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Peer-Reviewed

Colorado Forage Guide

Ranch landscape in Colorado

Introduction

The number of small acreage properties continues to increase throughout Colorado. Owners of these properties have a variety of goals for use of their land, including wildlife habitat, enjoyment of open space, farming enterprises, livestock grazing, greenhouse crop production, forestry, and horticultural activities.

Colorado contains over 18 million acres of pastureland and rangeland in farms and ranches, representing the majority of the state’s agricultural land base according to the 2022 USDA Census of Agriculture. This land not only supports the crucial agricultural products of the state but also sustains important ecological services like wildlife habitat, watershed functions and rural economies.

Grasses thrive in Colorado because they are adapted to the state’s dry climate, drought cycles, grazing, and periodic fires. Their deep root systems allow them to efficiently use water, recover from disturbance, and dominate landscapes where many other plants struggle to survive.

Grazing has been central to Colorado agriculture since the late 1800s. Native grasslands that once supported bison now support cattle and sheep, making ranching one of the state’s most important agricultural industries. Grazing allows productive use of Colorado’s vast semi-arid rangelands, which are often better suited for livestock than crop production

With Colorado’s strong agricultural and ranching heritage, and a higher demand for food and fiber, many non-native grass species were introduced to increase forage production, extend grazing seasons, improve livestock nutrition, and provide reliable hay supplies for periods when fresh forage was limited. These species were often selected for their ability to establish quickly and remain productive in areas where degraded native grasses might require more time to become established.

Species such as crested wheatgrass were once considered an ideal solution for Colorado’s challenging conditions, including dry climates, cold winters, and hot summers. While these grasses have proven highly resilient, their widespread use has also contributed to reduced plant diversity in some pastures and rangelands. Today, maintaining or restoring species diversity is increasingly recognized as an important goal in regenerative grazing and rangeland management, as diverse plant communities can improve ecosystem resilience, soil health, wildlife habitat, and long-term forage productivity.

This publication was developed to help small-acreage landowners understand the fundamentals of livestock forage production and grazing management. It provides information on common forage grasses grown in Colorado, the role of legumes in pasture systems, and key considerations for establishing or renovating pastures.

Understanding how forage species grow, their seasonal growth patterns, appropriate grazing rotations, hay harvest timing, and site-specific species selection can help landowners provide high-quality forage for livestock while maintaining soil health and pasture productivity. Sound management practices also reduce the need for costly pasture renovation and reseeding, which are often the result of overgrazing or poor species selection.

This guide introduces the most common forage grasses used in Colorado, their adaptations and growth characteristics, and best management practices for pasture establishment and renovation. It also covers stocking rates, grazing strategies, and other essential considerations to help landowners develop productive, resilient, and sustainable pastures that provide long-term benefits for both livestock and the land.

Pasture Revegetation

Reseeding pastures can cost around $200-400 per acre (CSU Extension). Ensuring the process is done correctly will help avoid repeated costs, additionally, proper management once pasture is established will ensure the long-term sustainability of the seeded forages.

The first step in pasture revegetation is determining whether reseeding is truly necessary. In many cases, pasture productivity can be restored through improved grazing management rather than reestablishment. Overgrazing is a common cause of pasture and rangeland decline on small acreages, but if desirable forage species are still present, allowing adequate recovery time, reducing grazing pressure, controlling undesirable vegetation, and implementing a rotational grazing system that matches stocking rates to the land’s carrying capacity can often restore pasture health and vigor without the expense of reseeding. These grazing management practices are discussed in the Grazing Management chapter.

In addition to the high cost of reseeding, many grasses require multiple years to become fully established and grasses should not be grazed before they are established to prevent animals from uprooting young plants. Where reseeding is needed, selecting the right species for your site and intended land use, purchasing quality seed and preparing a good seedbed will result in successful and long-lived perennial pastures.

Efficient use of water is crucial for plant establishment. On irrigated sites, coordinating seeding with irrigation schedules will help maintain seedlings alive, while on dryland pastures dormant seeding during the winter or spring will give the best chances of success, although dryland reseedings often require second attempts due to the unpredictability of precipitation.

When seeding or reseeding a pasture, there are some driving variables that will determine what grows best in your area. It is important to evaluate and get familiar with those to better select the species that adapt to those areas rather than try to correct the site conditions through management. Those site considerations include soils, water or moisture availability and time of seeding.

Site considerations

Soils

The process of revegetating a pasture starts by analyzing the site environment, such as its topography, soils, and amount of water it receives. Soils are the foundation and nutrient source for plants, and some plant species are better adapted to specific soil textures. Knowing the type of soil texture in the area to be reseeded is a first step to selecting an adequate forage species. A soil map of your land can be created using the online NRCS Web Soil Survey located at websoilsurvey.nrcs.usda.gov.

Loamy soils are the most versatile texture for plants because they have a balance of sand, sil, and clay particles. Plant establishment on sandy soils can be difficult because they do not retain as much moisture as clays or loams. Clay soils are more susceptible to heavy compaction and plant establishment may require mechanical cultivation prior to seeding, however these soils have a great capacity to hold moisture.

Saline soils are found throughout the state of Colorado. Soil salt content is measured in millimhos per centimeter (mmhos/cm), decisimens per meter (dS/m) and parts per million (ppm), also found on a soil test as Electrical Conductivity (EC). Soil EC above 4.0 dS/m is considered saline and reduces seed germination and plant nutrient absorption. EC levels of 12 or greater will only support a few forage species. More information, consider reviewing the Saline Soils fact sheet.

Water availability

Forage species should also be selected based on how much water the site receives. Dryland species are needed for sites that receive only natural precipitation. A difference of only 2 inches of average annual precipitation is enough to change the species that will survive the best. For example, thickspike wheatgrass performs better in areas receiving 12 to 13 inches of moisture than its closely related cousin, western wheatgrass. Grass species options increase as precipitation rises above 14 inches per year, however, the palatability of the species and growth season also need to be considered.

Sites near rivers, creeks, canals or ponds are sub irrigated when underground water is within reach of plant roots. They can be more productive than dryland sites and should be seeded with forage species that take advantage of the extra available water.

For irrigated pastures, determine how much irrigation water is available. Pastures are short of water if one or two irrigations are made in the spring and no (or limited) water is available in the summer. Different species are recommended for short-water versus adequate-water situations. It is recommended to test the quality of irrigation water, as high salts and nitrates can limit plant growth.

