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Ref.Page No. M2009-006 00094 <br /> Custom Soil Resource Report <br /> to separate the landscape into landforms or landform segments that have similar use and <br /> management requirements. Each map unit is defined by a unique combination of soil <br /> components and/or miscellaneous areas in predictable proportions. Some components may <br /> be highly contrasting to the other components of the map unit. The presence of minor <br /> components in a map unit in no way diminishes the usefulness or accuracy of the data. The <br /> delineation of such landforms and landform segments on the map provides sufficient <br /> information for the development of resource plans. If intensive use of small areas is planned, <br /> onsite investigation is needed to define and locate the soils and miscellaneous areas. <br /> Soil scientists make many field observations in the process of producing a soil map. The <br /> frequency of observation is dependent upon several factors, including scale of mapping, <br /> intensity of mapping, design of map units, complexity of the landscape, and experience of <br /> the soil scientist. Observations are made to test and refine the soil-landscape model and <br /> predictions and to verify the classification of the soils at specific locations. Once the soil- <br /> landscape model is refined, a significantly smaller number of measurements of individual <br /> soil properties are made and recorded. <br /> These measurements may include field measurements, such as those for color, depth to <br /> bedrock, and texture, and laboratory measurements, such as those for content of sand, silt, <br /> clay, salt, and other components. Properties of each soil typically vary from one point to <br /> another across the landscape. <br /> Observations for map unit components are aggregated to develop ranges of characteristics <br /> for the components. The aggregated values are presented. Direct measurements do not <br /> exist for every property presented for every map unit component.Values for some properties <br /> are estimated from combinations of other properties. <br /> While a soil survey is in progress, samples of some of the soils in the area generally are <br /> collected for laboratory analyses and for engineering tests. Soil scientists interpret the data <br /> from these analyses and tests as well as the field-observed characteristics and the soil <br /> properties to determine the expected behavior of the soils under different uses. <br /> Interpretations for all of the soils are field tested through observation of the soils in different <br /> uses and under different levels of management. Some interpretations are modified to fit local <br /> conditions, and some new interpretations are developed to meet local needs. Data are <br /> assembled from other sources, such as research intonation, production records, and field <br /> experience of specialists. For example, data on crop yields under defined levels of <br /> management are assembled from farm records and from field or plot experiments on the <br /> same kinds of soil. <br /> Predictions about soil behavior are based not only on soil properties but also on such <br /> variables as climate and biological activity. Soil conditions are predictable over long periods <br /> of time, but they are not predictable from year to year. For example, soil scientists can <br /> predict with a fairly high degree of accuracy that a given soil will have a high water table <br /> within certain depths in most years, but they cannot predict that a high water table will always <br /> be at a specific level in the soil on a specific date. <br /> After soil scientists located and identified the significant natural bodies of soil in the survey <br /> area, they drew the boundaries of these bodies on aerial photographs and identified each <br /> as a specific map unit. Aerial photographs show trees, buildings, fields, roads, and rivers, <br /> all of which help in locating boundaries accurately. <br />