800 stations in the Missouri River Basin and we originally selected, based on the type, frequency, and duration of their measurements, a total of 520 stations. After locating the watershed for these stations from the maps prepared by the OWDC, it was found that some stations are located in close proximity to one another. Also, a number of the stations either do not have sur- face water stations nearby or do not collect streamflow data themselves. By picking one station when several are located together, and eliminating those stations that do not have flow information (because the stream- flow data are essential in our future modeling effort), we reduced the number of the selected stations to 233. Locations of these stations are presented in Appendix C. In this program, the water quality data retrieved from the STORET for these 233 water quality stations are for those parameters which are most strongly influenced by the nonpoint sources. These parameters 48 ------- include sediment, nutrients, pesticide level, organic concentration and bacterial density. Table A-i presents the specifics of parameters retrieved from the STORET system, and their abbreviations appeared in the data report.* We found that most water quality statj.ons measure different sets of water quality parameters. The set of parameters pre- sented in Table A-i are not necessarily collected by all the stations we selected. We, therefore, elected to have printed, those parameters which are available from the ST0R for each station in our data re- port. Furthermore, we used the frequency of sampling for the majority of stations, and also the needs of our future modeling efforts as a basis for choosing only the seasonal and yearly averages for the years of 1968, 1969, and 1970. Periods of seasons and year are defined as follows: First season: December (previous year), January, February Second season: March, April, Nay Third season: June, July, August Fourth season: September, October, November Year: December (previous year) to November * STATION MASTER FILE. 49 ------- TABLE A-i SELECTED WATER QUALITY PARAMETERS Code Parameter Description Parameter Abbrev .ation 00010 TEMP CENT 00011 TEMP FAHN 00060 FLOW CFS 00070 JURB, J.U. 00075 TURB PPMSIO2 00095 CNDUTVY MO 00300 DO /L 00301 DO SAT PCT 00310 BOD5 MG/L O03 5 COD r /L 00400 PH SU 00500 T RSD MC/L 00505 TV RSD MG/L 00510 TFX RSD li/L 00515 TF RSD MC/L 00520 SIP RSD MC/L bo525 FF RSD MG/L 00530 TNF RSD MG/L 00535 VNF RSD MC/L 00540 FNF RSD MG/L 00545 S RSD ML/L 00600 T N MG/L 00605 OG N MG/L 00610 AM N MC/L 00615 NO2 MG/L N 00620 N03 MG/L N 00630 NO2&3 /L N 00635 AM&OG N MG/L 00650 T P04 /L 00655 FL P04 MC/L 100660 OT P04 MC/L 00665 T P MC/L 00666 D P MG/L 00667 I P MG/L 00670 T OG P MC/L 00930 D NA MG/L 00931 NA ADS RATIO 00935 D K MG/L 00936 SUS K MG/L Water Temperature (degree Centigrade) Water Temperature (degree Fahrenheit) Stream Flow (cubic feet per second) Turbidity, Jackson Candle (Jackson Unit) Turbidity, Ilellige (ppm as silicon dioxide) Conductivity (micromhos at 25°C) Dissolved Oxygen (mg/i) Dissolved Oxygen (percent of saturation) Biochemical Oxygen Demand (mg/i, 5-day-20?C) Chemical Oxygen Demand, 0.025N K 2 CrO 7 (mg/i) pH (standard unit) Total Residue (mg/i) Total Volatile Residue (mg/i) Total Fixed Residue (mg/i) Total Filtrable Residue (mg/i) Volatile Filtrabie Residue (mg/i) Fixed Filtrabie Residue (mg/i) Total Nonfiltrabie Residue (mg/i) Volatile Nonfiltrable Residue (mg/i) Fixed Nonfiltrabie Residue (mg/I) Settlable Residue (mi/I) Total Nitrogen (mg/i as N) Organic Nitrogen (mg/i as N) Ammonia Nitrogen (mg/i as N) Nitrite (mg/i as N) Nitrate (mg/I as N) Nitrite Plus Nitrate, One Determ. (mg/i as N) Ammonia & Organic Nitrogen, One Determ. (mg/i as N) Total Phosphate (mg/i as P0 4 ) Poly Phosphate (mg/i as P0 4 ) Ortiho Phosphate (mg/i as P0 4 ) Total Phosphorus, Wet Method (mg/i as P) Diss. Phosphorus, Wet Method (mg/i as P) Insoluble Phosphorus (mg/l as P) Total Organic Phosphorus (mg/i as P) Dissolved Sodium (mg/i as N 8 ) Sodium Adsorption Ratio Dissolved Potassium (mg/i as K) Suspended Potassium (mg/i as K) 50 ------- TABLE A-i (Concluded) Code Parameter Description Parameter Abbreviation 00937 T K MG/L 00940 CL MG/L 31501 T CLF1/100 ML 31503 T CLF2/l00 ML 31504 T CLF3/100 ML 31615 F CLF1/100 ML 31616 F CLF2/i00 ML 3 16 73 F STC1/l00 ML 31679 F STC2/l00 ML 38260 MBAS t’ /L 70299 SS MG/L 70300 TF RSD MG/L 70302 DS TONS/DAY 70303 DS TONS/A-FT 70324 SUS SED MG/L 71845 AM MC/L Nl- 14 71850 N03 /L 71855 NO2 MC/L 71886 TP MG/L P04 71887 TN MG/L N03 71888 TSP MG/L P04 71889 so P04 MC/L Total Potassium (mg/i as K) Chloride (mg/i as Ci) Tot3L Coliform (membrane filter, imined., M-Endo Med, 35°C, /100 ml) Total Coliform (membrane filter, delayed, M-Endo Med, 35°C, /100 ml) Total Coliform (membrane filter, immed., Lcs Endo Agar, 35°C, /100 ml) Fecal Coliform (MPN, EC Med., 44.5°C, tube. 31614, /100 ml) Fecai Coliform (membrane filter, M-FC Broth, 44.5°C, /100 ml) Fecal Streptoccoci (membrane filter, KF Agar, 35°C, 48 hr, /100 ml) Fecal Streptoccoci (MF M-Enderoccocus Agar, 35 C, 48 hr, /100 ml) Methylene Blue Active Substance Suspended Solids (Residue on Evap. at 180 C, mg/I) ‘Total Filtrable Residue (dried at 180 C, mg/l) Dissolved Solids - Tons per Day Dissolved Solids - Tons per Ac-Ft Suspended Sediment (mg/l) Ammonia Nitrogen (mg/i as N H 4 ) Nitrate (mg/i as N03) Nitrite (mg/l as NO 2 ) Total Phosphorus (mg/I as P0 4 ) Total Nitrogen (mg/i as N03) Total Soluble Phosphorus (mg/i as P04) Soluble Orthophosphate (mg/i as P0 4 ) 51 ------- The concentration of insecticides, as denoted by INSECTICIDES in the data report, was taken as the average concentration in whole water sani- pie (jig/liter) of the following parameters: Code - - - Parameter 39330 A ldrin 39340 BHC 39350 Chiorodane 39360 DDD 39365 DDE 39370 DDT 39380 Dieldrin 39388 Endosul fan 39390 Endrin 39398 Ethion 39400 Toxphene 39410 Heptachior 39420 Heptachior Epoxide 39430 Isodrin 39440 NUX 39450 NHP 39460 Ch lorobenzilate 39470 Dilan 39480 Methoxychior 39530 Malathion 39540 Parathion 39550 Chiorothion 39560 Demeton 39570 Diazinon 39580 Guthion 39590 Hept 39600 Methyl Parathion 39610 Phosdrin 39620 Tepp 39750 Sevin 39780 Dicofol 39782 Lindane 39786 Trithion 39790 Methyl Trithion 39800 Imidan 39900 Al lethriri 39910 Cinerin 39930 Pyrethrins 52 ------- The concentration of herbicides, as denoted by HERBICIDES in the data report, was the average concentration of the following parameters in the whole water saniple, with unit pg/i: Code Parameter 39730 2,4-D 39740 2,4,5-T 39760 Silvex 39770 Dacthal (DCPA) 39920 DNOC Hydrological Data The principal agencies operating hydrologic stations in the basin are the USGS and the Corps of Engineers. The USGS is the more complete source of hydrologic information. It publishes hydrologic data each year for each state in the basin. Besides being published in tabular form, these data are available in computer-processible form. The USGS operates more than 2,900 surface water stations in the basin with at least 40 stations in every basin state; the single exception is Minnesota. Of these 2,900 stations, over 1,300 report daily discharge and other data less frequently. These data are, for example, stage, peak stage, low flow, cross section, flow duration, flood frequency, coeffieient of roughness, time of travel and surface inflow-outflow. The USGS office in each basin state has developed a streamfiow model for that state. These models are based on a regression analysis of all pertinent data, and relate such parameters as rainfall, soil class, drainage area, etc., to the s treamf low rate. The number, frequency and location of hydrologic measurenents have been sufficient to generate multiple-regression correlations that can be used to predict streamflow, The results of these analyses will be extrenely useful to this program. Further details of these are presented in Appendix D. The Corps of Engineers takes ‘hydrologic data for use in its reservoir and channel straightening work. Most of the information obtained is put into the USGS computer system. The Corps also investigates flood plain for specific watersheds. The results of these investigations are published in reports. The less important source of hydrologic information for the Missouri River Basin is the River Forecasting Center of National Oceanic and Atmospheric Administration (NOAA) in Kansas City. It has developed long-term hydrographs for 800 subbasins which encompass the entire 53 ------- Missouri Basin plus an additional quarter milliop square miles. These subbasins average about 1,000 square miles, but may be as small as 200 to 400 square miles. With these hydrographs and computer models for runpff, NOAA can successfully predict river stages along the Missouri River. The major concern of this program is the analysis of pollutants from non- point sources. The pertinent hydrologi c data are obviously the stream- flow rate. Among 233 selected water quality stations, 183 stations col- lect streamfiow data. For 50 other stations, we have identified the nearest gauge stations which have streaniflow information to supplement our need. We were able to retrieve these data for 24 of these 50 sta- tions from EPA’s STORET system. Data for the re aining 26 gauge sta- tions can be obtained from their respective agencies. In our data report, the streamf low daia are presented in terms of their seasonal and yearly averages for 1968, .969, and 1970. Climatological Data Climatological factors of most importance to our study are rainfall intensity and amount.* Because of the frequez cy with which these data are taken, much data are available. The principal sources of these data are the U.S. Department of Commerce, National Oceanic and Atmospheric Administrations, Environmental Data Service, Asheville, North Carolina. Climatological information, such as temperature, precipitation, wind, humidity, etc., for various locales in the country are stored by the NOAA in computer-processible form. From this storage, in addition to the raw data, information resulting from variots types of statistical manipulation can also be retrieved, e.g., the total precipitation for a certain geographical area in a defined period of time, or probability that a given rainfall will occur at a certain location for a certain number of times per year, etc. In the data report of this program, the precipitation data are presented on the seasonal and yearly basis. These data were originallyprocessed by the NOAA. from its tapes, and were available from each weather st i •. in the basin. NRI carried out further statistical manipula i n on these data to obtain county-precipitation data, which were subsequently pre- sented in the Data Report. * Wischmeier, W. IL, and D. D. Smith, “Ratnfall Energy and Its Rela- tionship to Soil Loss,” Transaction 1 Amer. Geoph. Union , 39 (2), 851 (1958). 