Time of seeding

Dormant seeding is recommended for dryland fields. This approach places seed in the soil before the growing season so it can take advantage of any moisture as soon as it becomes available. The dormant-seeding window extends from November 15 to April 15, as long as the soil is not frozen. Planting before March 1 ensures seeds are already in place and ready to grow with early spring rains, helping landowners avoid the challenges of trying to seed on wet soil or between rainstorms.

Grasses break dormancy when soil temperature and moisture are favorable. Cool-season grasses will germinate and emerge in March or April. Warm-season grass seeds will lay dormant longer and germinate in May.

If irrigation water is available, forage seeds can be planted 6 to 8 weeks before the first hard freeze, generally late August to early September.

Buying seed

State and Federal laws require seed dealers to label all seed offered for sale. The label must list seed origin, purity, species identity, percent germination, and weed seed content. It also must list the seed lot number and the company or person responsible for label content.

As previously discussed, successful reseeding is rarely guaranteed in Colorado, especially because of the variability of moisture availability throughout the state. Buying good quality seed can help achieve better results. Local seed companies often provide a a wider variety of grass and legume species and cultivars, have better traceability of where their product comes from and can provide customized seed mixes or recommend you an adequate seed mix for your intended use and area.

Seed tag example
Fig 1. Seed tag example

Origin. All seed lots offered for sale in Colorado must have the state of origin listed on the seed tag or state if the origin is unknown. It must be stated on the tag if the origin of the seed is unknown. Seed with origin close to the location where it will be planted will be more adapted to the local conditions.

Purity. Is the percentage of desirable seed species in the bag. Purity % + inert matter% + weed seed %+ other crop seed % must add up to 100%. Inert matter includes small sticks and stems, chaff, and infertile flowers. Inter matter content over 15% makes the seeds difficult to plant, however, some native grasses like the bluestems, gramas and Indiangrass have higher inert matter percentage because they are hard to clean. Drills with seed-box agitators are recommended to plant these seeds.

Weed Seed. The label should indicate that no prohibited noxious weed seeds are present. For other weed seeds, Colorado Seed Law states that they cannot total more than 2% by weight.

Germination. Total viable seed includes the percentage of all seed that germinates in a lab analysis, plus the amount of hard and dormant seed. Species vary regarding the amount of hard and dormant seed, but dormant seeds are not undesirable; the higher the total germination, the better. Germination for most grass species should not be lower than 60%. Germination of chaffy seeds may be lower.

Species Identity. Forage seed is sold as Common, VNS (Variety Not Stated), or Certified. Certified seed is typically the most expensive, but it provides assurance that the stated variety is accurate. When certified seed is unavailable, verifiable seed varieties are a reliable alternative. Some VNS lots may also originate from high-quality blends of different verifiable varieties. If neither certified nor verifiable varieties are accessible, choosing seed with a known origin and proven adaptation to the intended planting area is a good alternative.

Estimating amount of seed needed: Pure live and bulk seed

Seed is sold and purchased on a Pure Live Seed (PLS) basis because of the differences in purity between seed lots and germination. PLS is calculated by multiplying seed purity by seed germination. Use the decimal representation of a percent (proportion) when calculating bulk seeding rates. In other words, 70% purity equals 0.70.

Planting based on PLS seeding rates ensures that the number of seeds planted on the ground matches the desired number of plants that have the potential to germinate and being growth. PLS factors out the dead seeds, weed seeds, and inert matter in seed lots that will not produce desired plants.

The PLS value should be used to determine the amount of bulk seed to purchase. Bulk seed is the retail product in seed bags. The bag’s weight includes that of PLS, dead seeds, weed seeds, and inert matter.

If you want to plant 5 PLS pounds per acre of a grass on 10 acres, first calculate the PLS for the seed lot. For example, the seed lot label (Figure 1) indicates that the seed purity is 66% and the germination is 97%.

PLS = 0.66 × 0.97 = 0.64 The PLS

To calculate pounds of bulk seed to buy and plant:

(PLS lb/acre) ÷ (PLS) = bulk lb/acre seeding rate

(5 PLS lb/acre) ÷ (0.64) = 7.8 bulk lb/acre

(7.8 bulk lb/acre) x (10 acres) = 78 lb total bulk seed

When using a grass drill, using about 5 more pounds of seed than needed might help push down seed through the seeding tubes as the box empties.

Solo and mixed seedings

Solo plantings (monocultures) or mixed seedings are good options that offer different benefits depending on the intended use and management of the land. Mixed seedings are more ecologically desirable because they offer stand diversity, more resistance to disease and insect problems and endure different extremes in climatic conditions. Mixtures can also make a more efficient use of available moisture, light and nutrients through the growing season.

Dryland and irrigated pasture seed mixes are often available on the retail market and through Conservation Districts. These mixes often contain combinations of native and introduced grasses, so careful observation should be done to ensure these pre-made mixes contain species that fulfill the intended uses and management of the property. Seed prices tend to be higher on orders of less than 50 pounds.

Mixed pastures can include various combinations of grasses and legumes. Mixing plants with different seasons of growth is generally not advised on small acreages. While these mixes can extend the grazing season of dryland pastures (less so on irrigated pastures), they are best seeded in separate pastures for ease of management. Cool season pastures, for example, can be used in spring and again in the fall (depending on moisture). Warm season pastures can be used in the summer while cool season grasses are dormant. However, these types of systems may not be suitable for small dryland parcels.

Mixed stands of cool- and warm-season grasses often become dominated by the cool-season species over time. Cool season grasses are often favored by winter and early spring moisture and nutrients, while warm season grasses remain dormant and use the leftover moisture in late spring or summer. Summer rains may be of little benefit as they are often inconsistent in timing and amount. Warm-season grasses will dominate if the cool-seasons are continually overgrazed in the spring.

Native and introduced species mixes are also challenging, since many introduced species tend to establish quicker than natives, creating an advantage of those over native grasses. Mixes of native species interact well and tend to complement each other. Simple mixes of three to four species for irrigated pastures are often recommended. In dryland sites, using a wider variety of species may be more suitable. This is especially true in sites where water tables, soil salt content and soil textures are variable. Each species will be established on the microsite to which they are better adapted. More details on warm season and cool season grass species and native and introduced species can be found in this guide.

