Native warm-season grasses play a crucial role in abandoned mine land (AML) reclamation. They have greater tolerance of acidic, droughty and low fertility soils than do most introduced, cool-season grasses. Native warm-season grasses produce excellent forage if managed correctly on good reclamation sites and provide excellent wildlife habitat on all AML sites. Native warm-season grasses are long-lived once established and managed correctly. Trees can quickly invade native warm-season grass stands without the use of fire. Improper haying or grazing practices can quickly destroy a stand of native warm-season grasses.
A significant problem with native warm-season grasses is that establishment is slow and the seeds are difficult to plant due to their hairy or bearded seed coats. They require special planting equipment to handle the bearded seeds and plant them at the appropriate depth with proper seed-to-soil contact. Native warm-season grasses initially grow downward, building an extensive root system that enables the plants to survive harsh, dry soil conditions so common on the prairie during August and September. Shoot growth is minimal during the first two years, giving the appearance that the stand has failed. Native warm-season grasses appear small and weak in the first year, but by the third year they develop into robust, mature plants. Once the root system is established, native warm-season grasses can endure severe drought, low nutrient levels and acidic minespoils. Patience is necessary in establishing native grasses. The Missouri Department of Conservation and the Natural Resource Conservation Service provides publications and assistance to help landowners and managers identify native grasses.
Green Manure Crops
The best method to establish native warm-season grasses includes planting green manure crops in the minesoil for several growing seasons prior to planting native warm-season grasses. Green manure crops are plantings of quickly established, fast-growing cereal grasses and legumes that are turned into the soil while they are green, hence green manure. This is an old agricultural practice used to improve the soil’s tilth, infiltration rate and water-holding capacity. Incorporating legumes into the mix adds nitrogen, which promotes the development of a soil biological system, resulting in improved nutrient cycling. Multiple seasons of green manure crops increase the length of time that beneficial soil microbes and fungi have to colonize a reclamation site. This may be especially important because it may take five to seven years for mycorrihzae to colonize a drastically disturbed site.
Native warm-season grasses and forbs should be planted in the spring. Native warm-season grass seed planted in the fall may germinate during an Indian summer, making the immature seedlings susceptible to frost heaving and winter kill. Native warm-season grasses can be frost-seeded in winter, but erosion may remove seed from an unprotected site. The site can be protected from erosion by planting a green manure crop of cereal grasses and legumes. Cereal grain grasses should be mowed before their seeds ripen to limit self-seeding.
Heavy mulch may be applied to protect the site from erosion. The mulch can be native prairie hay or cereal straw free of weed seed or cool-season grass seed such as fescue. Old hay that is unfit for livestock may be used because the goals are site protection and the incorporation of organic matter. Do not apply and incorporate more than five tons of mulch per acre per year.
A summer-planted green manure crop of milo, corn or sorghum-sudan grass, planted with a legume like common lespedeza, soybeans or hairy vetch, can be useful in protecting the reclamation site from summer storms. This should be turned into the soil in late summer and a second green manure crop of wheat and a legume planted. In this fashion, two green manure crops can be worked into the reclamation soil prior to planting native warm-season grasses.
In the spring before the planting, the green manure crop or mulch must be turned into the soil by discing to increase the organic matter content. Soil tests should be taken and the soil topdressed at the time of discing. Never should more than 30 pounds of nitrogen per acre be applied for native warm-season grass establishment, regardless of soil test recommendations. Excess nitrogen stimulates weedy competition.
Native grasses can be directly no-till drilled into wheat stands later in the spring. However, there is a risk that the wheat could out compete the native warm-season grass seedlings for water and sunlight. Mowing before the seed heads ripen may be necessary to limit the wheat reseeding itself.
The seed should be purchased from a certified seed dealer and free of noxious weeds. Native warm season grass must be purchased on a pure live seed basis. Pure live seed equals the purity of the seed times the germination and firm seed percentage and makes sure the seed is viable and of high quality. Seed should be stratified for immediate germination upon planting. The seed dealer must certify seed purity and that the seed is free of contamination by old world bluestems. The addition of prairie forbs to the seed mixture provides structural diversity and multiple sources of food for wildlife. Forbs are not purchased on a PLS basis. Forb seeds can be expensive and the reclamation budget may limit the number of species in the mixtures. Debearded big bluestem and Indiangrass seed is available but costs 20 to 25% more than bearded seed. A traditional grass drill can be used to plant debearded seed.