54 ------- For the information about the rainfall intensity, we elected to use statistical values of maximum 30-mm rainfall that will occur once per year. Intensity data for each county in the basin were also obtained from the NOAA.* Soil-classification data The types of soil directly influence the quality and quantity of pol- lutant in the surface runoff and the agricultural practices on the lands. Furthermore, the agricultural practices greatly affect the water quality of the streams. Soil-classification data, therefore, are extremely im- portant to the development of models re3ating water quality to land use. There are several ways in which soil can be classified. One method is to classify soil by the crops or plants that it will support. There are eight such classifications. Class 1, few limitations that restrict its use; Class 2, some limitations that reduce the choice of crops or require moderate conservation practices; Class 3, severe limitations that reduce the choice of crops or require special conservation practices or both; Class 4, severe limitations that restrict choice of crops and require cAreful management; Class 5, little or no erosion hazard but limitations that are impracti- cal to remove--that limit use largely to pasture, range, woodland, or wildlife food and cover; Class 6, severe limitations that make it unsuited for cultivation and limit use to pasture, range, woodland, or wildlife; Class 7, limitations that make it unsuited for cultivation or restrict itsuse to grazing woodland or wildlife; and Class 8, limitations that preclude their use for commercial plant produc- tion or restrict their use to recreation, wildlife, water supply, and aesthetic purpose. * “Rainfall Frequency Atlas of the U.S.,tt U.S. Department of Commerce, Washington, D.C. (1961). • 55 ------- There are subclasses for each of these classes with the exception of Class 1: Subclass e, erosion--made up of soils where susceptibility to erosion is the dominant hazard and problem in its use; Subclass w, wetness--made up of soils where excess water is the dominant hazard to limitations in its use; Subicass s, soil--made up of soils with characteristics in the root zone area which are dominant limitations in its use; Subclass c, climate--made up of soils where temperature and lack of moisture are limitations in its use. Information on the preceding type of classification is available from the Conservation Needs Inventory (1967). This inventory classifies the soil on a county-by-county- basis for each state in he basin. These data are stored in computer accessible form and we have included them in the data report. The 1967 Conservation Needs Inventory has data of “Soil Erosion Class” for each county. The Inventory classifies the soils into: little ero- sion; moderate erosion; severe erosion and gullies; and denoted them with 1, 2, 3, and 4, respectively. Whenever there is no information for a county, a number 0 is shown. We have these data compiled in the data report. The other method of classifying soil is based on the rate of infiltra- tion of water and takes into account water intake, surface texture, soil permeability, water-holding capacity, and tendency to seal under rain- drop action. The effects of land use, management, slope, vegetation cover, etc., are not considered. The result of this classification is the following six hydrologic soil groupings: Group 1 is barren rock, shale, and badlands--included are barren and seini-barren badlands, high Alpine mountain areas, and impermeable saline alkaline soil areas. The rate of infiltration is less than 0.05 in/hr. Group 2 is clay, and claypans, which are slowly permeable and have a slow intake rate of 0.05 to 0.2 in/hr. Group 3 is moderately fine textured, and has moderately slow permeability and intake of 0.2 to 0.6 in/hr. 56 ------- Group 4 is medium textured, moderately permeable, and has a moderate intake of 0.6 to 2 ] n/hr. Group 5 is moderately sandy, has moderately rapid permeability and an intake of 2 to 6.3 in/hr. Group 6 is sand and gravel, rapidly permeable, and has a very rapid intake--over 6.3 in/hr. These types of data are available from the U.S. Department of Agriculture, Soil and Water Conservation Research Division, The Forest Service and the Soil Conservation Service. They are also available from the U.S. Army Corps of Engineers and the U.S. Department of Interior, Bureau of Reclamation. Data from these sources have been summarized in the Missouri Basin Inter-Agency Committee report, and are presented in our data re- port. Another type of hydrologic soil grouping which has also been developed by SCS is the soil infiltration index. The computed data (in inches) were based on information on soil type, cover, and agricultural practices, and have been obtained for most parts of the basin. These values were used in system studies of streamf low characteristics of various drainage areas by the USGS. These data also appear in our Data Report. Land use data : Land use in the Missouri River Basin can be divided into the following: agriculture, recreation, urban, military, grassland, wildlife areas, forest areas, and water areas. The sources of land use data include the Bureau of Census, the various branches of the U.S. Department of Agri- oilture-- the Statistical Research Service, the Agricultural Stabilization and Conservation Service, the Forest Service and the Soil Conservation Service. Each state also has a epartment of Agriculture which collects land-use data. The Department of Interior has land use data in several branches, such as Bureau of Reclamation, etc. The major source of land use information for this program is the Census of Agriculture for 1969. This census includes detailed land use data by county for each state of the union. The 1969 Census for each state in the basin has become available recently on tape and includes 1964 statistics for comparison with 1.969 figures. For each county, data in- clude information about all farms, such as the number, the acreage in the farms, and the land use. The census includes the size of the farms, the farm operator tenure, the farm income and sales, farm production expenses, machinery and equipment, amounts of livestock and poultry and - 57 ------- crops harvested. It also contains some data on irrigation and artificial drainage as well as the agricultural chemicals and commercial fertilizer used. The crops are divided into corn, sorghums, hay, feed, field seeds, strawberries, anall grains, soybeans, peanuts, potatoes, tobacco, cotton, vegetables, tree fruit and grapes, nursery and greenhouse products, and forest products. All farms with sales over $2,500 I year were polled, and 507. of farms with sales less than $2,500/year were polled to obtain this information. Over a 907. return was received. The other important source of land use information is the Conservation Needs Inventory. Two Conservation Needs Inventories have been published, one for 1958 and the other for 1967. The 1958 inventory contains data on land use and conservation treatment needs by county for the entire United States. Statistics include cropping patterns with yield and pro- jected yield by resource area, soil resource group, and subbasin. The inventory information is correlated with the soil classification data in the Missouri Basin and the correlations are on tapes. The inventory includes all land use except built-up areas and land owned by the federal government. The 1967 inventory includes all acreage except urban and built-up acres, and all land owned by the federal government other than cropland operated under lease or permit. The inventory was developed from basic data re- garding present acreage in major uses and acreage of each land use clas- sified by physical problems affecting use. Estimates of needs for con- servation treatment for each major land use were based on the acreages and conditions of the land or the vegetation cover as of the crop year 1967, with due regard to locally applicable information and experience in solving conservation problems. The 1967 Conservation Needs Inventory is available on magnetic tape for all states in the basin. On a county basis, the data include land capability class and subclass, information on acreage of corn and sorghum, other row crops, close grown crops, summer fallow, total field crops, rotation hay and pasture, hay land, conservation use only, temporarily idle cropland, total tillage rotation, orchards, vineyards and bush fruit, open lands formally cropped and total cropland. Most of these data are based on a 27. sample. Still another source of information on crops and land use is the Agri- cultural Stabilization and Conservation Service of the USDA. They have a summary by county of all farms which participate in the ASCS program. This summary represents over 75% of all farms. Through the year 1970, the data cover wheat, cotton, and feed grains, but the 1971 report will 58 ------- be more extensive--going into more detail and including other grains. The 1971 data will include some information on nonparticipating farms. ASCS uses magnetic tapes for storing their data. Another data source is the detailed data sheets compiled by counties for the Land Resource Appendix of the Missouri Basin Comprehensive Frame- work Study. These working papers include land use data for public lands which are not available in the Conservation Needs Inventory. The papers are of value because they present a single source of data on use of these public lands. These data are located otherwise in several government agencies having legal jurisdiction over these lands, i.e., Bureau of Land Management, Forest Service, Bureau of Reclamation, Corps of Engineers, etc. We have these papers in our file. A final source of land use information is state cropland and livestock data. All states in the Missouri Basin provide an annual or biannual agricultural census and keep a record of major