Advantages of grass–legume mixtures are discussed in the “Legume” section of this publication. Legumes perform best when paired with shorter, less aggressive grasses. However, some legume species can cause bloat in cattle and sheep due to their rapid digestion. This fast breakdown releases gases quickly inside the rumen, which can become life-threatening if not properly managed.

To reduce the risk of bloat, the proportion of bloat-causing legumes such as alfalfa and clovers should not exceed 25% of the pasture composition. Careful attention should be given to managing legume–grass pastures, as livestock often prefer legumes and may overgraze them if not allowed adequate time for regrowth.

Mixed stands should have species similar in palatability (the degree of being desired by livestock), regrowth ability, time of maturity, and competitiveness. Livestock will favor and overgraze the more palatable species in unbalanced mixes. Balanced mixes foster optimum forage quality when harvested for hay.

Grass monocultures can be suitable in certain situations because they are easier to manage in terms of forage regrowth and maintain consistent palatability. Grasses such as pubescent wheatgrass, tall fescue, smooth brome, and crested wheatgrass are often best managed as monocultures. However, careful consideration is needed before planting these species, as they can spread beyond their intended area and become invasive or difficult to control. Despite this risk, they often provide high-quality forage and show strong resilience to drought and cold winters.

Species suggestion

A summary description of growth season and habits can be found on Appendix A. When deciding on a grass species consider the growth height and intended purpose of the pasture. Some grasses are optimal for hay cutting while some others are better suited for grazing. More characteristics of grasses and legumes can be found on Appendix B and C. The individual species descriptions in this publication also provides information on species that grow well together and their adaptability do different management scenarios.

Designing a seed mix

On customized seed mixes, seeding rate for each species needs to be calculated based on the PLS for each species and its weighted proportion in the mix. PLS may be different depending on the seed supplier and seeding rates vary within species, seeding method and location of the seeding. Additionally, considering the price of the species to be seeded can impact the percentage of that species to be used in a mix, and should be considered in addition to the desirable composition of the mix.

An example of a custom seed mix can be found below:

Desirable species and percentages:

  • 30% sideoats grama
  • 30% big bluestem and
  • 40% switchgrass

Step 1: Determine the PLS for each species (from seed tag)

A
Purity
B
Germination
C
PLS (A×B)
Sideoats grama 0.70 0.80 0.56
Big bluestem 0.60 0.80 0.48
Switchgrass 0.90 0.90 0.81

Step 2: Adjust the mix for PLS pounds per acre.

D
Desired Mix (%)
E
lb PLS/acre
(solo planted)
F
lb PLS/acre in mix
(D×E)
Sideoats grama 30 4.5 1.4
Big Bluestem 30 5.5 1.7
Switchgrass 40 3.0 1.2

Step 3: Adjust the mix for bulk pounds per acre.

F
lb PLS/acre
G
lb bulk seed/acre (F÷C)
Sideoats grama 1.4 2.5
Big bluestem 1.7 3.5
Switchgrass 1.2 1.5
Total bulk seeding rate in lb per acre (Sum of G)= 7.5

Other characteristics to consider for grass seeding

Bunch and sod-forming grasses

Perennial grasses can be classified by their growth habits into bunch grasses or sod-formers. Bunchgrasses grow in distinct clumps with upright, tufted growth and minimal lateral spread, and often leave small areas of bare soil between clumps. Sod-forming grasses spread horizontally through rhizomes or stolons creating a dense mat that fills in any gaps of bare ground.

Bunchgrasses typically have more leaves than sod-forming species. Many have leaves grouped near the plant base. They typically produce more forage than sod-formers but need more intensive grazing management to optimize productivity. For example, grass growth will be delayed if the growing points are defoliated, this is especially risky in the elongation phase of a bunch grass, when the seeds talks are developing. Some species raise their seed stalks earlier during the growing season than others. However, some bunchgrass species such as orchardgrass, perennial ryegrass, and meadow brome continually initiate new tillers, and their production is impacted little by defoliation.

Sod-forming grasses have underground stems, called rhizomes, which run parallel to the soil surface. Rhizomes form a sod that can tie the soil together, making these grasses a good option for erosion control. New above-ground shoots are sent up from nodes located along the rhizomes. These shoots tend to fill in and cover bare spots on the soil. Examples of sod-formers are Kentucky bluegrass, western wheatgrass, and smooth brome.

Pastures dominated by sod-formers are not as rough as those dominated by bunchgrasses. Sod-formers are typically less productive but often tolerate more grazing than bunchgrasses because they grow new shoots from rhizomes.

Rhizomes and roots of western wheatgrass
Fig 2. Rhizomes and roots of western wheatgrass
Warm- and cool-season grasses

We have referenced a plant’s growth season throughout this guide. Grasses can either be cool season or warm season, but either between those two kinds, some grasses being growth earlier or sooner in the season and that can play a key role in terms of grazing management.

Grasses that grow during spring and fall when temperatures are still cool are known as cool season grasses. Their growth and forage production peaks in the spring and fall and go dormant in the summer when temperatures starts rising. These plants are also known as C3 plants, which refers to its photosynthetic pathway, which relies on the enzyme Rubisco.

Rubisco binds oxygen, especially with warm temperatures, which causes the plant to enter photorespiration. This process reduces carbohydrate production in the plant, causing slow growth. C3 plants become less efficient at high temperatures and with low water availability they go dormant.

With insufficient irrigation, these grass species will look brown during the summer, however, with enough water they can remain green. This is the case with most lawn grasses, like Kentucky bluegrass, which under summer irrigation remain green and productive during the heat of the summer.

Warm season grasses being growth around mid-May (on a typical year), when soil temperatures reach 60°F. These grasses use the C4 pathway, which relies on the PEP carboxylase enzyme, which does not bind oxygen. This mechanism prevents photorespiration entirely, even under high heat.

Because of that pathway, C4 grasses are more efficient at fixing CO2, especially under high heat. They require more energy (carbohydrates) to function, but they store water more efficiently and maintain higher productivity in hot, dry conditions. They tend to be more drought tolerant than C3 grasses and can be a good option for water efficiency. Corn and Sorghum are examples of C4 annual grasses, buffalograss and blue grama are some native perennial warm season grasses.

