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(Key Words: Nitrate, Sorghum Forage, Millet.) Annual forage crops like sorghums and small grains make valuable contributions to profitable beef production in Oklahoma. They are well adapted, very productive and provide high quality forage. Infrequently, some of these plants accumulate toxins that can result in costly livestock losses. Nitrate is the primary nutrient form of nitrogen in most soils and is a normal constituent of plants. Normally nitrate is assimilated so rapidly following uptake from soil that its concentration in plant tissues is low. Occasionally, excessive levels occur in plants. The most notorious accumulators of nitrate in Oklahoma are the sorghums. Other annuals that less frequently accumulate nitrate are small grains (wheat, oats, rye and barley). Some perennial grasses (bermudagrass, fescue and johnsongrass) and certain weeds (pigweed, mustard, nightshade and lamb's quarters) also can contain dangerous levels. Accumulation is usually triggered by some environmental stress, where plant growth is restricted but absorption of nitrate from soil continues. The most common stress of summer annuals is drought. Lack of moisture, together with excessive soil nitrogen for existing growing conditions, is a frequent cause of toxic levels of nitrate in sorghums. Other stress factors which favor buildup are reduced sunlight from cloudiness or shading, frost, certain herbicides including 2,4-D, acid soils, low growing temperatures, and deficiencies of essential nutrients like phosphorus and sulfur. When more soil nitrogen is present than needed for maximum growth, some plants tend to accumulate nitrate even without environmental stress. This response is particularly true with hardy soil feeders like sorghums, noted for "luxury consumption" of certain nutrients. When accumulation occurs, the concentration of nitrate in plant parts is greater in stems than leaves. Seeds seldom contain significant amounts. Rate of uptake diminishes with increasing maturity; thus mature plants usually contain less nitrate than immature ones. Differences in potential for accumulation exist among species and varieties. The level of nitrate that causes toxicity in ruminants varies depending on rate of intake, diet, acclimation to nitrate and nutritional and reproductive status. As a rule, forage containing less than 6,000 ppm nitrate on a dry matter basis is safe for non-breeding cattle. Forage containing 6,000 to 10,000 ppm nitrate is considered potentially toxic when provided as the only feed. Forage containing over 10,000 ppm nitrate is considered dangerous but often can be fed safely after proper dilution with other feeds. Some diagnostic laboratories are even more conservative and suggest that 9000 ppm nitrate can be lethal. Questions among cattle producers and hay growers about the potential nitrate accumulation in various forages caused the following experiment to be conducted and reported. Two or three cuttings were made at each location each year. In the second year, very heavy rains at the Eastern Station forced the re-planting of the plots in late June rather than the late May plantings at the other locations. The very hot dry months of July and August then produced heat and drought stress on the plants at that location. The very high concentrations of nitrate in the first cutting of 1991 at the Eastern Station apparently were the result of those weather conditions. Data from the hay samples of the first cutting at the South-Central station in 1991 were not available. A statistically significant two-way forage type by location interaction meant that we should look at each location each year to study the differences in nitrate accumulation among the four forage types. Table 1 illustrates the mean concentration of nitrates in parts per million (100% dry matter) for each forage type. Pearl Millets had greater mean concentrations of nitrate at all locations. The magnitude of difference was greater when all plants were stressed and each forage type had increased nitrate content. The relationship between yield per acre and nitrate content was very small. The partial correlation was r = .08. Chi-square analysis was used to determine if differences in the frequency of "dangerous" (>10000 ppm) samples were significant. A greater proportion of the Pearl Millet samples was found to be in the "dangerous" category than other forage types. See Table 2. The OSU Current Reports 2112 for 1990 and 1991 list the varieties, yield data, and rainfall totals by month at each of the experiment stations. No difference in nitrate concentration was found among the other three forage types. There was no difference in nitrate concentrations of individual varieties within each forage type. These results agree closely with an earlier, and much smaller study from two different research stations in central Oklahoma (Lemon and McMurphy, 1984). Nitrate accumulated in Pearl Millets in greater concentrations than Sorghum x Sudan hybrids, Sorgo x Sudan hybrids, or Sudan x Sudan hybrids. Table 1. Least squares means and standard error of means for nitrate concentration in ppm for four types at three locations. Location Forage type Eastern South-Central Southwest Sorghum x Sudan 7794 ± 285 3306 ± 380 7048 ± 317 Sorgo x Sudan 7369 ± 344 3233 ± 435 6739 ± 380 Sudan x Sudan 8150 ± 553 3360 ± 660 7204 ± 597 Pearl Millet 13911 ± 474 6552 ± 635 10311 ± 536 Table 2. Proportion of samples that exceeded 10000 ppm nitrate among the four forage types. Forage type
Proportion of samples
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