Grazing Land Management and Water Quality

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Grazing Land Management and Water Quality In generally management of grazing lands requires fewer chemical inputs such as fertilizers and herbicides. However, grazing lands account for a larger land surface than cropland Therefore, there impacts on water quality must be considered

Grazing Land Management and Water Quality Traditional grazing management is generally less problematic No supplemental fertilizers Few pesticides However, the distribution of manure and soil disturbance can be problematic Traffic and defecation near and/or in stream channels is a significant source of nutrient and sediment pollution

Grazing Land Management and Water Quality Commercial/intensive grazing systems can have problems similar to cropland if not properly managed. In addition to traffic and defecation in stream channels Excess nutrient applications can cause Nutrient stratification and loss of soluble nutrients

Grazing and Conservation Buffers Filter strips and grass buffers placed down slope from cropland are effective conservation tools to reduce transport of pollutants to surface waters Effectiveness of buffers is a function of its height, density and age of vegetation Grazing and/or haying is generally prohibited by NRCS Programs Buffers can be managed to improve wildlife habitat to offset decreased grazing/crop prodution potential

Grasslands and Bioenergy Production Lignocellulosic biomass can be used for direct generation of energy through combustion Current technologies are also capable of producing ethanol from lignocellulosic biomass The real question: Can bioenergy outbid animal production for the biomass???

Grasslands and Bioenergy Production Biofuel produced from grasses can be carbon negative Will take up more CO2 from the atmosphere than what is released during the production cycle. When new stands of permanent grass such as switchgrass are planted on planted on previously cultivated soils the net decrease in CO 2 emitted is even greater due to soil carbon sequestration

Grasslands and Bioenergy Production It is often stated that grasses can be grown on marginal lands for bioenergy This has come under question in the past few years. Economics may not work out Yields must be high enough to pay for harvest and transportation costs

Grasslands and Bioenergy Production Utilizing CRP lands for Bioenergy CRP lands are highly erodible Many CRP lands have very low productivity Those that are erodible yet productive could be economically viable options for bioenergy This could reduce the cost of CRP program and maintain permanent cover Of course grazing could accomplish this if properly managed

Grazing Methods There are a variety of grazing methods Optimum grazing methods are dependent on: Climate Species composition of the pasture Need for additional ecosystems services Wildlife habitat Recreational value of rangeland is in many cases greater than value for grazing

Examples of Grazing Method Continuous grazing: Unlimited access for an unlimited time Can adversely impact soils if stocking rate is to high for droughty periods. Mixed grazing: Two or more animal species grazing the same field. Can provide better utilization of forage because species will differ in their forage selection

Examples of Grazing Method Rotational grazing: Animals are moved from one paddock to another in systematic intervals Intermittent grazing: Moving animals from one paddock to another in nonsystematic intervals Non-continuous grazing systems have in the past been thought to decrease potential for overgrazing and soil deterioration However, Stocking rate is much more important

Stocking Rate In native systems stocking rate is dependent on rainfall and species composition A base stocking rate that is 75% of the average carrying capacity of the field will provide resilience against drought Prevents overgrazing and/or need to sell animals due to lack of forage In average or above average years additional animals can be purchased to take advantage of excess forage

Stocking Rates In introduced grass systems both rainfall and nitrogen availability dictate stocking rates. Again base stocking rates should be set to ~75% of average carrying capacity In average or above average years hay production in addition to grazing is a option Nitrogen as well as other deficient nutrients must be applied to realize production potential Nitrogen deficiencies can result in overgrazing

Benefits of Grazing Moderate grazing is beneficial to ecosystems services: It increased net productivity by removing excess biomass It can increase species diversity by limiting the growth of dominate species It aids in nutrient cycling It efficiently produces animal protein for human consumption