Seasonal forage production distribution chart
Fig 3. Seasonal forage production distribution (Alabama Extension, 2022)
Native and introduced grasses

Native grasses evolved with the climate and soils of the area. They typically live longer than introduced species and require little maintenance. Because they have evolved with the soil types and characteristics of the region, they typically do not require supplemental fertilizers. Native grass seeds tend to have higher prices, some species are difficult to harvest and can make availability scarce on some years. They typically take three to four years to become bully established, grazing is not recommended until grasses are established.

Introduced grasses evolved outside of North America and were imported for their production potential and their ability for faster establishment. They respond better to fertilizer and irrigation than native grasses and seed costs can be lower. Introduced grasses may not have the longevity of native grasses and may require renovation more frequently.

Introduced grasses, brought into the United States in the late nineteenth century, became popular because of their adaptability to local growing conditions. They are often highly productive and quick to establish, but some species can aggressively colonize landscapes and displace other plants if not properly managed. In Colorado, brome hay is frequently assumed to be the standard when purchasing grass hay for livestock, as brome has been managed for hay production for generations. However, several native grass species can be equally productive and nutritious. For example, big bluestem can reach a crude protein content of 11–12% at harvest, comparable to smooth brome. Ultimately, choosing between native and introduced species depends on key factors such as soil type, irrigation availability, and intended use, each of which plays an important role in selecting the right grass for a pasture.

Legumes

Legumes are broadleaf plants or forbs, often high in protein. Some species form symbiotic relationships with bacteria that live in their nodules (or knots) located on their roots. These bacteria is called Rhizobia and can convert nitrogen from the air into plant available forms. This fixed nitrogen is provided to the legume, and another small portion becomes available to any grass growing in their proximity over time. Each legume requires a specific species and strain of Rhizobia for nodule formation. Inoculation with Rhizobia is often needed for some legumes to ensure nodulation.

Depending on the legume species, and soil moisture, legumes can increase forage production. Alfalfa is usually the top choice because it fixes the most nitrogen. Legumes can also produce more forage during the summer than cool season grasses and improve forage quality factors such as palatability, digestibility and nutrient content.

Plant varieties

When choosing seeds for pastures, either from grasses or legumes, and even other crops and ornamental plants, different varieties (also known as cultivars) may be available. These varieties have been specifically developed to enhance some of the properties of the plant like their adaptability, yield potential or aesthetic values. Each species listed on this guide provides a list of commonly available or planted varieties for this plant, although availability can change from one season to the other. Additionally, for some crops like alfalfa, many varieties are bred and developed every year to achieve market needs and address different challenges or conditions related to its production.

Crested wheatgrass monoculture
Crested wheatgrass tends to form monocultures with patches of bare ground between plants due to its bunch growing habit.

Plant Establishment

Weed management

A key step for pasture revegetation and maintenance is weed management. Sites that are dominated by weeds will be less productive and newly seeded grasses or legumes will struggle to establish because they have to compete against highly opportunistic invasive weeds.

An integrated weed management approach is the most effective and it involves incorporating a combination of mechanical, chemical, biological and cultural practices to mitigate and prevent weed infestations. For example, frequent mowing, combined with fall herbicide applications can be very effective against some perennial weeds like Canada thistle. After new forage is established, maintaining a healthy forage stand (not overgrazing) will help prevent weed re-infestations.

All commercial herbicides, either synthetic or organic contain a label with directions, best management practices, re-entry intervals and proper equipment and management instructions. Reading and following herbicide label instructions is the law.

The best methods and timing of control will depend on each weed’s lifecycle. Annual weeds germinate, grow and reproduce within one year or less and are best managed before seed production. Examples of annual weeds include kochia and Russian thistle. Biennial weeds are plants that survive through two years. They germinate and remain as a rosette during the first year and bold and produce flowers and seeds the second year. These should also be managed prior to seed production, mechanical removal of the rosette or herbicide applications are very effective during the first year of their lifecycle.

Perennial plants live for many years, and like many of the perennial grasses, they can store carbohydrates in their root systems, go dormant during the winter and/or summer and continue to grow and reproduce for many years if left unmanaged. Simple perennials reproduce by seeds only, however, there are creeping perennial plants that have the ability to reproduce through vegetative tissue. This is the case for field bindweed. Frequent defoliation through cutting or mowing can suppress these plants but complete control of these plants is difficult and often requires a combination of mechanical removal and herbicide applications for the course of many seasons.

Leafy spurge noxious weed
Fig 4. Leafy spurge is a List B noxious weed in Colorado.

The Colorado Noxious Weed Act is a legal document that classifies weeds by required management in different lists, based on their distribution and control efforts, ranging from mandatory eradication for rare species to recommended suppression for widespread species. Noxious weeds are designated as such because of their capacity to spread and their potential to harm ecosystems, agricultural land, private property and potential risks to the health of animals, ecosystems or people. Private and public landowners have a legal duty to control noxious weeds in their property. Counties and municipalities are empowered to enforce compliance.

Soil testing

Taking soil tests annually offers many benefits, whether you plan to fertilize existing pastures, reseed or overseed them. Nitrogen, phosphorus, and potassium are key nutrients that require close attention, as deficiencies can limit forage yields. However, excess levels of these and other nutrients can create water quality concerns. A soil analysis provides the exact amount of nutrients your plants need.

For an accurate soil test, collect at least 10 sub-samples from different areas of your field, mix them thoroughly in a clean bucket, and submit a pint-sized portion to a certified soil testing laboratory. The lab will include fertilizer recommendations with your results. Submit samples at least four weeks before seeding.

For dryland seeding, apply no more than 30 pounds per acre of nitrogen fertilizer; higher rates will only encourage annual weed growth. Adding phosphorus (20–80 pounds per acre) will improve seedling vigor and root development.

Seedbed preparation

Forages can be established in either clean-tilled or stubble-mulch seedbeds. Clean-tilled seedbeds are prepared by cultivating the soil with a sweep, chisel, disc, or plow. This approach offers several advantages, including improved seed-to-soil contact, more uniform stand establishment, reduced competition from existing vegetation, better incorporation of fertilizers and organic amendments, and more consistent drill depth and seed placement. On sites smaller than one acre, a power tiller may be a practical option for achieving similar results.

Clean tillage can leave susceptible soils vulnerable to erosion. Although it is not always economically feasible, incorporating well-rotted manure or compost into the soil can improve forage establishment and productivity. In sandy soils, organic amendments increase water-holding capacity and nutrient retention, while in clayey soils they improve soil structure, aeration, and drainage.