crop acreages and of the number of livestock on farms on a county basis. For most Missouri Basin states, these reports have been compiled for many years (10 to 40 years). While these data are not as detailed as the Conservation Needs Inventory or Census of Agriculture, they represent an annual data source. Because of their easy accessibility, and nature of the data, the Census of Agriculture (1969) was chosen as the primary source of land use data reported in this program. Data extracted from this document are listed below: County land area Total crop area Pasture grazing Woodlands Irrigated Corn Sorghum Wheat Other grain Soybeans Hay Cotton Peanuts Tobacco Potatoes Vegetables Berries Orchards Other crops Cr eenhous es 59 ------- From the data tapes of the Census of Agriculture, we also obtained data on fertilizer use and livestock. Topographic data : The topographic information needed for this study includes items such as tributary location, drainage area, river mileage, river channel slope, drainage area slope, etc. For drainage area and river mileage, we were able to obtain data from the following agencies: MBIAC : It has published a report entitled ItCondensed Tabulation of River Mileage and Drainage Areas,” in 1965, which lists for approximately 900 gauged tributaries: (1) gauge location, (2) mileage above the mouth, (3) noncontributing area, and (4) drainage area. This publication is a supplement to the 1949 edition of the Corps of Engineers’ “Missouri River Basin - River Mileages and Drainage Areas.” USGS : Gauge locations and drainage areas are always listed in its annually published “Water Resources Data.” The slope data are probably the most important topographic data for this program. We found that river basin slopes are available from USGS for a very small number of areas in the basin, and were restricted to small tributary areas only. The amount of data was so small that it did not warrant collection. The 1967 Conservation Needs Inventory has data of “Slope Percent Classtt for each county, which relate to our needs. We have these data compiled in our Data Report. Ideally, we need drainage basin slopes for all 233 watersheds selected in this program. However, basin slopes are not available in any publica- tion or from any agency, and would require a tremendous effort if esti- mated by ourselves. However, our literature survey indicated that main channel slopes may be used in place of basin slopes. Empirical evidence shows that steep ground slopes are expected to correspond with steep channel gradients; and shallow ground slopes with low stream channel gradients. This re- lationship has been developed by Horton,* who used the definition: Slope 1 atio = Channel Slope Ground Slope * Horton, R. E., “Erosional Development of Streams and Their Drainage Basins; Ilydrophysical Approach to Quantitative Morphology,” Geol. Soc. Amer. Bull. , 56, 275 (1945). 60 ------- Strahler* found that, in general, ground slope varies somewhat less than the first power of channel slope, and that the slope ratio tends to range from one-fifth or one-fourth for low values of slopes, up to about one-half for higher values. We have, therefore, decided to include main channel slope data in our data report. Some of these data are available from the USGS and the Corps of Engineers, and some of them have been estimated from the USGS’s topographical maps. Livestock Data Data on livestock are available semiannually from the State Agriculture Boards on a county basis. Similar data are also reported in the Census of Agriculture (1969), although less frequently (at 5-year intervals). Due to the computer accessibility, the latter was chosen as the primary source of livestock data in this report. Types of data reported are: Total cattle Cattle feed].ots Cattle in feedlots Total hogs Hog lots Hogs in lots Sheep Horses and ponies Total chickens Chicken lots Chickens in lots Sizes of commercial feedlots have been arbitrarily defined as: Cattle 500 + Hog 200+ Chicken 1,600 + Fertilizer Use Data The Census of Agriculture reports the total tonnages of fertilizer and lime on a county level. The lime data presented in our report were * Strahier, A. N., “Equilibrium Theory of Erosional Slopes Approached by Frequency Distribution Analysis,” Am. J. of Sci. , 248, 673 (1950). 61 ------- retrieved from this document. For informatioi about fertili er use, we need more specific information than what is available from th Census, We have beer able to obtain desirable data either directly frqm state agriculture agencies, or from the combination of several information sources. The fertilizer-use-data compiled in this program are given as to total nitrogen (N), phosphoric pentoxide (P 2 0 5 ), and potash (K 2 0) tonnages for the first and second half of 1969. For Colorado 1 Iowa, Kansas, Missouri , and Nebraska , whjch report their county iisage data semiannually, transformation of their data into the desirabl format was straightfor- ward. For Minnesota, Montana, Wyomi g , and North and South Dakota , which report data only on a statewide basis, two 4Ufe en’t methods we e adopted to calculate N, P, K data for each county. North and South Dakota : Fertili er usage in t rms oç N, P. iç or each county were calculated based on the acreage of iajor crops in the county and application rate of N, P, K to these crops. qounty crop çLata of 1969 were obtained from the reports of the State Department of 4gricul- ture, while the fertilizer application rates to these crops were sup- plied by persons who have the best know .e4ge ot their state i this regard. They are: Mr. E. H. Vasey Extension Soils Specialist Cooperative Extension Seri4ce Department of Agriculture North Dakota University Fargo, North Dakota arid Mr. Paul Carson Soil Testing Plant Science Department College of Agriculture and Biological Sciences South Dakota University Brookings, South Dakota Minnesota, Montana, and Wyoming : These three states h ve the tonnage data of N, P, K sold for the first and second half o ] 969 on a state ’- wide basis. To arrive at fertilizer usage jn each county, calculations were carried out as follows: I. County data from the 1969 Census of ‘Agr c ilture were used to deter- mine the percentage o the state’s total fertilizer which wap applte in each county. 62 ------- 2. This percentage was used in conjunction with the state report of fertilizer usage. The 1969 Census reported total tons of material in some cases and tons of plant nutrients (N, P, K) in others.* The method we adopted for these three states may be more accurate because we know the tons of plant nu- trient sold. Pesticide Data Pesticides are usually grouped into three major categories: herbicides, fungicides, and insecticides. Herbicides are used primarily for weed control on crop and pastureland and for brush control on range and pastureland. The Conservation and Land Use Division of ASCS reports the acreage of rangeland, cropland and pastureland treated for control of brush and weeds in each state. This report deals with cost-sharing programs, and is estimated to cover 90% of all herbicide use. During 1969-- the last year for which data are presently available--some 2.4 million acres were treated for weed and brush control. Of this total, about 157 .were in the 10 states included in the Missouri River Basin, with about 8.57. of the total U.S. Herbicide consumption actually taking place within the basin. Fungicides are used in substantial quantities for a variety of purposes, although farmers are depending less on chemicals and more on resistant varieties for control of plant pathogens. Some of the major uses of fungicides are for algae control (copper sulfate) and as wood preserva- tives (creosote and pentachlorophenol). The use of these chemicals is not controlled, and reports of their application are not required. Con- sequently, only the total quantity of various types of fungicides con- sumed in the U.S. is available. If we allocate usage according to the total land in farms, the Missouri River Basin is estimated to account for some 23% of the total domestic use of fungicides. Insecticides are the most controversial of the pesticides. As in the case of herbicides and fungicides, the total U.S. production and con- sumption are reported annually by ASCS, although the methods, extent and timing of use are not known for any specific area. About 26.57. of the total U.S. insecticide use is believed to occur in the Missouri River Basin. This estimate is based on the area in crops and the insect con- trol reconmiendations published by the various state agencies. * Personal comnuinlcation, Mr. Larry Bourret, Resource Management Special- ist, Wyoming Department of Agriculture, Cheyenne, Wyoming. 63 ------- No reliable data are available on a county basis regarding pesticide applications, other than those published in the Census of Agriculture. The Census reports expenditures of each farmer on a county basis for pesticides for various uses, and the number of acres on which the pesti- cides were used. However, these data do not constitute the information directly related to our needs. For the estimation of pesticide applicatiqns on a county level, two different methods were considered. 1. A mail survey of county extension agents to determine local pesti- cide application practices. 2. The following equation, developed from data on a national level and based on typical farm practices for different types of crops: P = 6.5 C + 2.0 S + 1.0 W + 4.0 B + 0.2 H + 8.0 M where P is the total pesticide application for a county, state or region, ecpressed in pounds; C represents the acres of corn harvested within that area; S , the acres of sorghum harvested; W , the acres of wheat harvested; B , the acres of soybeans harvested; H , the acres of hay, grass and pasturelands; and M , the total acres of all other farm crops harvested. This equation has been discussed in more detail in the Phase IA Final Report of this project. Though easy to handle, the pesticide equation described above does not tak? into account the heterogeneity of economical, physical, and land use characteristics of subdivisions in the basin. We, therefore, used a uailed survey as the primary source of pesticide application data on a county basis. The survey questioanaire for this purpose was prepared and sent to all county agents in the basin. The data surveyed include the quantity of herbicides and insecticides used on crops and on pasture, the most used pesticides in their county, the seasons those substances were applied, and the extra usage of particular insecticides during the past 10 years. Of the total 409 questionnaires mailed, 114 were returned with the re- quested data, representing 30% coverage of counties within the basin. Most indicated at least 307. accuracy in their estimations. 