Farmers installed permanent high-tensile fencing around the edge of their farms, while they obtained mobile electrified fencing to avoid the animals from escaping into neighboring crop fields, and to facilitate Management Intensive Grazing (MIG). MIG involved daily moves of the animals, where the animals are allowed to consume only a portion of the standing biomass, while the remainder is left standing to either regrow or as mulch for the following crop to favor soil health improvement. The cover crops were often grazed more than once, in which case a sufficient rest period was included after each grazing event, allowing the soil to recuperate from the grazing impact, and the cover crop to regrow until it was ready for repeat grazing. Buried water pipes were installed to bring water to the edge of the field, while above-ground flexible water pipes with quick connects were used to bring water to the paddocks that changed every day. The farmers spent about 20 minutes every day to move the animals, some of which were purchased specifically for this project.
The researchers went out about 2-3 weeks after farmers started grazing a cover crop field to measure standing and post-grazing cover crop biomass, and soil health before, the day after, and 2-3 weeks after grazing. Soil health parameters measured were water infiltration rate, soil bulk density, aggregate stability, organic matter, active soil carbon, and carbon-dioxide burst. The cover crops were planted after corn silage or after wheat harvest. Fall planted cover crop species after corn silage included triticale, wheat, annual ryegrass, hairy vetch, and crimson clover, while summer cover crops planted after wheat included pearl millet, sorghum-sudangrass, sunnhemp, sunflower, cowpea, radish, and forage rape. Many times, mixtures of these were planted together, increasing biodiversity.
We determined that soil health on all farms was excellent, and not affected by grazing. While we hoped for a positive effect of grazing, we were pleased to see that grazing did not lead to detrimental soil compaction. Further, the amount of consumed cover crop biomass varied from 1000-2300 lbs drymatter per acre per grazing. Depending on regrowth the farmers grazed 1-3 times. The farmers left always at least 50% of standing biomass for soil function and protection. We calculated the economics of grazing cover crops after corn silage for each farm, considering the investments in permanent and mobile fencing, buried and above-ground water systems, the labor needed to move the animals (at $20 per hour), and the value of the grazed biomass (at $190 per Ton). We assumed permanent fence and buried water had a lifespan of 40 yrs, mobile fencing 20 yrs, and above ground water 10 years, and used a 5% interest rate. We determined that net value of grazing varied from $48 to $233 per acre per year.
One big factor determining profit was the number of times the cover crop could be grazed, and the quantity of grazed biomass consumed. Further, the cost of exterior fence was another big factor – by fencing in a larger, regularly shaped area, the costs per acre could be reduced. Further, the amount of time spent moving the animals could also be a big cost which could be reduced primarily by having more animals in the herd or reducing travel time to the field. Altogether, the farmers were very pleased with their grazing cover crop experience and most are expanding the practice on their farms, while figuring out how to do it better. Another important finding was that the environmental functions of cover crops (such as its effects on soil health and water infiltration) can be preserved while grazing them, at least if done in permanent no-till and using Management Intensive Grazing practices.
Source : psu.edu