Plowed soils may need to be disced as a second operation. Smoothing and firming are accomplished with harrow, field cultivator, or roller/packer implements. The seedbed should be firm enough that a person’s footprint does not sink deeper than one-half inch. Clods should not be over 2 to 3 inches in size.

Stubble-mulch seedbeds are advised for dryland soils to reduce soil erosion. Plant stubble (standing plant stems) protects establishing forages by buffering wind, improving soil moisture, and decreasing soil temperature and weed competition. Planting on existing vegetation is a viable option. Annual crops, known as cover crops, can also be established and mowed, killed or harvested before seeding.

Sorghum and forage millet can be used as cover crops in areas at up to 7,000 ft in elevation. Sterile sorghum varieties can also be viable options. As they do not produce seeds at maturity. Cereal crops, such as oats, are a good option at elevations above 7,000 feet.

Sorghum and forage millet can be planted from late May through June 30, before grass seed planting in the fall. Sorghum can be seeded at a rates of 4 to 8 lb/acre. The lower rates are recommended for clay soils in dryer conditions, while 8 lb/acre can be seeded on irrigated sites. Forage millet can be seeded at rates of 25 to 30 lb/acre on irrigated land and 8 to 10 lb/acre on dryland.

Sorghum should be seeded at 1 to 1 ½ inches deep using a seed drill, and forage millet can be seeded at ¾ to 1 inch deep. These species can be cut for hay in late summer or early fall, leaving a 6 to 10 inch stubble height. Taller stubble heights may be needed on sandy soils.

Grass seeding methods

Forages can be seeded using a drill or broadcasting seed across the soil surface. Drilling is the recommended method for grass seeding and is essential for planting into stubble mulches. Drills with a seed box agitator for fluffy seeds, double-disc openers, depth bands, and packer wheels are the best choice for grass seedings. Small-seeded legumes can also be seeded with a drill, but seeds need to be placed separate from grass seeds to adjust the flow rates appropriately.

Drills allow proper seeding depth, good seed-to-soil contact, and protection of seed from climatic extremes and wildlife predation. If the drill does not have packer wheels, roll or drag the field after planting to increase seed-to-soil contact.

Large-seeded grasses should be planted to a ½ inch depth, small-seeded legumes at ¼ inch depth on loam or clay soils or ½ to 1 inch depth on sands. Coated alfalfa seed performs well at ½ inch depth on sands.

Rows should be 7 to 12 inches apart. Cross-seeding pastures may give pastures a more appealing look when seeding bunchgrasses only. Plant 50% of the seeds in each direction.

Broadcast seeding can be done with an agricultural seeder, a whirl seeder, or by hand. For larger areas, an agricultural seeder such as a Brillion is an effective tractor-drawn implement for establishing grasses and legumes. It drops seed from its boxes onto the soil surface and then presses it in with trailing rollers to ensure good seed-to-soil contact. Brillions work well on clean-tilled seedbeds, but they are generally not accessible to most small acreage owners.

A whirl seeder is a small, hand-powered and inexpensive spreader commonly used for short-distance applications such as grass seed, fertilizer, or ice melt, typically reaching up to five feet. After seed is broadcasted whether by hand or with a whirl seeder, it should be covered by pulling drags, pipes, harrows, chains, or rollers across the soil to improve soil coverage.

Broadcasting requires twice the amount of seeding rates than drilling. Seed covering efforts are useful for protecting seeds from the elements but some seeds will still be left exposed in the soil surface. These seeds are usually lost to rodents and birds or dry out and die after germinating.

Early stand management

As mentioned earlier, successful forage establishment on dryland is never guaranteed. A dry spring season may result in seedlings drying out and dying shortly after germination. As a result, the reseeding process may have to be repeated. Growth might seem extremely slow during the first year of establishment as the grass attempts to establish its root system. Most of the growth during this time occurs underground, this can result in weak-looking seedlings, but these might recover and begin more vigorous growth in the second and third years.

Newly established dryland grasses should not be grazed until after they set seed, which depends on soil moisture availability, climatic conditions, and individual species. Native plants do not establish quickly and will need up to four years of growth before being grazed. Introduced grasses on dryland will need at least one year from seeding before being ready for grazing. Irrigated introduced grasses can often be lightly grazed during the seeding year once their roots cannot be pulled up by livestock., usually once the plant has at least four leaves and one or two tillers showing. Some irrigated forages like birdsfoot trefoil establish slowly over two to three years. Irrigated stands can be harvested for hay during the establishment year if a 6-inch stubble is left.

Weeds can cause poor stand establishment because they compete for water, space, light, and nutrients. A moderate cover of weeds, however, can shade emerging forage plants and provide a protective environment. On most sites, weeds will need to be controlled during the forage establishment year and possibly during the second year. Mow weeds to 6 inches high, two or three times during the establishment year. Remove mowed material if it is thick enough to smother new plants. Herbicide options exist for newly seeded grasses that have reached at least the three-leaf stage. Herbicides cannot be used on grass-legume mixes because they will kill either the grass or legume.

Ridgway Colorado Cattle Ranch

Grazing Management

Good pasture management sustains forage production, encourages animal health, and discourages weed invasion. It protects soil and increases water infiltration rates and soil organic matter content.

Many dryland pastures in Colorado receive an average of only 12 to 16 inches of precipitation annually. Average precipitation, however, is rarely received in a given year. Most years have precipitation totals below the average, which can be as little as 9 inches. Often a major proportion of precipitation never enters the soil and is lost to evaporation or runoff. As a result, many dryland pastures in Colorado exist in a near-desert climate, creating a fragile environment for forage health and survival. Dryland pastures are more susceptible to these changes, although irrigated pastures are often limited by water available in that ditch during that year.

Proper grazing management on small acreages should aim to preserve forage stands. Animal nutrition and turnout time should be taken into consideration on a grazing rotation but ultimately, a sustainable grazing management plan will always consider leaving some of the plant for proper regrowth.

How a grass grows

Perennial grasses grow from growing points called meristems, located near the base of the plant and close to the soil. Leaves emerge from these growing points, expand upward and capture sunlight for photosynthesis. The carbohydrates produced during photosynthesis are used for new leaf growth, root development and storage in crowns, roots and stems. Perennial grasses survive from year to year because they are capable of retaining energy reserves in their root systems.