64 ------- These 114 counties (Figure A-i) which responded to our survey are spread randomly but uniformly over the entire basin and should, therefore, be representative of agricultural practices throughout the Missouri River Basin. For these 114 counties, the pesticide use data that appear in the data report were directly obtained from the survey. For those counties which did not answer the survey, usage data were estimated by using the insecticide and herbicides application rate per acre of crop .and. The pesticide application rates were calculated by averaging the application rates of the counties in the same land resources subregions,* which re- turned the survey. This figure was multiplied by the total cropland acreage to obtain the amount of pesticides applied. From the results of the county pesticide survey, we reached a conclusion that 857, of the herbicides and 99.67, of the insecticides were applied to the cropla.nd. We, therefore, chose to estimate pesticide use based on crop acreage alone. * U.S. Department of Agriculture, Soil Conservation Service, Agri- culture Handbook 296 (1965). 65 ------- Figure A-i - The Result of Pesticides Use Data Survey. The dotted counties are those that answered the questionnaires. a’ 0’ L ------- t 5 ELE A-2 DArA Lt!t,Ofl 4flfl Zafl’Y Infostatien Water Quality Records, Statistics Ikily Records Water Q ality Records, Statistics Statistics of Water Quality Stations Waste frealusont Pacilities In- ventory and Facil ltiea Needs Statistics of Jaier Quality Stations Population Service, &ipply Source Type of eatnent, Design Ca- I)acit3’, daate (PR;, Strews Clas- s i t icatton Daily Records of the azepended Sediment l,osd, Statistics Drainage Area, Aversge Sediment for the Drainage Area and Per Unit Area, Soil Classification Daily Records of the Suspended Sediment losd A Suonisry of General Chemical Quality of Surface Water snd Relation of Quality Chsracteris- tics with Geologic, TOpographic, Influences Water Quality Related to Fishery Pollutin Data, Stream Water Quality Data, Inventory of Treatment Facilities Stream Mater Duality Near the Theaheent Plant Moderate Light Project Reports Moderate — Yes Unknown Sample Reports from K C fltada, Kansas. Bi. Blue hver West- side Mtss,,ar Analysis r each Snb-bas n Format 0 ’ •- 1 Data Coverage EPA STORET — Natoowide S “Water ftesources Data” Pert h - Nationwide URG E IJIGS Magnetic Storage Nationwide GWDC Tables and Magnetic Storage Nationwide EPA S f 12’ ? hattoawide 118 15 “National Reference List of Water Quality Stations” Nationwide State Dovernts “Inventory of Public Water and Waste ‘freathient Pa- c i ii ties’ Each State Corps of Reginesra “Suspended Sediment in the Missouri River Baainwide MBIAC “Sedimentation” (9 parts) Basinwide Corps of Engcneera C,E. Magnetic Tapes Baainwid.e !Uascur dater “Chemical Quality of State of Pollution Board Missouri Surface Water” Missouri dtjo’sing iame and Reports on Water Some Streams “ish Coneission Quality Studies and Lakes in Wyoming r tra :tate “hater P—hutton in Two Major ‘i Montana’ (2 Parts) l 5R-l9eO Basins in Montana tier arc datte “)peratin,r Records” Basi’iaide :reaiaent -e.nta Aonunt as ,fand Puma.rke Extensive All Stations in Basin, Statistics Extensive All Basin States Extensive None Extensive Basin Extenstve Basin Extensive Water Tears 1 5 11-1 512 Extensive Kansas, Missouri, So’..tn Dakota, lortn Inkota Wyoming, Montana, Iowa Moderate - Basin, 1949-1964 Modarata Yes Moderate None ------- ThBLS A—3 DATA CAflZOfl : MYDROSCG!C Aeency Forent Data Coverage — — Information Awnnt On Hand Remarks USGS “Water Resources Data,” Nati ide Drainage Area, Daily Dischsrge Extensive All Basin States Pert I Statistics USGS USGS Magnetic Tapes Nationwide Daily Discharge, Statistics Extensive None The Rest Hydrologic Data Storage Avail- able EPA STORE? Nationwide Daily Discharge, Statistics Moderate All Stations in Basin. Statistics River FOrecast SF0 Magnetic Tapes Basin-wide Gage Bating Curve, I idrograph Extensive None Center, W.B. USGS “Travel of Salutes in the Prom Yankton, Time of’ Travel of Solutea, Moderate Yes Lower Missouri River” South Dakota, Dispersion and Dilution of to St. Louis, the River Missouri USGS ‘tow Flow Characteristics State of’ Statietical Study of tow-Flow Extensive Yes of Missouri Streams” Missouri Information C D MBIAC “Stream Flow Character- Basinwide Stream Flow Duration, Mi Extensive Tee istics in the MBR,” and Low-flow Variation Char— 9 Parts acteristics USGS ‘ valuation of the Stream The Basin Stream Flow Characteristics, Extensive AU. the Basin States Except flow Data Program” States Basin Characteristics, and Minnesota Climatic Characteristics, and Relation Aenng Thea, on the State Basis Bureau of Tables, a List of Water Basinwide The Stations for Which the Moderate Yes Reclamation Stattons Data Have Not Been Published USGS Tables Basuiwide River Depth, flow Velocity Extensive None Not Published Tables, and Magnetic Stor- Nationwide Statistics of Surface Water Extensive -Basin age, “Catalog of InfOrmation Stations on Water Data” Corps of Maps, “Flood Plain In- Nationwide Water Surface Profiles; Extensive Johnson County, llama Engi-eers fornation” Flood Plain Cross Sections ------- BLE A-4 MTA CAWLOFI; CLIM&TOLO IICAI Data Coverage Information A m aunt On Hand Re 1rarks RCAA “Cl lratological lhta” Nattons,tde (i) Hourly Precipitation end Extensive 1966-1571 Excellent Data Tar. les Temperature for the First AU Basin States Order localities; (ii) Daily Precipitation, Daily Mexiaiss and Mlnlrasn T era- bite for all Stations, Prow Fail end Daow on the Ground for S Stations (iii) Monthly S ry; Yearly Busrj. 5DM SCM Megnetic Tspea The Basin Precipitation Data Extensive Yea States MBIAC “Selected Climatic ltpa” The Baste (i) Normal Annual Total Moderate Ye, States Precipitation (ii) 2lrHr, 25-Year Rainfall (iii) Monthly Distribution of Precipitstion (iv) Temperature Distribution - ‘ by Months 0” (v) Prevailing Direction and S O Stan Speed of Wind (Monthly), etc. MBIAC “Mclti-Annual Precipitation Sasiowide (i) Adjusted Average Annual Extensive Yes Analysis for Each Probabilities” (S Parts) Precipitation Dab-basin (ii) Multi-Annual Preciptta- tion Probabilities (iii) Annual Run-Off vs. An- nual Precipitation, etc I€IAC “Analjsis of Freeze-Thaw Basinwide (i) Preeze-Up and Break-Up Moderate Yes Dates” Dates for )tjor lakes and Reservoirs (ii) Average Number of Days Per Winter Season in a Freeze Condition (iii) Average Data of Com- plete Break-Up, etc ‘Evaluation of Stream floe Bastowide (t) Mean Annual Precipitation Moderate All Basin States Br- Data were used t’ C,rrelats Data Program” (ii) 2-Year, 24-dr, Precipt- cept Minnesota with Stream floe Data tation Intensity (iii) Mean Minimum Jsnua Temperature etc CiAA “ at’ Cs trequencj Nation.ide Rainfall Frequencj Moderste Tea -tIe: c’ iou u.s.” and lotenait l ------- rAPT -F -5--- DaTA CAThGORY: LARD USE Pormat Data Coverage Information Amount On Rand markz Soil Conservatior Tanles ‘Conservation Nationwide On t im County Basis - Land Use All Basin States Service Needs Inientory,” 1958- and Conservation Trea nt 1360 Needs; Statistics of Cropping - Patterns with Yield end Pro- jected Yteld b7 Source Area. - Soil Resource Groups, and Sub-basins; Public Lande Are Not Included. IGIAC Magnetic Tapes Baainwide The Above Inventory Plus Soil £çs Classification Soil Conservation Tables. Magnetic Tapes Nationwide On the County Basis - Acreage Extensive All Basin States Service “Conservation Needs In- — - in Major Uses end Acreage of ventory” 1966-1967 Each Lend Use Classified by Thysical Problems Affect ng Its Use, Estimates of Needs for Coneervation Treathent. Public Lands are Not Included. 0 - Bureau of tne Tablee, Magnetic Tapes, Nationwide FOr Each County, Number of Farm Extensive Magnetic Tapes, All Census “Census of Agriculture” Land in Fkrms, the Lend Use; Basin States 1363 Livestock and Ibultry, Crops Harvested, Agriculture Chemical Used, Etc. Data Include 1964 Statistics for Comparison With 1969 Figures . MBIAC Working Papers “Land Basinwide On tim Sub-Basin Basis - Areas Yes Resource Appendix” of Land and Water, Land Owner- ship, Land Uses State Board of Tables. “State Crop- State Major Crop Acreage, Production Extensive All Basin States Agriculture land and Livestock Data and Livestock Data, by Except Minnesota Data” (Annual Publication) County USDA (ABCS) Tables. Magnetic Tapes Nationwide By County and by State, Netail Extensive 1970, Tables by State Feed Grain and Wheat Crop Acreage Programs.” 