The seedbed should be firm. Cultipacking may be required in loose, sandy or dry soils. The seed in the drill hoppers must be thoroughly mixed to be sure adequate distribution of seed will result in the proper stand diversity. A specifically designed native-grass seed drill is far and away the best tool to establish a successful and diverse stand. Grain drills or cool-season grass drills “adapted” to planting natives perform poorly. The Missouri Department of Conservation, the USDA Natural Resource Conservation Service and local soil and water conservation districts can assist landowners in locating native grass seed drills.
Good seed-to-soil contact and proper planting depth are necessary for native warm-season grass seed germination and development. The seed should be placed no deeper than one-quarter (1/4) inch (controlled by depth bands) and pressed firmly into the soil by press wheels. If the seed is deeper than ¼ inch, the seed leaves may be able to penetrate through the soil surface. Gamagrass can be seeded up to one inch in depth. Expensive native warm-season grass and forb seed is wasted if improperly planted. Cutting corners with poor quality seed or using inferior planting methods is bad management and will greatly increase costs to the landowner or manager.
Native warm-season grass planting on minesoils should be completed between March 15 and May 30. Planting after May 31 increases the risk that inadequate summer rainfall will result in excessive seedling mortality. This is especially true for droughty, AML mine spoils. Late planted seedlings with poorly developed root systems can be lost to winterkill or frost-heaving.
A successful first-year reclamation planting should have a minimum of one native warm-season grass plant per square foot by Sept. 1. If this density is not present, the weak areas should be reseeded the following spring. Wheat or mulch can be used on the bare areas for temporary overwinter protection. When direct, or no-till seeding, it is important to use a seed drill with a trash rack or blade that cuts straw or mulch rather than pressing it into the soil. Crimped organic litter (trash) and straw acts like a wick, drawing moisture away from the seedbed and the germinating seed.
The warm-season grass stand will look very weak, perhaps weedy, in the first season. Do not be discouraged by this appearance. It takes only one native warm-season grass plant per square foot to grow into a closed canopy in three years. Warm-season grasses expend most of their energy developing rhizomes and growing roots deep within the soil during the first two years. The soil protects the roots and rhizomes from sudden environmental change on the harsh prairie. A six-inch-tall big bluestem seedling may have a four-foot-deep root system extending over an area of one foot in diameter. There may be only a few leaves scattered in small clumps. The ground may be mostly barren, but roots and rhizomes are extensive in the first year, making the site far more resistant to erosion than a casual observer would suspect. The thick, extensive woody roots and rhizomes of native warm-season grasses and forbs are adaptations to Missouri’s periodic droughts. As with oaks or hickories, survival under these conditions forces plants to develop extensive root systems and a physiology that places a premium on drought and low-nutrient tolerances. These conditions are common on drastically disturbed lands. Rhizomes enable native warm-season grasses to spread following drought. Unlike the shoots that die every year, the roots and rhizomes are the perennial living parts of prairie plants.
Perennial ryegrass is a short-lived, cool-season grass that plays a significant role in early establishment of the native warm-season grass stand. It is quickly established following seeding. The result is a closed ground cover for both aesthetics and erosion control. Perennial ryegrass planted at a low rate (never more than three pounds PLS/acre) is not overly competitive, allowing the native grass to germinate and grow through and above the shorter perennial ryegrass. Perennial ryegrass will persist only two to three seasons. Thus, when the ryegrass is dying out in the third year, the native grasses should experience rapid shoot growth.
Reclaimed mine soils rarely have a large weed seedbank, and therefore weeds usually do not threaten native warm-season grass establishment during the first season. Ragweed, cocklebur and other tall weeds can shade out native warm-season grass seedlings. By the second growing season, more weeds will invade the mine site, but the native warm-season grasses should not be greatly affected. Annual weeds can be mowed in May of the second growing season if it appears the weeds are excessive. The mower should be set at 12 inches to miss the grasses and forbs. The site must be protected from grazing during the second year because the native warm-season grasses are still developing their root systems. The site should not be hayed the second year because that can inhibit root and shoot growth the next season. Mowing and grazing reduces photosynthesis, which in turn reduces the production of carbohydrates. Native warm-season grasses must be allowed to recharge their carbohydrate reserves to prepare for winter and to grow well the following season.