Diagram showing parts of a grass plant
Fig 5. Grass parts

As grasses mature, they develop vertical stems and their growing points move higher above the ground. When these growing points are removed through grazing or mowing, the plant can no longer rely on them for regrowth. Instead, it must produce new shoots using stored carbohydrate reserves rather than energy generated through photosynthesis. If this occurs repeatedly, the plant’s energy reserves become depleted, leaving less energy available to break dormancy, recover from stress, and sustain vigorous growth. Over time, plant productivity and persistence decline, which is a common consequence of overgrazing.

Overgrazing

Overgrazing is often he main reason for pasture decline. It results from not allowing grazed plants adequate time for regrowth, and not reducing the grazing pressure (time and/or animal numbers) during drought. Overgrazing reduces plant health and eventually causes desirable forage plants to die. In addition, overgrazed pastures also degrade through increased soil erosion and loss of soil organic matter, reduced water infiltration, and increased weed invasion.

Small acreage dryland pastures, in particular, can fall rapidly into poor condition from overgrazing. Uninformed grazing managers often expect more from dryland pasture plants than what plants can actually produce. Adequate plant regrowth does not occur when forages are either grazed continuously too close to the ground, or regrazed before reaching a target height.

Dryland pasture
Fig 6. Continuous grazing vs rest period on a dryland pasture

The time needed for adequate regrowth depends on the forage species, climate, soil moisture, and time of year. On dryland pastures, 30- to 90-day recovery periods may be needed; on irrigated land, 15 to 30 days. Cool-season grasses regrow faster during cool weather in the spring or sometimes fall; warm-season grasses recover during hot summer weather. Both groups of grasses require adequate soil moisture to support regrowth during the recovery period. Overgrazing can occur when grazing of cool-season grasses is not stopped before dry, hot weather comes in June. These grasses will go dormant and not regrow, leaving the plants with low root and stem base food reserves.

Sometimes pastures may be grazed non-uniformly and more frequently during the rapid plant growth period of early spring with no major negative impacts. In this scenario, the animals will return and re-graze plants, leaving the taller plants alone. The taller plants are not as tender and desirable as the fresh regrowth, so they will continue to grow, while the newer plants get a second grazing. Close attention is still necessary because if regrowth continuously grazed, those plants will lose vigor and die if not allowed to recover.

Drought years can cause a rapid decline in root carbohydrate reserves. These conditions exists when precipitation is 75% of average or lower for several months. This, combined with overgrazing, greatly increases the risk of grass mortality. To reduce this risk, grazing management should be conservative during both drought periods and the growing season following drought. This means grazing fewer animals for shorter periods of time, leaving more leaves and stems for plant survival and regrowth.

Grazing management guidelines

Grazing management refers to grazing at the right time and intensity to maintain sufficient plant cover, protect the soil, and maintain or improve the quantity and quality of forage. Proper grazing management techniques are improved when managers are familiar with the forages in the pasture, their growing season and the animals that will be grazing the pasture. It requires “being on the ground” and being aware of how both forages and animals are performing. Grazing management is both and art and a science.

A major consequence of poor grazing management is that desirable forages will be replaced by undesirable weeds like Russian thistle, downy brome, kochia, and bindweed. Using grazing management to return a poor-condition pasture back to one in good condition is a difficult, long-term process. This task can also be costly because interseeding and a reduction of livestock numbers may be necessary. Good grass and legume stands are difficult to reestablish under dryland conditions. A primary goal of grazing management should be to prevent pastures from deteriorating in the first place. A rule of thumb for proper grazing management is the “take half, leave half principle” for grasses. This means that once animals have grazed half of the height of the grasses in the field, they should be removed to allow grasses to grow back. As mentioned previously, this requires you to learn and understand the full-heigh of the grass species in your field. Table 1. Provides a list of common forage grasses and minimum stubble heights for various species after pasture has been properly grazed.

To understand grazing management, certain terms must be defined and understood:

Stocking Rate

Stocking Rate is the number of animals that graze a pasture over a period of time. It factors in the grazing animal, the available forage, and the length of grazing time. Stocking rates need to be adjusted according to the amount of forage available at the beginning of a grazing period. Available forage changes throughout the year in response to climate, soil moisture, rest period length, adn the grazing history of the pasture. Stocking pastures too heavily will reduce forage regrowth opportunity, reduce animal performance, and initiate a decline in pasture condition. An example of a stocking rate is 0.5 Animal Unit Months per acre (AUMs/ac). This means one acre provides enough forage to support half of an animal unit for one month. In other words, one animal unit could graze a single acre for half a month before needing to move, or it would require two acres to meet its forage needs for a full month and avoid overgrazing.

Animal Units

One Animal Unit (AU) is equivalent to a 1,000-pound cow or five sheep, each weighing 200 pounds. This metric can be applied to all farm animals, and the number of animal units per species or category of animal can be adjusted up or down depending on its weight. For example, a cow weighing 1,300 pounds would be equivalent to 1.3 AUs. This also means that a 1,300-pound cow is estimated to eat 30% more forage compared to a 1000 lb. cow.

Proper Grazing Use

Managing livestock in a way that ensures enough leaf area is left for the plant to maintain vigor and regrowth potential. Once proper use is achieved, forages should be allowed to regrow by moving animals to another pasture or into a corral.

A grazing stick to measure grass height
Fig 7. A ruler or grazing stick can be used to monitor grazing height before and after grazing.

One approach to evaluate proper grazing use is to monitor the pasture currently being grazed for how much forage is left, as opposed to how much has been consumed. This involves looking at how uniform the plants are grazed, and the stubble height (how much growth is left standing) of the grazed plants. When grazing is evaluated correctly and animals are moved at the right time, plants have the best opportunity to regrow as rapidly as possible.

A properly grazed pasture will have an uneven look. Most plants will have been grazed to the minimum stubble height; a small percentage may be shorter. The remaining plants will be tall and either lightly grazed or ungrazed. A pasture is overgrazed if it continually looks like it has been mowed and the forage is uniformly short. Ungrazed plants or patches are normal and result from plants being trampled, fouled by dung or urine, or from natural grazing patterns.

Table 1 lists minimum stubble heights for various forage species after a pasture has been properly grazed. Tall, warm-season grasses include big bluestem, sand bluestem, prairie sandreed, and switchgrass. A small percentage of forages will have stubble heights either shorter or taller than those heights listed. Some of these exceptions are noted in Table 1.