1970, 1971 ------- ______ TA CATEGOR - TOPCGRAFII ; fl1E A.5 Toograph teal Maps “Miso’jri River Basil Condensed Tabulation or River Mileage and Drain- age Areas” “Evaluation of Stream flow Data Program” _____________ Information Elevatio’i Contour Scale Interval Natinr.i e 1:24,000 10 ft - - 1:250,000 50 ft 1.500,000 200 ft —Sasnvite Listing 900 Tributaries for: (a) Gage Locat:ons (ii) Mileage Above the Mouth (iii) Noncontributing Area (iv) Drainage Area Nationwide Basin Characteristics in Terms of Drainage Area, Main Channel Slope, Forest Cover, Soil In- filtratio’i Index, Etc. Mountainous Area in Colorado, Wyoming and Montana Elevation vs. % of Area Below or at Some Elevation Moderate Al ], Basin States Thccept Minnesota Batensive Yellowstone River, Big Horn River Mire Letailed Information Availanle from the State Agencies Correlation of Stressi Flow Characteristics with Basin and Climatic Charac- teristics USGS u&;s Table, “Slopes of Basil Drainage Areas” Tables Basinvide For Drainage Area of Lees Than 10 Sq Mi Basinwide Drainage Area, Cross-Sectional Area of River Stream, River Body Slope Moderate None Thctensive None Information for Gaged and iineaged Sites. Not Published Soil Conservation Service !tgnetic Tapes “Conserva- tion Needs Inventory” 1966-1967 Nationwide Slope Forcent Class of County bctensive Yes Format : Eata Coverage Agetcy US GS K IAC USGS River FOrecast Center, NOAA Remarks Amount On Hard Exteneive Clay County, Kansas AU Basin States Moderate Yes “Area - Elevation Maps” ------- TABLE P-i ______ Data Coverage Information Generalized Soil Infiltration Grounings, Infiltroseter Field-Plot Data Infltrat :,r Estimates from Rydrograph and Storm Analyses, and Infil:rati:n Values Used in Design Fltod Studies Basinwide Soil Classification CorreleLed With the Land Use Survey Froa the Conservation Needs Inventor’g Nationwide Soil Maps, Soil Laboratory Data, Land-Capability Interpretatz ons, Soil-Woodland Interpretation Engineering Use of Soil, eto Tables, Maps Great Plains Soil Classification Based on States Sediment Yield Tables Basinwide Soil Index b,r Watershed ttgnetic Tapes, “Conserva- Nationwide County Soil Erosion Class tion Needs Inventory” (1966-1967) The Mist Cusprehensive and Systnastic Soil Classi- fication data Available for MBR (According to Mr Putman of MBIAC) Extensive None (under Capable of Extend:ng to .it preparation) Basin States Extersiye AU Basin States Extensive AU sin States , Basinwjda a,- DATA CATh(YJRY: 50Th 2ASSIs IrrTo., A gency - i:rnat MBIAC TaUss and ‘!ats MBIAC Magnetic Tape USDA (ASCS) “Soil Survey” USDA (ASCS) USGS Soil Conservation Service 1.) Fusar ics Amount c _ 1a’ - Materste Yes Extensive Yes Extensive “Soil Sr sy” of Shawnee County, Kansas and “Published Soil Survey of the U.S ------- TABLE A-S DATA C TROItf: LIVESTOCK Pgency Format Data Coverage Information Ai unt On Hand Remarks State Board of Tables, “State Cropl.and State Number of An imals (Cows, Beef Extensive All Basin States A g rtcu lture and Livestock Data” Cattle, Hogs, Sheep, Pbultry) of Each Type by Counties, Published Annually USDA “Agricultural Statistics” Nationwide Same, by Stetes Yes Bureau of Census Tables, )tgnetic Tapes Nationwide Number of Animals, Inventory Extensive Sgnetic Tapes, “Census of Agriculture” and Sales by County AU Basin States 1969 ------- TABLE A- S DATA CA’ltGOfff’ PS3TICIJE3 Format Data Coverage Infcrmation Amcant On Hand Remarks 5:; ‘;s:s) Pest:cide Renew” ilstion’.ide Gross ran ai Prodactir o ’ Yes (1970) Major Her :c des, ci es and }bst c des; Some Data :n State Level Agr:czlr.ral Statistics Netionjide Total ?rod,.cticr. b T ’pe Yes State Extezsiot ‘Livestock Ir’sect Co trc1 Basinwide Recon ended Applicaticri Rates Yes (Kansas) Ser’nce Recommer,dations” ard Practices of I’secticides on Livestock State Extenz:c,’- F:eld Crop Thse:t Control Service Reccendations” Stete Recou endedApplicattcn Rates Yes ( Kansas) and Practices of Insectic:des a - on Field Crops State Exte sio’ ‘Chemical Weed Control State Recoinended Application Rates Yes (Kansas) Service in Field Crops’ and Practices of Herbicides on Field Crops State Exte;s c-, “Chemical Weed Control State Recommended Application Rates Yes (Kansas) Ser-nce in Horticult ural arid and Practices of Herbicides Fcrestr 1 Plants” on Horticulture and B.brestr: ’ Plants USDC, Bureau of ‘Census of Agriculture” Nationwide Cost of Chemicals Used on rtgnetic Tapes, the Census Venous Crops end Acres Treated All Basin States for Insect and Weed Control, by Counties Countj Extension “131 Qiestionneire” Bssinwide Qientity of I sticides Used in Extensive One third of Service County, Names of the Most-Used Counties in the &sticides, and Events of Heavy Basin &st Infestations ------- TABLE A- b DnA ZEGCPY: FERTILI R Forcat Data Coverage Inforaation Amturt On Rand State 3c,ard :f “Fertilizer Tonnage Easinwide Consumption By County or State All Basin States ;ri:an.re Pepcrt” Spring and Fall . “Agricultural Statistics” Nationwide Consumption by State of Yes Four Major Categories of Fertilizers USDA CASTS) “The Fertilizer Supply” Nationwide Gross Production by ‘pe, Yes of Major !L pes of Fertilizers -4 t i ! USDC, ?ureau of Tables, gnatic Tapes Nationwide Cost and Ai unt of Corercial Magnetic Tapes, the Census “Census of Agriculture” Fertilizers and Lime Used and All Basin Stetea 1969 Acres on Which Used, by County ------- ThELE A-fl ; ci cLn::sI: : 2o;F ;.FE: Fon at Data ovsra e Informat±on ______ - s r i Remarks Bureau of tne Censt.s ttgnetic Tapes, Nationwide Population, Area, Income, Extensive Tatlas Tat J.es end Other Economic Infor- mat ion U S Water ?esouces Tables, “Economic Nationwide Population, Income, Fhploy- Extensive Yes Council Activity in the U.S. ment, and Other Economic by Water Resources Information Regions end Subareas, Historical, and Pro- jected 1929-2020.” a ’ ------- APPENDIX B INDIVI DUAL CONTACTS 77 ------- G. R. Coop Philips R. Johnson Fl. F. Mondschein V. Hagarty W. D. Haggard Balke H. Gunewald Walter Pool R. W. Eikleberry J. Karabatsos E. Burnett Organiz at ion MBIAC MBIAC Missouri River Basin Planning Office Corps of Engineers Corps of Engineers Washington, D.C. Lincoln, Nebraska Lincoln, Nebraska Name Mr. N. Mr. K. Mr. P. Barbarossa F. Myers L. Harley City, State Washington, D.C. Lincoln, Nebraska Omaha, Nebraska Omaha, Nebraska Kansas City, Missouri Kansas City, Missouri Asheville, North Carolina Kansas City, Missouri Washington, D.C. Kansas City, Missouri Billings, Montana Denver, Colorado Washington, D.C. Lincoln, Nebraska Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Mr. Dr. Mr. Mr. Mr. Mr. Mr. Mr. S. Conger P. Linderstruth D. B. Parke J. Keyes P. Gibbs I. A. Watson J. M. Ingles R. D. Hockensmith J. Putman NOAA, River Forecast Center NOM, U.S. Department of Commerce NOAA, U.S. Department of Commerce EPA, STORET EPA Bureau of Reclamation Bureau of Reclamation USDA Economic Research Service SCS U.S. Forest Service Scs 78 ------- Name Mr. D. White Mrs. M. Mason Mr. J. Towler Mr. J. T. Breen Mr. E. A. Moulder Mr. Grogil Mr. S. W. Wiitala Mr. q. W. Lane Mr.,fIP. Jordan Mr. A. M. Diaz Mr. E. R. Hedman Mr. C. R. Collier Mr. A. Homyk Mr Jeffrey Mr. G. Pike Mr. K. A. Mackich n Mr.IR. C. Williams Mr. J. E. Powell Mr. 0. Larimar Mr, R. Cushman Mr.}1. D. Edwards Mr. F. H. Pauszek Mr. Leman Mr. K. Webb Organization EPA Iowa State University ASCS BMreau pf the Census USGS USGS USGS USGS USGS USGS USGS USGS USGS USGS USGS Division of Game, Fish and Parks Water Pollution Control Commission 79 City, State Arlington, Virginia Ames, Iowa Kansas City, Missouri Suitland, Maryland Denver, Colorado Iowa City, Iowa Lawrence, Kansas St. Paul, Minnesota Rolla, Missouri Helena, Montana Lincoln, Nebraska Bismarck, North Dakota Huron, South Dako t a Cheyenne, Wyoming Washington, D.C. Denver, Colorado Denver, Colorado ------- Name Organization - - City, State Mr. F. D. Rolf Colorado Crop and Livestock Denver, Colorado Reporting Service Dr. G. M. Van Dyne Colorado State University Fort Collins, Colorado Colorado Soil Conservation Denver, Colorado Service Dr. Gakstatter The Stat;e Hygienic Des Moines, Iowa Laboratory Mr. R. Schliekelman Environmental Engineering Des Moines, Iowa Service Mr. R. H. Sutherland Iowa Crop and Livestock Des Moines, Iowa Reporting Service Iowa Soil Conservation Des Moines, Iowa Service Mr. 3. Burns Department of Health, Topeka, Kansas Mr. J. Stoltenberg Sewage, and Water Treatment Mr. R. Schoonover Kansas Forestry, Fish and Pratt, Kansas Came Commission Mr. J. Reh State Soil Conservation Sauna, Kansas Service Mr. F. Mosier ASCS Manhattan, Kansas Mr. F. Hoover State Board of Agriculture Topeka, Kansas Mr. J. E. Pallesen Kansas Crop and Livestock Topeka, Kansas Reporting Service Mr. Steps State Water Commission Topeka, Kansas Dr. H. Jacob Kansas Water Resources Manhattan, Kansas Research Institute Mr. R. Hyde State Extension, KSU Manhattan, Kansas (Agronomist) 80 ------- Organization State Extension, KSU (Agronomist) Entomologist Forester Department of Agronomy, KSU Environmental Health Program, KU Clay County Extension Johnson County Commission Johnson County Extension Miami County Extension Water Department Superintendent Board of Public Utilities Water Pollution Control Plant Water Department Water Works Department Water Department Municipal Service Soil Conservation Service Missouri Water Pollution Control Board Missouri State Department of Health Missouri Crop and Livestock Reporting Service Manhattan, Kansas Lawrence, Kansas Clay Center, Kansas Olathe, Kansas Olathe, Kansas Paola, Kansas Parsons, Kansas Kansas City, Kansas Kansas City, Kansas Ottawa, Kansas Leavenworth, Kansas Topeka, Kansas Russell, Kansas St. Paul, Minnesota Jefferson City, Missouri Jefferson City, Missouri Name Mr. L. Brooks Mr. J. Geisler Dr. 0. V. Bidwell City. State Manhattan, Kansas Mr. F. Bieverly Mr. W. Mr. R. Mr. T. Mr. E. Mr. J. Mr. A. Mr. M. Campbell Davis Hall J. Sisk N. Lackey W. Rumsey Cailtuex Mr.C.C. Mr. A. C. Mr. C. E. Mr. G. J. Nut t Lee Reynolds Boyd Mr. Mr. Mr. C. Stiefermann J. K. Smith D. Sayre Mr. D. W. Barrowman Columbia, Missouri 81 ------- C. H. Taylor R. Jackson’ D. Taylor Missouri Soil Conservation Service Capital City Water Company Water Treatment Plant Kansas City Water Works Chillicothe Municipal Utilities Sedalia Water Department Pollution Control Depart- ment Minnesota Crop and Live- stock Reporting Service Minnesota Department of Agriculture State Department of Health State Statistical Office Department of Game, Fish, and Parks Soil Conservation Service Agricultural Experiment Station, Montana State University Economic Research Service, Montana State University Nebraska Water Pollution Control Council Department of Game, Fish, and Parks 82 City, State Columbia, Missouri Jefferson City, Missouri Jefferson City, Missouri Kansas City, Missouri Chillico the, Missouri Sedalia, Missouri Kansas City, Missouri St. Paul, Minnesota St. Paul, Minnesota Name Mr. J. V. Martin Organization J. H. Fondreu C. P. Wood H. Marks C. Bennett Mr. Mr. Mr. Mr. Mr. Mr. Mr. Helena, Helena, Helena, Mr. L. M. Lehn ‘‘Mr. D. G. Williams Mr. D. L. Herbert Mr. Whitney Dr. C. Smith Dr. D. Larson Mr. R. Langemeir Mr. Foster Montana Montana Montana Bozeman, Montana Bozeman, Montana Bozeman, Montana Lincoln, Nebraska Lincoln, Nebraska ------- Name Mr. N. D. Belier Mr. P. Carson Williamson Mr. D. Dexter Mr. L. J. Hoffman Mr. R. C. Kronenberger Mr. L. Bourret Professor H. W. Hough Organization State-Federal Division of Agricultural Statistics Soil Conservation Service North Dakota State Department of Health North Dakota Crop and Livestock Reporting Service Soil Conservation Service State University Station North Dakota State University State Department of Health South Dakota Crop and Livestock Reporting Service Soil Conservation Service Plant Science Department South Dakota State University State Office of Health, Education and