In the spring of the third year, the warm-season grass stand can be burned by the landowner or manager to promote maximum shoot growth. Burning releases some nutrients in the ash and allows sunshine to warm the soil and begin new growth earlier in the spring. Burning also promotes development and flowering of the prairie forbs, enhancing diversity and the beauty of the stand. Burning greatly improves wildlife habitat. Technical assistance in planning the burn can be obtained from the local Natural Resource Conservation Service office, local extension offices, the Soil and Water Conservation District and state wildlife conservation agencies. The site can be lightly grazed or hayed in the third year if the stand is robust and thriving. However, cattle should not be allowed to graze, nor should the grass be cut for hay after August in the third year. This will allow native warm-season grasses to replenish carbohydrate reserves for the next growing season. Removing organic matter in the third year will retard the natural reclamation process and will slow the closure of the native warm-season grass stand.
Managing warm-season, native grasses for Wildlife
Burning plays a major role in maintaining a native warm-season grass stand and promoting wildlife habitat. Burning removes thatch and dead plant litter. This warms the soil more quickly in the spring and promotes the growth and development of prairie forbs. Many important legumes need fire to create conditions for regeneration by seed. Legumes and forbs are high-quality food sources for wildlife. Illinois bundleflower, partridge pea, common lespedeza and compass plant support a great many insects that in turn are consumed by other wildlife.
Native grasses provide excellent canopies for young animals to feed and take cover under. Cold, wet summer mornings can be fatal to quail or turkey chicks. Native grass stands can have enough open areas for the chicks to sun themselves during such weather.
Native warm-season grass stands promote natural succession on mine sites. Native grass stands are susceptible to woody plant invasion without fire. Trees and shrubs find niches of bare soil in the open, native grass stands to grow and develop. Cool-season grasses tend to form thick, thatchy sods that inhibit natural succession and woody invasion.
Managing warm-season, native grass for hay
Hay cutting of warm-season, native grass on reclaimed minelands should be delayed until the third growing season. Hay should be cut no shorter than 8 to 12 inches, and no later than Aug. 1. This is to ensure adequate carbohydrate reserves for overwintering. Gamagrass should be cut no closer than 6 to 8 inches, no later than 60 days before the first hard frost.
Native grasses typically do not require large amounts of fertilizer to maintain hay yields. Periodic liming and fertilizing to soil test is important in maintaining the stand and hay yields. The University of Missouri Extension Centers can provide assistance in soil testing and analysis.
Improper or poor management can weaken a native grass stand and allow undesirable species to invade the site. The manager must remember that removing hay reduces photosynthesis and may deplete the carbohydrate reserves necessary for good winter hardiness and successful spring green-up. Hay removal must be seen as a balancing act between productivity and native grass sustainability. For further information, contact the local U.S. Department of Agriculture Natural Resource Conservation Service Center.
Grazing warm-season, native grass
Grazing on reclaimed minesites can be extremely dangerous to native warm-season grass maintenance and productivity. Native warm-season grasses should be grazed quickly, leaving 12 inches of stubble no later than Sept. 1 to replenish carbohydrate reserves. Animals should be removed if the soil becomes too wet in mid-summer.
Reclaimed minelands are not as productive as most native soils. Excessive grazing can quickly destroy a good stand of native warm-season grasses. Wildlife carrying capacity, including ground-nesting bird habitat, is quickly reduced. Grazing is a balancing act between productivity and native grass sustainability. Managers must closely monitor grazing of native warm-season grass on reclaimed sites or face complete stand failure. This could result in erosion and exposure of acid-forming materials, causing environmental degradation. For further information, contact the local USDA Natural Resources Conservation Service Center.
Old World Bluestems (OWB)
Old World Bluestems (OWB), such as caucasian or King Ranch bluestem, should not be planted. OWBs are aggressive and force out more desirable native species. Once a prairie or native warm-season grass stand is contaminated, the only way to remove OWBs is to kill the entire stand or prairie, which is unacceptable.
Missouri Department of Natural Resources, Missouri Department of Conservation and U.S. Department of Agriculture’s Natural Resource Conservation Service staff can discuss with the landowner the particular requirements to establish and manage native grasses on reclaimed minelands. Patience must be emphasized, especially in the first growing season when the native warm-season grasses are small. The landowner must be aware of the unique management requirements, including prescribed burns and closely managed grazing and haying of native warm-season grasses. If the landowner is unwilling to manage the native warm-season grasses as required, then it makes no sense to go to the trouble and expense to plant them. Most failures result from bad management. (For a discussion of native warm-season grasses and reclamation, see Warm-Season, Native Grasses on Reclaimed Minelands - Landowner Management Guide - PUB2082.)
Nothing in this document may be used to implement any enforcement action or levy any penalty unless promulgated by rule under chapter 536 or authorized by statute.