If pastures are continuously grazed (never allowed a 30-day or more rest period), stubble heights should be double the listed height to achieve proper grazing. On smooth brome-alfalfa mixed pastures, smooth brome can occasionally be grazed down to 2-3 inches to favor alfalfa stands.

Minimum stubble heights should still be maintained during the dormant season. Grazing too severely during dormancy can injure plant crowns and reduce stem base carbohydrate storage needed for spring growth. Maintaining minimum stubble heights through winter also allows the stubble to trap snow, protecting the plants and enhancing soil moisture in the spring.

Table 1: Minimum stubble heights for various species after a pasture has been properly grazed
Forage Minimum Stubble Height (inches)
Cool-season grasses
Most species 4
Crested wheatgrasses 3
Western wheatgrass 3
Tall wheatgrass 6
Warm-season grasses
Tall species 6
Little bluestem 4
Sideoats grama 4
Blue grama 2
Irrigated grasses
Most Species 4
Kentucky bluegrass 2
Legumes
Alfalfa 3-4
Birdsfoot trefoil 4-6
Sainfoin 3-4
Clover (white)
Clover (alsike and red)
2
4

Carrying Capacity

Carrying Capacity is the average number of livestock that can be sustained on a management unit (pasture) compatible with management objectives for the unit. It is similar to stocking rate, but on a more refined level. In addition to site characteristics, it is a function of management goals and management intensity.

Setting the carrying capacity is the most important grazing management decision. Carrying capacities are estimates based on expected forage production and performance. They are refined based on experience, grazing methods, and goals.

The amount of forage a pasture produces varies with available moisture, soil types, and pasture condition. Average total forage production (on an air-dry matter basis) ranges from 300 to 2,000 pounds per acre per year on most dryland pastures in Colorado. In contrast, irrigated pastures produce 1 to 6 tons per acre with 4 tons per acre being a good average for the state.

Not all of the forage produced in a year can be grazed. Pastures that are grazed properly will have about 50% of their total forage left as stubble. An additional 25% will be lost to trampling, insects, rodents, and fouling. This leaves 25% of the forage available for livestock consumption. A portion of the 25% wastage can be grazed beneficially in properly managed pasture rotation systems.

Calculating a pasture’s carrying capacity
  1. Determine the annual forage production per acre:

The estimated total annual forage production/acre can be obtained through forage clippings or estimates from platforms such as Web Soil Survey or the Carrying Capacity app. Contact your local NRCS office to obtain forage clippings for your property.

  1. Calculate usable forage:
  • lb of usable forage/acre = lb total annual forage production/acre × 0.25 (25% livestock consumption)
  • Total lb of usable forage/year = lb of usable forage/acre × total acres in pasture
  1. Convert to grazing days for one animal unit (AU)

One AU consumes an average of 2-3% of their body weight daily (1 AU= 1000 lb cow), or approximately 25 lb of air-dry- forage per day.

Days of grazing/year = Total lb of usable forage/year ÷ 25 lb/day

Note that you might need to adjust depending on the animal species, for example, a 1,000-pound horse typically grazes and tramples more forage than a 1,000-pound cow and is equivalent to 1.25 AUs. An average horse will eat and trample 31 pounds of air-dry forage per day. Table 2 contains a list of common grazing species and their equivalent to Animal Units. The AUE for different species can be used to calculate carrying capacity.

Table 2. Animal Unit Equivalent for different species
Animal Species AUE
Cow/calf pair 1.00
Cow (1000 lb) 1.00
Steer (Weight × 0.03)/30.42
Calf (8-12 months) 0.70
Calf (weanling to 8 months) Weight × 0.70
Doe/kid pair 0.25
Donkey 0.60
Draft horse 1.60
Ewe/lamb pair 0.30
Llama 0.50
Mature bull 1.50
Miniature horse 0.37
Horse 1.30
Weaned kid 0.15
Weaned lamb 0.15

The following is an example of calculating carrying capacity:

Assume a 30-acre pasture produces an average of 1,000 pounds of annual forage per acre. One 1,000-pound horse (1.25 AU) will graze it.

  • 1,000 lb/acre × 0.25 (25% utilization) = 250 lb of usable forage/acre
  • 250 lb of usable forage/acre × 30 acres = 7,500 lb of total usable forage
  • 7,500 lb/ (31 lb grazed /day by a 1,000 lb horse) = 242 days of grazing by one horse to achieve proper grazing use.

Conversely, 2 horses grazing on the same property could remain on pasture for 121 and maintain proper grazing.

7,500 lb/ (62 lb/day (2 horses eatinch 31 lb/day each) = 121 days.

To convert to carrying capacity value:

242 days of grazing / 30 acres = 8 horse days per acre (or 10 AU days/acre)

In other words, enough forage exists on one acre of this pasture to meet the horse’s needs for 8 days per year.

In the above example, the same 8 days of grazing on 1 acre can also provide enough forage for:

  • 6 sheep
  • Twelve 100-lb animals (since they are the equivalent to 1 horse or 1.25 AUs)

Similarly, one 1,000-lb cow can graze on one acre for 10 days, which is equivalent to 5 sheep or ten 100-pound animals because they are equivalent to 1 cow or 1.00 AU.

Carrying capacities calculated in the above manner are estimates for average production years. Adjust these estimates based on experience, stubble height monitoring, animal weights, and for dry or wet years.

Table 3 provides an example of how land area and the number of animal units grazing a hypothetical dryland pasture in Colorado influence turnout times. This example considers only forage demand and forage supply and assumes that 30 acres provides enough forage to meet the demands of one animal unit for 365 days while leaving adequate plant residual on site.

The daily turnout times are not recommendations for grazing management as no consideration has been given to timing of plant growth, planning for adequate recovery (plant regrowth without grazing pressure), distribution of grazing use, and timing of grazing use.