Welfare State Game and Fish Office Wyoming Cooperative Crop and Livestock Reporting Service Soil Conservation Service Wyoming Department of Agriculture Plant Science Division The University of Wyoming 83 Lincoln, Nebraska Bismarck, North Dakota Fargo, North Dakota Bismarck, North Dakota Fargo, North Dakota Pierre, South Dakota Sioux Falls, South Dakota Huron, South Dakota Brookings, South Dakota Cheyenne, Wyoming Cheyenne, Wyoming Cheyenne, Wyoming Casper, Wyoming Cheyenne, Wyoming Laramie, Wyoming City, Lincoln, State Nebraska Mr. V. Heavelen Mr. N. Peterson Mr. J. R. Price Professor E. H. Vasey Mr. M. Alluin Mr. J. C . Ranok ------- No Page 84 ------- APPENDIX C WATER QUALITY STATIONS SELECTED 85 ------- MRI STOR I’T ‘ STORET ( LLion Station Agency Code Code Stream Name Station Location 1000001 06058502 II2WRD Missouri Canyon Ferry Dam, M,intan,i 10(10006 00370033 I11ONET Missouri Bismarck, North Dakota 1000011 00300031 1I1ONET Missouri Onaha, Nebraska 1000016 00190029 111ONET Missouri Kansas City, Kansas 1000021 06934500 112WRD Missouri Hermann, Missouri 1100001 06026500 I12WRD Jefferson Twin Bridge, Montana 1120001 06016000 112WRD Beaverhead Barretts, Montana 1120006 06018500 112WRD Beaverhead Twin Bridge, Montana 1400001 06089000 112WRD Sun Vaughn, Montana 2100001 06140500 I12WRD Milk Havre, Montana 2100006 06154100 1I2WRD Milk Harlem, Montana 2100011 06172000 112WRD Milk Vandalia, Montana 2100016 06174200 112WRD Milk Glasgow, Montana 2500001 00571004 1117MBR Yellowstone Fishing Bridge, Wyoming 2500006 06191500 112WRD Yellowstone Corwin Springs, Montana 2500011 06192500 112WRD Yellowstone Livingstone, Montana 2500016 06214100 I12WRD Yellowstone Laurel, Montana 2500021 06218000 112WRD Yellowstone Custer, Montana 2500026 06296120 112WRI) Yellowstone Miles City, Montana 2500031 00290055 I11ONET Yellowstone Sidney, Montana 2520001 06202610 112WRD Stiliwater Beehive, Montana 2530001 06207500 112WRD Clarks Fk. Yellow Belfry, Montana 2550001 06264700 112WRD Bighorri Lucerne, Wyoming 2550006 06268600 I12WRD Bighorn Worland, Wyoming 2550011 06279500 112WRD Bighorn Kane, Wyoming 2550016 06287000 112WRD Bighorn St. Xavier, Montana 2550021 06288500 112WRD Bighorn Hardin, Montana 2550026 06294701 I12WRD Bighorn Bighorn, Montana 2551001 06228000 112WRD Wind Riverton, Wyoming 2551006 06259000 112WRD Wind Boysen Res., Wyoming 2551101 06233600 112WRD Popo Agie Hudson, Wyoming 2551106 06235500 112WRD Little Wind Riverton, Wyoming 2554001 06270000 112WRD Nowood Tens leep, Wyoming 2554006 06274220 112WRD Nowood Manderson, Wyoming 2555001 06277500 I12WRD Greybull Basin, Wyoming 2556001 06282000 112WRD Shoshone Buffalo Bill Res., Wyoming 2556006 06284400 112WRD Shoshone Garland, Wyoming 2556011 06286200 I12WRD Shoshone Kane, Wyoming 86 ------- MR. [ sToREr STORLI Stattim Station Agency (oth. Code Code Stream Name Stat LcflL Locat lult .!557001 06294000 II2WRD Little Bighorn Ilardin, MonLaiia 2 70001 06306300 1I2WRD Tongue Montana-Wyoming Line 5700O6 06308501 I12WRD Tongue Miles City, Montana 2530001 0631250() I12WRI) Powder Kaycce, Wyoming 2530006 0631700() U2WRD Powder Arvada, Wyoming 2580011 06324500 LI2WRJ) Powder Moorhead, Montana 2581001 06313000 I12WRD S. Fk Powder Kaycce, Wyoming 2583001 06313400 112WRI) Salt Creek Sussex, Wyoming 2584001 06316400 I12WRD Crazy Woman Cr. Upper Station, Wyoming 2585001 06326000 1 I2WRD Clear Creek Aryada, Wyoming 2700001 00400955 21S1)AKO1 Li LtIL’ Missouri Camp Crook. South Dakota 2800001 06340500 II2WRD Knife ll,izen, North Dakota 2810001 06340000 II2WRD Spring Creek Zap. North Dakota 3400001 06357500 I12WRD Grand River Sh .uhIitLL. South Dakota 3600001 06395000 1 IZWRD Cheyenne Edgc’nlont, South Dakota 3600006 06401500 112WRD Cheyenne Ango tura Dam, South Dakota 3600011 06423500 112WRD Cheyenne Wasta, South Dakota 3630001 06394000 112WRD Beaver Creek Newcastle, Wyoming 3650001 06427850 1I2WRD Belle Fourche Devils Tower, Wyoming 3650006 06428500 112WRD Belle Fourche Wyoming-South Dakota Line 3650011 06437000 112WRD Belle Fourche Sturgis, South Dakota 3650016 06438000 11ZWRD Belle Fourche Elm Springs, South Dakota 3651001 00460895 21SDAKO1 Redwater Belle Fourche, South Dakota 3800001 06445000 112WRD White Whitney, Nebraska 3800006 06447000 112WRD White Kadoka, South Dakota 3800011 00460003 I2IMBRCE White State Highway 47, South Dakota 3900001 00300917 21NEBOO1 Ponca Creek Verdel, Nebraska 4100001 06455900 112WRD Niobrara Dunlap, Nebraska 4100006 06457000 I12WRD Niobrara Coic. lesser, Nebraska 4100011 00300963 21NE13001 Niobrara RI ’c rview, Nehr akr 4100016 00300901 2 NEB00l Niobrara Niobrara, Nebraska 4110001 00300916 21NEBOO1 Keya Paha Napcr, Nebraska 4200001 06469000 I12WRD Jamestown Res. Jamestown, North Dakota 4200006 06470500 112WRD James l Moure, North Dakota 4200011 06471000 ]I2WRD James Cohm bia, South Dakota 4200016 00460041 I117MBR James Redfield, South Dakota 4200021 00460038 1117MBR James Huron, South Dakota 4200026 00460770 21SDAKOI James Mitchell, South Dakota 4200031 06478500 I12WRD James Scotland, South Dakota 4260001 00460052 I1L7MBR Redstone Creek Forestburg, South Dakota 4300001 06479000 1I2WRD Vemillion Wakoiila, SouLh lakota 440q0oL 00460740 2 ISDAKO1 Big Sioux W3ICL ’LOWII. South Dakota 87 ------- Stream Name Big Sioux Big Sioux Big Sioux Big Sioux Rock Floyd Little Sioux Maple Soldier Big Papillion Cr. L’la I t ’ Platte Platte Platte Platte Platte Medicine Bow Rock Creek Little Medicine Sweetwater Laramic Laramie Little Laramie Rawhide Creek Horse Creek Horse Creek Pumpkin Creek South Platte South Platte South Platte South Platte Station Location BrookingS, South Dakota Dell Rapids, Iowa Sioux Falls, South Dakota Sioux City, Iowa Minnesota-IOWa Line Sioux City, Iowa River Sioux, Iowa Frederick, South Dakota Mondamin, Iowa 1li1ha, Nebraska Brady, Nebraska Overton, Nebraska Grand Island, Nebraska Duncan, Nebraska Schuyler, Nebraska Plattsmouth, Nebraska Northgate, Colorado Seminoe Rca., Wyoming Alcova, Wyoming Casper, Wyoming Glenrock, Wyoming Orin, Wyoming Glendo Rca., Wyoming Guernsey Res., Wyoming Wyoming-Nebraska Line Lisco, Nebraska Seminoc Res, Wyoming Rock River, Wyoming Bow Medicine Bow, Wyoming Alcova, Wyoming Laramie, Wyoming Fort Laramie, Wyoming Two Rivers, Wyoming Lingle, Wyoming Wyocross Ranch, Wyoming Yodel, Wyoming Bridgeport, Nebraska South Platte, Colorado Littleton, Colorado Kersey, Colorado Weldona, Colorado MRI STORET SLati on Station Agency Code Code Code 4400006 06480000 11 2WRD 44001)1 I 0o48 1000 1 1.!WRD /440()0 H, 01)460081) 1 I 1 ONET /i40 00 2 I 064859,1) I I 2WRD 44 1000 I 0C8 1 5 E64 2 I Ml MN /4500001 06600520 I I2WRD 5600001 06607513 [ I2WRD 46 I 00(11 00460810 .1 1SDAKO1 4/00001 0b( 0850” I 2WRD 4800001. 00300205 2 INI:lioOl 4900001 06765991 I 12WRD 4900006 06767999 I I2WRD 4900011 06770499 I 12WRJ) 4900016 0674000 1L2WRD 4900021 06794700 1 I2WRD 4900026 00300086 I11ONET 4910001 06620000 I12WRD 4910006 06630000 1 12WRD 4910011 01,642000 I I2WRD 40 10() 16 0(m45000 1 I2WRD 4910021 06646800 IL2WRI) 4910026 0665200() II2WRD 4010031 06652800 1 I2WRD 49W036 06656001 II2WRD 491004 I 066 74500 1 12WRD /i910046 (16686000 I L2WRD 4911001 06635001) ll2W IU) 491111)1 0663350(1 I12WR1) 4q [ 1 ‘Ill 06634601) I I2WRI) 4912001 061,39000 I I2WRB 491’300l 06660000 1I2WRD 6913006 06656000 ILZWRD 4913101 06661500 I I2WRD 4914001 06671000 I12WRD 4915001 06676550 I 12WRD 4915006 06677010 II2WRD 491.6001 06685000 112WRD 4920001 00000025 21COLOO1 4920(106 00000024 2ICOLOOL 492001 1 06754000 I1ZWRD North North North North North North North North North North Platte Platte Platte Platte Platte Platte Platte Platte Platte Platte 88 ------- MR I ST ORE’l STORET L.ILhon Station Agency Code Code Code Stream Name Station Location 4t)20021 000O0O. 1 2ICOLOO1 South Platte lloliac, Colorado 4’) 0().!6 06764001 II2WRI) South Platte Julesburg, Nebraska 4’)20tfl 1 00300912 2INEBOOI South Platte Hershey, Nebraska 4 ’L 200L o000003 21c:oLOOi Bear Creek Jcff-Arapahoe Line, Colorado 4)2J001 00000346 2ICODIIDP Cherry Creek Denver, Colorado 4974001 00Q0003 2 1c:OLOOl Clear Creek Golden, Colorado 4924006 00000034 21c0L001 Clear Creek Derby, Colorado 4925001 06731000 1I2WRD St. Vram Creek Platteville, Colorado 4925101 00000033 21COLOOI Boulder Creek Boulder-Weld Line, Colorado 4926001 06744000 II2WRD Big Thompson La Salle, Colorado 4927001 00000027 2lCOLOOl Lache La Poudre Greeley, Colorado 4928001 00300931 2INEBOO1 Lodgepole Creek Chappell, Nebraska 4930001 06772500 112WRD Wood Chapman, Nebraska 4940001 00300914 21NE 13001 Loup Monroe, Nebraska 4941001 00300922 21NEBOO1 South Loup St. Michael, Nebraska 4942001 00300990 21NEBOO I Middle Loup Dunning, Nebraska 4942006 06778500 l].2WRD Middle Loup Comstock, Nebraska 4’)42011 00300921 21NEBOO1 Middle Loup Boelus, Nebraska 4942016 06785000 112WRD Middle Loup St. Paul, Nebraskd 4942101 00300993 21NEBOO1 Dismal Dunning, Nebraska 4943001 00300983 21NEBOO1 North Loup Taylor, Nebraska 4943006 00300920 21NEBOO1 North Loup St. Paul, Nebraska 4943101 00300986 21NEBOO1 Calamus Burwell, Nebraska 4944001 00300935 2INEBOOI Cedar Fullerton, Nebraska 4950001 06799000 112WRD Elkhorn Norfolk, Nebraska 4950006 06799300 112WRD Elkhorn Stanton, Nebraska 4950011 06800500 112WRD Elkhorn Waterloo, Nebraska 4951001 06799450 I12WRD Logan Creek Pender, Nebraska 4951006 06799500 112WRD Logan Creek Uehling, Nebraska 4952001 06800000 I12WRD Maple Creek Nickerson, Nebraska 4960001 06803500 112WRD Salt Creek Lincoln, Nebraska 4960006 00300930 21NEBOO1 Salt Creek Ashland, Nebraska 4961001 06804000 II2WRD Wahoo Creek Ithaca, Nebraska 5100001 06810000 1I2WRD Nishnabotna Hamburg, Iowa 5200001 00301140 21NEBOO1 Little Nemaha Auburn, Nebraska 5300001 00301136 21NEBOO1 N. Fork Big Nemaha Dawson, Nebraska 5300006 00300904 21NEBOO1 Big Nemaha Preston, Nebraska 5400001 06813000 112WRD Tarkio Fairfax, Missouri 5500001 06817500 112WRD Nodaway Burlington Junction, Missouri 5500006 06817800 112WRD Nodaway Oregon, Missouri 5600001 06821200 112WRD Platte Platte City, Missouri 5610001 00280158 12INBRCE 102 River Avenue City, Missouri 89 ------- MR I STORET STORET tat1or Station Agency Code Code Code Stream Name Station Location 570000] 06889000 112WRD Kansas Topeka, Kansas 0000ô 06892500 1 L2IJRD Kansas Bonner Springs, Kai’s;Lr 7 [ 0001 00000070 ICOLOO 1 Republican Bonny Res. , Kansas 7 [ 0006 06824500 II2WRD Republican Benkelman, Nebraska ‘ 7l0011 06829500 II2WRD Republican Trenton, Nebraska 5710016 00300913 2INEROOI Republican McCook, Nebraska 5710021 06844500 I12WRD Republican Orleans, Nebraska 5710026 06849500 I I2WRD Republican harlan County Dais, Nebraska 5710031 06853000 1I2WRD Republican Guide Rock, Nebraska 3710036 06853400 112WRD Republican Superior, Nebraska 5710041 00190175 21NEBOO1 Republican Hardy, Kansas 5710046 06854500 112WRD Republican Scandia, Kansas 5710051 06856000 112WRD Republican Concordia, Kansas 5710056 06857100 112WRD Republican Milford Darn, Kansas 5713001 06835500 112WRD French Creek Culburtsori, Ncbraska 5714001 06837900 I12WRD Red Willow Cr. Red Willow, Nebraska 5716001 06845000 1 I2WRD Sappa Creek Oberlin, Kansas 5716201 06844900 112WRD S. Fk. Sappa Creek Achilles, Kansas 5716301 06846500 112WRD Beaver Creek Cedar Bluffs, Kansas 5717001 06847900 112WRD Prairie Dog Cr. Norton, Kansas 5717006 06848500 I12WRD Prairie Dog Cr. Woodruff, Kansas 5718001 06855800 1I2WRD Buffalo Creek Jamestown, Kansas 5720001 06862700 1I2WRD Smoky Hill Schoenchen, Kansas 5720006 06864000 IL2WRD Smoky Hill Russell, Kansas 5720011 06864500 112WRD Smoky Hill Ellsworth, Kansas 5720016 06865500 112WRD Smoky Hill Langley, Kansas 5720021 06866500 1I2WRD Smoky Hill Mentor, Kansas 5720026 06870200 I12WRD Smoky Hill New Cambria, Kansas 5720031 06877600 112WRD Smoky Hill Enterprise, Kansas 5723001 06863500 1I2WRD Big Creek Hays, Kansas 5724001 06867000 I12WRD Saline Russell, Kansas 5724006 06868200 II2WRD Saline Wilson Dam, Kansas 5724011 06869500 I12WRD Saline Tescott, Kansas 5724016 06870100 112WRD Saline New Cambria, Kansas 5724101 06867500 1I2WRD Paradise Creek Paradise, Kansas 5725001 0687590() I12WRD Solomon Glen Elder, Kansas 5725006 06876900 I12WRD Solomon Niles, Kansas 5725101 06871000 1I2WRD N. Fk. Solomon Glade, Kansas 5725106 06872500 112WRD N. Fk. Solomon Portis, Kansas 5725201 06873000 112WRD S. Fk. Solomon Webster Res., Kansas 5725206 06874000 1L2WRD S. Fk. Solomon Osborne, Kansas 90 ------- N IH STORET STORET Station Station Agency Code Code Code Stream Name Station Location 5726001 06878500 I I2WRD Lyons Creek Woodbine, Kansas 5730001 06879900 I I2WRD Big Blue Surprise, Nebraska 730006 00300924 21NEBOO1 Big Blue Crete, Nebraska S730011 068824(K) II2WRD Big Blue Okcto, Kansas 5730016 0688700() II2WRD Big Blue Manhattan, Kansas 5731001 06880000 1I2t4RD Lincoln Creek Seward, Nebraska 5732001 06880800 112WRD W. Fk. Big Blue Dorchester, Nebraska 5733001 06881200 1I2WRD Turkey Creek Wilber, Nebraska 5734001 06883000 1I2WRD Little Blue Deweese, Nebraska 5734006 00301107 2INEBOO I Little Blue GiLead, Nebrdska 5734011 00301104 2JNEBOO1 Little Blue Fairbury, Nebraska 57i40 16 06884400 111LJRD Little Blue Barnes, Kansas 57 i)00I 06890400 112.tJRD De1 iwarc Arrtngton, Kansas 5740006 00190191 UIMBRCE Delaware Perry Res. Kansas 57 500() I 06891500 1 12WRD Wakarusa Lawrence, Kansas 5800001 06902000 [ 12WRD Grand Sumner, Missouri 5810001 06899620 I12WRD Thompson Chillicothe, Missouri 5900001 06905500 112WRD Chariton Prairie Hill, Missouri 6100001 00280955 2lM0000l Lamine Pilot Grove, Missouri 6200001 00280943 211400001 Moreau Jefferson City, MissQuri 6300001 06916600 I12WRD Marais Des Cygnes Kansas-Missouri Line Osage 6300006 0028095C) 211400001 Lake Ozark Warsaw, Missouri 6300011 00280957 211100001 Osage St. Thomas, Missouri 6310001 06917000 112WRD Little Osage Fulton, Kansas 6311001 06917500 112WRD Marmaton Fort Scott, Kansas 6320001 00280963 211400001 Sac Stockton, Missouri 6330001 00190206 12IMBRCE Poimne de Terre R. Hermitage, Missouri 6340001 00280965 21M00001 South Grand Urich, Missouri 6400001 00280967 211400001 Gasconade Jerome, Missouri 91 ------- No Page 92 ------- APPENDIX D SELECTION OF IMPORTANT PARAMETERS 93 ------- For the purpose of providing adequate streamfiow information at any point on any stream, the U.S. Geological Survey has set up a nationwide program to study the streainflow characteristics by means of systems model approach. Both methodology adopted and result obtained in this program are published and are extremely useful to this project as an indication of important data parameters. The statistical characteristics of streamflow can be defined by stream gauging, analytical methods of regionalization, systems studies, or any combination of these. Stream gauging at every site where information may be required is generally considered to be too expensive. However, Cost of obtaining adequate information can be reduced by supplementing the information with regionalization and system studies. The method adopted to regionalize streamfiow characteristics for natural- flow streams is to relate them to basin and climate characteristics in equations developed to use multiple-regression techniques applied to historic data. The standard error of estimate of regression equations thus obtained can be used to judge the accuracy of estimation. The equation and its constants having been defined, streamf low characteris- tics for a specific site in a given basin can be computed by substituting the appropriate values of the hydrologic variables in the equation. Tables D-l, D-2, and D-3, respectively, list streamfiow parameters, drainage-basin physical parameters and climatic parameters considered in this program. Table D-4 presents regression equations for the basin states. 94 ------- TABLE D-l SUMMARY OF STREAMFLOW CHARACTERISTICS Symbol Characteristics Definition M 72 , M 7 , 10 , M 720 Low-flow Annual minimum 7-day flows at 2-year, 10-year, and 20-year recurrence. Q 2 Q 5 , etc. Flood-peak Discharge from the annual flood- frequency curve at recurrence - intervals of 2, 5, 10, 25 and 50 years. - V 7 , 2 V 710 , V 750 Flood-volume Annual highest 7-day mean-flows at recurrence intervals of 2, 10, and 50 years. Q Mean-flow, annual Mean-flow of the annual means. a Q Mean-flow, monthly Mean-flow for each calendar month, subscript “n” refers to the nu- merical order of the month begin- ning with January as 1. SDa Flow-variability, Standard deviation of annual mean. annual SD Flow-variability, Standard deviation of monthly means, monthly subscript “n” refers to the nu- merical order of months with January as 1. ------- TABLE D-2 SUMMARY OF DRAINAGE BASIN PHYSICAL CHARACTERISTICS Symbol Characteristics Unit Definition A Drainage area Square mile Area measured in a horizontal plane, enclosed by a topographic divide from which direct surface runoff from precipitation normally drains by gravity into the stream above the specific point. L Main-channel length Miles The distance from the gauging station to the basin divide. S Main-channel slope Ft/mile The river body slope determined from the elevatioz at points 107. and 857. of the distance along the channel from the gauging station to the divide. E Mean-basin elevation Feet Mean elevation for the basin above mean sea level. F Forest area Percent The percentage of forested area in total drainage area. S Area of lakes and ponds Percent The percentage of area of lakes and ponds in total drainage area. ‘S 1 Soil infiltration index Inches The value of potential maximum infiltration during an annual flood under average soil-moisture conditions. ------- TABLE D-3 SUMMARY OF DRAINAGE BASIN CLIMATIC CHARACTERISTICS Symbol Characteristics Unit Definition P Mean annual Inches precipitation P Mean monthly Inches Mean precipitation for each calendar month, sub- precipitation scription “n ” refers to the numerical order of months with January as 1. P 24 2 Rainfall intensity I nches The maximum 24-hr rainfall having a recurrence interval of 2 years. P 24 , 50 Rainfall intensity Inches The maximum 24-hr rainfall having a recurrence interval of 50 years. E Evaporation Inches Mean annual evaporation in basin. Snowfall index Inches The water equivalent of snow on ground 1-15 March with 10% probability. Mean minimum January temperature Mean maximum March temperature Mean maximum July temperature ------- TABLE D-4 SUNMARY OF REGRESSION ANALYSES OF ME&N ANNUAL FLOW Standard Error of Region Equation Estimate, 7. Remarks Colorado 0.189 -Mountains Region Qa = 0.00140 A° 956 S 0192 p 21 ° 1 T 1 47 Kansas Q = 0.106 A° 947 (P_14.O)L 613 E -0.771 28 a v Missouri -Plains Region a = 0.037 A° 983 P 242 2 . 7 O Si- 0 . 511 10.6 -Plateau Region 0.288 A 11 ° (F + 1)0.124 27.5 Montana 0.900 4.91 0.430 -Region A Qa = 0.000344 A (E/1000 F 31 E 6 , 000 = Area above 6,000 ft P 0555 E UJ. 4 ft elevation, 7. 6,000 -Region B Q = 0.0522 L’’ 47 E° 613 53 a 6,000 0 937 0.406 -Region C Q 8 = 0.002 A S F° 581 P 0 . 889 27 pl. 61 E° -° 3 24,2 6,000 Nebraska -Sand Hills Region a = 0.0175 LL 23 S °. 499 S 1 19 D ° 405 33 D = A special index developed for Sand Hills Streams -Outside the Sand Q = 0.0484 A ” 55 A ° 54 ° F° 97 P 1 . 65 31 A = Contributing drainage Hills Region a E °• 954 S -1.70 n area, square miles North Dakota a 0.54 A° 975 S° 36 ° (E - 12)1363 61 Sh = Basin shape factor, a (T 3 - 26)] 176 h° 359 (F + 0.01)0084 ratio of length to the ------- - TABLE D-4 (Concluded) SUMMARY OF REGRESSION ANALYSES OF MEAN ANNUAL FLOW Standard Error of Region Equation Estimate. % Remarks 0.951 4.342 1.283 South Dakota a = io 6 A s 66.2 -James River Basin -the remaining portion Qa 6.11 X 1O ALOO 2 F° 224 1.916 0.624 : 1224 Sn 72.7 of the state 1.01 -0.123 0.051 0.788 Iowa = 0.00341 A S F (P-20) 15 0.261 -0.294 0.366 (T 7 -80) s 24.2 0.56 1.64 1.78 0.76 Wyoming Qa = 3.12 x iO A° 97 S E P Lat 27 Lat = Latitude of the center of the drainage basin, in decimal form, less 40.00. ------- No Page 100 ------- APPENDIX E MRI STATION AND RIVER CODES 101 ------- The water quality stations selected in this program were operated by 10 different agencies, and each agency has its own coding system. To facilitiate easy identification a special MRI coding system was designed. The MRI station code has seven digits, the first five comprise the river code and the last two are the station number. From the code, we can tell on which river the station is located and its relative location to other stations along that river. The River Code The five-digit river code (Table E-1) is a specific number assigned to each stream for the identification of: (1) stream rank; and (2) stream number. The stream rank is indicated by the number of digits in the code, which are other than zero. These nonzero digits are assigned from left to right, with higher nonzero digits for higher rank streams. The Missouri River main stem is ranked one and is coded with one nonzero digit (code 10000). Rivers flowing directly into the Missouri River are ranked two and are coded with two nonzero digits (e.g., the Sun River: 14000). Rivers of other ranks are coded in the same manner. The stream numbers are assigned consecutively in the downstream direction. Based on the observer looking downstream, the first river encountered is given a number 1 (the last nonzero digit). The next river encountered is given a number 2, etc. In general, we have less than 10 rivers in a single tributary. Therefore, a single digit has been sufficient to in- dicate the stream number. The exception is the Missouri River, to which more than 50 secondary streams are tributaries. The stream numbers for these tributaries are given by the numbers 11 to 64 with deletion of the numbers 20, 30, 40, 50, and 60, each of which would indicate a stream of rank one. For example, the code for the Milk River is 21000 instead of 20000 which would indicate a stream rank equivalent to that of the Missouri River. Furthermore, MRI River Code 14000 given to the Sun River, indicates that: (1) it is a second-rank stream (two nonzero digits); and (2) it is the fourth tributary (from upstream) encountered by a river of the next higher rank (the Missouri River). 102 ------- Station Number The two-digit station number is assigned also in the downstream dircction. The first station is given the number 01, the second station is given 06, etc., each time with five higher than the previous number to leave space for the addition of new stations. The combination of River Code (at right) and Station Number constitutes the MRI Station Code. For example, Station 2500006 is the second station (06) on River 25000 (the Yellowstone River). Appendix C lists the codes for all the selected stations. 103 ------- TABLE E-l RIVER CODE MISSOURI RIVER BASIN River Code Tributary Missouri River 10000 Jefferson River 11000 Montana a. Bedrock River 11100 Montana b. Beaverhead River 11200 Montana c. Ruby River 11300 Montana d. Big Hole River 11400 Montana e. Boulder River 11500 Montana f. Madison River 11600 Montana Gallatin River 12000 Montana Smith River 13000 Montana Sun River 14000 Montana Marias River 15000 Montana a. Two Medicine Creek 15100 Montana b. Outbank Creek 15200 Montana c. Willow Creek 15300 Montana d. Teton River 15400 Montana Arrow River 16000 Montana Judith River 17000 Montana Husseishell River 18000 Montana a. Boxelder Creek 18100 Montana Dry Creek 19000 Montana Milk River 21000 Montana a. Big Sandy Creek 21100 Montana 1. Sago Creek 21110 Montana b. Peoples Creek 21200 Montana c. White Water Creek 21300 Montana d. Frenchman River 21400 Montana e. Beaver Creek 21500 Montana f. Rock Creek 21600 Montana Redwater Creek 22000 Montana Poplar River 23000 Montana Big Muddy Creek 24000 Montana Yellowstone River 25000 Wyoming, Montana, North Dakota a. Shields River 25100 Montana b. Stiliwater River 25200 Montana c. Clarks Fork 25300 Wyoming, Montana d. Pryor Creek 25400 Montana 104 ------- TABLE E-l (Continued) River Code Tributary e. Big Horn River 25500 Wyoming, Montana 1. Wind River 25510 Wyoming (a) Popo Agie (Little Wind) River 25511 Wyoming 2. Muskrat Creek 25520 Wyoming 3. Badwater Creek 25530 Wyoming 4. Nowood Creek 25540 Wyoming 5. Greybull River 25550 Wyoming 6. Shoshone River 25560 Wyoming (a) North Fork Shoshone River 25561 Wyoming 7. Little Big Horn River 25570 Montana f. Rosebud Creek 25600 Montana g. Tongue River 25700 Wyoming, Montana h. Powder River 25800 Wyoming, Montana 1. South Fork Powder River 25810 Wyoming 2. Middle Fork Powder River 25820 Wyoming 3. Salt Creek 25830 Wyoming 4. Crazy Woman Creek 25840 Wyoming 5. Clear Creek 25850 Wyoming 6. Little Powder River 25860 Montana i. O’Fallon Creek 25900 Montana Little Muddy Creek 26000 North Dakota Little Missouri River 27000 Montana, South Dakota, North Dakota a. Boxelder Creek 27100 Montana Knife River 28000 North Dakota a. Spring Creek 28100 North Dakota Heart River 29000 North Dakota Apple Creek 31000 North Dakota Cannonball River 32000 North Dakota a. Cedar Creek 32100 North Dakota Beaver Creek 33000 North Dakota Grand River 34000 North Dakota, South Dakota a. North Fork Grand River 34100 North Dakota b. South Fork Grand River 34200 South Dakota Moreau River 35000 South Dakota 105 ------- TABLE E-l (Continued) River Code Tributary Cheyenne 36000 Wyoming, South Dakota, Nebraska a. South Fork Cheyenne River 36100 Wyoming b. Lance Creek 36200 Wyoming c. Beaver Creek 36300 South Dakota, Wyoming d. Hat Creek 36400 South Dakota, Nebraska e. Belle Fourche River 36500 Wyoming, South Dakota 1. Redwater Creek 36510 South Dakota f. Cherry Creek 36600 South Dakota Bad River 37000 South Dakota White River 38000 South Dakota, Nebraska a. South Fork White River 38100 South Dakota Ponca Creek 39000 South Dakota, Nebraska Noibrara River 41000 Nebraska, South Dakota a. Kayapaha River 41100 South Dakota, Nebraska James River 42000 North Dakota, South Dakota a. Pepestem Creek 42100 North Dakota b. Elm River 42200 South Dakota c. Mud Creek 42300 South Dakota d. Snake Creek 43400 South Dakota e. Turtle Creek 42500 South Dakota f. Redstone Creek 42600 South Dakota Slermillion River 43000 South Dakota Big Sioux River 44000 South Dakota, Iowa, Minnesota a. Rock River 44100 Iowa, Minnesota Floyd River 45000 Iowa Little Sioux River 46000 Iowa, Minnesota a. Maple River 46100 Iowa Soldier River 47000 Iowa Papillion Creek 48000 Nebraska Platte River 49000 Colorado, Wyoming, Nebraska a. North Platte River 49100 Colorado, Wyoming, Nebraska 1. Medicine Bow River 49110 Wyoming (a) Rock Creek 49111 Wyoming (b) Little Medicine Bow River 49112 Wyoming l0 ------- TABLE E-1 (Continued) River Code Tributary 2. Sweetwater River 49120 Wyoming 3. Larainie River 49130 Wyoming, Colorado (a) Little Laramie River 49131 Wyoming 4. Rawhide Creek 49140 Wyoming 5. Horse Creek 49150 Wyoming, Nebraska 6. Pumpkin (Pumpkinseed) Creek 49160 Nebraska b. South Platte River 49200 Colorado, Nebraska, Wyoming 1. South Fork South Platte River 49210 Colorado 2. Bear Creek 49220 Colorado 3. Cherry Creek 49230 Coloardo 4. Clear Creek 49240 Colorado 5. St. Vram Creek 49250 Colorado (a) Boulder Creek 49251 Colorado 6. Big Thompson River 49260 Colorado 7. Lathe la Poudre River 49270 Colorado 8. Lodgepole Creek 49280 Nebraska, Wyoming c. Wood River 49300 Nebraska d. Loup River 49400 Nebraska 1. South Loup River 49410 Nebraska 2. Middle Loup River 49420 Nebraska (a) Dismal River 49421 Nebraska 3. North Loup River 49430 Nebraska (a) Calanius River 49431. Nebraska 4. Cedar River 49440 Nebraska a. Elkhorn River 49500 Nebraska 1. Logan Creek 49510 Nebraska 2. Maple Creek 49520 Nebraska f. Salt Creek 49600 Nebraska 1. Wahoo Creek 49610 Nebraska Nishnabotna River 51000 Iowa, Missouri a. East Nishnabotna 51100 Iowa Little Nemaha River 52000 Nebraska Nemaha River 53000 Missouri, Kansas, Nebraska Tarkio River 54000 Iowa, Missouri Nodaway River 55000 Iowa, Missouri 107 ------- TABLE E-1 (Continued) River Code Tributary Platte River 56000 Iowa, Missouri a. One Hundred and Two River 56100 Iowa, Missouri Kansas River 57000 Colorado, Nebraska, Kansas a. Republican River 57100 Colorado, Nebraska, Kansas 1. North Republican River 57110 Colorado, Nebraska, Kansas (a) Arikaree River 57111 Colorado, Nebraska 2. South Republican River 57120 Colorado, Kansas 3. Frenchman Creek 57130 Colorado, Nebraska (a) Stinking Water Creek 57131 Colorado, Nebraska 4. Redwillow Creek 57140 Nebraska 5. Medicine Creek 57150 Nebraska 6. Sappa River 57160 Colorado, Nebraska Kansas (a) North Fork Sappa River 57161 Kansas (b) South Fork Sappa River 57162 Kansas (c) Beaver Creek 57163 Colorado, Nebraska, Kansas 7. Prairie Dog Creek 57170 Kansas, Nebraska 8. Buffalo Creek 57180 Kansas b. Smoky Hill River 57200 Colorado, Kansas 1. Beaver (Ladder) Creek 57210 Coloardo, Kansas 2. Hockberry Creek 57220 Kansas 3. Big Creek 57230 Kansas 4. Saline River 57240 Kansas (a) Paradise Creek 57241 Kansas 5. Soloinan River 57250 Kansas (a) North Fork Soloman River 57251 Kansas (b) South Fork Soloman River 57252 Kansas 6. Lyon Creek 57260 Kansas c. Big Blue River 57300 Nebraska, Kansas 1. Lincoln Creek 57310 Nebraska 2. West Fork, Big Flue 57320 Nebraska 3. Turkey Creek 57330 Nebraska 4. Little Blue River 57340 Nebraska, Kansas 108 ------- TABLE E-l (Concluded) River Code Tribut y d. Delaware River 57400 Kansas e. Wakarusa River 57500 Kansas Grand River 58000 Iowa, Mis,souri a. Thompson River 58100 Iowa, Missouri Chariton River 59000 Iowa, Missouri Lamine River 61000 Missouri a. Blackwater River 61100 Missouri Moreau River 62000 Missouri Marias de Cygnes-Osage River 63000 Kansas, Missouri a. Little Osage River 63100 Kansas, Missouri 1. Marmaton River 63110 Kansas, Missouri b. Sac Riuer 63200 Missouri c. Poitune de Terre River 63300 Missouri d. South Grand River 63400 Missouri e. Niangua River 63500 Missouri Gasconade River 64000 Missouri 109 ------- No Page 110 ------- APPENDIX F MAPS SHOW INC COUNTY - WATERSHED RELATIONSHIPS FOR SUBBASINS 31 THROUGH 42 111 ------- Figure F-i - Subbasin 31 112 ------- NEBRASKA KANSAS 1 - ARK N A$-WHtTE-RED DRAIN.thF AflEA • tE}!H Li -1 - NEBRAS KANSAS YAP Figure F-2 - Subbasin 32 ------- p 1 S t Figure F-3 - Subbasin 33 \ I \ I - ’ ------- /1 F 4 gure F-4 - Subbasin 34 4 Q a ------- IOWA !M ISSOIJRI a’ 33 3’ Figure F-5 - Subbasin 35 ------- w r, ‘UNCI MAt 28 irnumE —- -= .$ Figure F-6 - Subbasin 36 117 MAP UPPER M12 1SS1PPI DRAINAGE AREA YRLOW M DICIN( ------- / SI I - / - — -- / fz - / L / • t : ‘ / ( - > . , 3 / •‘ / / I / ¼ \/ / %l. ‘p / - - % .: i’ . .1. 5 S - .5 .s ... -. S .,S - - / // Figure F-7 - Subbasi 37 ------- - I Figure F-8 - Subbasin 38 ------- — - — — - - - — — — — A ’ r \ i ’ __1 _ 2 • L L\ ;) 4-,, ___ .,.I ..,.,. •,,S 1 1 • I 1 _. — — \ -, I ‘r s&. : ‘ r — S.., \ (S / - : ,t, - : :. , / ( 1 I J •JS ; S); 0 ‘ H ‘- 1( , 00 i :. . l v Si’ -j’ I ‘ 4 ’ — - . .. ‘ . . - D(E L • 5., i •. .‘‘ • , \ ‘1 \ 1; L • bi • E. — - - __ L , v u —- I L - v’ ‘‘ 1 .. . R’ ‘ - . N I / /N’ S I . Q ‘‘ •• c’ ,: ‘I I . . . . \ I I — “ Ti’ ’ _:_ ‘ ‘ r .N i.., -, - _I 1’ § • L_ ,. Figure F-9 - Subbasin 39 120 ------- IC 1 I - ‘ . - : cY\ R 1 - I - \ \ - - ‘a —. ••__•* i? ’ - ) ‘ --‘— • ‘ )t ’ : - - .— ::. 1 ; — Figur F-1O - Subbasin 40 - - -/ - - - ------- \ — -r ) 4 A / — I “ i $4jV I OC ‘ 1\• \ f \.“ _) ‘ s . : ‘\ -% 1’ ‘ - \ V •‘“ - 1 I t. ‘L - ___ -- • Figure F-il - Subbasin 41 122 ------- \ AP ‘ 40 Figure F-12 - SubbaBin 42 123 L.4p / / ------- |