Table 3. Carrying capacity scenario in hours per day
Land Area
Animal Units 30 Acres 10 Acres 5 Acres 2.5 Acres
1 24 hrs/day 8 hrs/day 4 hrs/day 2 hrs/day
2 12 hrs/day 4 hrs/day 2 hrs/day 1 hrs/day
3 8 hrs/day 2.6 hrs/day 1.3 hrs/day 40 hr/day
4 6 hrs/day 2 hrs/day 1 hr/day 30 min/day
5 4.8 hrs/day 1.6 hrs/day 50 min/day 24 min/day
6 4 hrs/day 1.3 hrs/day 36 min/day N/A
8 3 hrs/day 1 hrs/day 30 min/day N/A
10 2.4 hrs/day 50 min/day 24 min/day N/A

General pasture management guidelines

  1. Get familiar with a pasture’s carrying capacity and manage it accordingly. Know the pasture’s carrying capacity and manage grazing accordingly. If a pasture supports a horse for only 300 days, do not graze it for 301 days unless moisture conditions provide additional grazeable forage growth.
  2. If you have more animals than the carrying capacity of the pasture, some must either be sold or removed and fed in a corral or holding pasture.
  3. Overgrazing can occur in two ways: leaving your livestock on a pasture for too long or not allowing enough time for the forage to regrow after grazing.
  4. Manage livestock grazing in your pasture by monitoring minimum stubble heights (see Table 1) and the appearance of the whole pasture. Move animals off pasture once minimum stubble height is reached in some areas. The pasture should not look mowed, but rough with areas of taller and shorter grasses. Allow regrazing only after the forage has had time to regrow adequately. A rule-of-thumb is to let the plants regrow to twice their minimum stubble heights before allowing grazing.
  5. Avoid grazing livestock when pastures are wet to minimize plant trampling, damage to plant crowns and to prevent soil compaction.
  6. Spring can be a critical time for forages as they are using root and stem base reserves for growth. Delay grazing until plants reach 5 or 6 inches in height (three to five leaves for grasses). Cool season grasses may be grazed slightly heavier in spring due to favorable regrowth conditions, but they still require sufficient recovery time after grazing. Early spring grazing can also be a cause of pasture-induced laminitis in horses if grazed too soon.
  7. Start the grazing rotation on a different pasture every year. Pasture health will benefit from protecting plants during the “boot stage” when the grasses are elevating their seed heads. Cool season grasses head out in late spring; warm season grasses in mid- to late summer.
  8. Rotational grazing systems allow you to manage your pasture more intensively. If the system is managed correctly, forest harvest efficiency increases. A rotation system will require the pasture to be fenced off into at least two smaller paddocks, but a minimum of 4 is often recommended (see Figure 7 for a rotational grazing plan example). Animals are rotated between the paddocks in time intervals which depend on the season, weather conditions, soil type, and forage condition, tethering can also be a tool to restrict grazing areas for rotational grazing. Typical rest periods are 30 days to 90 days, depending on the time of year and the amount of water available.
  9. Restrict animal access to rivers, creeks, and ponds to protect water quality.
Pasture Diagram

Many small dryland pastures do not grow enough forage to feed a horse for a year, or even a month. Rotating animals between a holding pasture and different sub sections of the pasture provides an alternative that allows fresh forage, pasture management and turn-out times. Animals should be rotated based on forage regrowth rather than calendar time.

Ungrazed pastures

Ungrazed established pastures can still be managed to maintain grass health. Mowing every other year can help recycle plant nutrients by depositing older plant tissue into the soils, increase light penetration through the plant canopy and encourage new leaf growth. Tall, unmanaged grasses may die off and deteriorate if left unmanaged. Mowing is usually not recommended during drought.

Monitor your pasture on a yearly basis for noxious weeds and control them when found. Areas with low densities of desirable vegetation will likely have heavy annual weed infestations. Successful long-lasting control of these weed species can be achieved by applying mechanical or chemical treatment before seed production. Reseed weedy areas after control at the appropriate time to get a good forage stand that will prevent future weed infestations.

Grass Species and Varieties

Legume Species and Varieties

Appendices

Appendix A: Species suggestions for various sites

Site and Species Growth Habit* Season of Growth Origin**
Clay and loam Soils
Crested wheatgrass B Cool I
Russian wildrye B Cool I
Green needlegrass B Cool N
Western wheatgrass S Cool N
Intermediate/pubescent wheatgrass S Cool I
Sideoats grama B Warm N
Little bluestem B Warm N
Big bluestem S Warm N
Switchgrass S Warm N
Blue grama S Warm N
Yellow Indiangrass S Warm N
Alfalfa S Warm N
Sandy Soils
Thickspike wheatgras S Cool N
Prairie sandreed S Warm N
Switchgrass S Warm N
Big bluestem S Warm N
Sideoats grama B Warm N
Yellow Indiangrass S Warm N
Sand bluestem S Warm N
Little bluestem B Warm N
Alfalfa – – I
Saline Soils
Tall wheatgrass B Cool I
Intermediate/pubescent wheatgrass S Cool I
Alkali sacaton B Warm N
Russian wildrye B Cool I
Western wheatgrass S Cool N
Sideoats grama B Warm N
Green needlegrass B Cool N
Switchgrass S Warm N
‘NewHy’ Wheatgrass S Cool I
Site and Species Growth Habit * Season of Growth Origin **
Gravelly Foothills
Big bluestem S Warm N
Little bluestem B Warm N
Crested wheatgrass B Cool I
Sideoats grama B Warm N
Thickspike wheatgrass S Cool N
Western wheatgrass S Cool N
Prairie sandreed S Warm N
Alfalfa – – –
Subirrigated
Smooth brome S Cool I
Western wheatgrass S Cool N
Int/Pub wheatgrass S Cool I
Tall wheatgrass B Cool I
Switchgrass S Warm N
Big bluestem S Warm N
Yellow Indiangrass S Warm N
Alfalfa
Birdsfoot trefoil
Irrigated – Adequate water
Orchardgrass B Cool I
Meadow brome B Cool I
Kentucky bluegrass S Cool I
Tall fescue B Cool I
Alfalfa
Clovers
Cicer milkvetch
Irrigated- Short water
Smooth brome S Cool I
Intermediate wheatgrass S Cool I
Big bluestem S Warm N
Int/pubescent wheatgrass S Cool I
Yellow Indiangrass S Warm N
Switchgrass S Warm N
Alfalfa
Cicer milkvetch
Sainfoin
Low Maintenance Areas (short grass; not grazed)
Blue grama S Warm N
Buffalograss S Warm N
‘Ephrain’ crested wheatgrass S Cool I

*S = sod former, B = bunchgrass, **N = native, I = introduced

Appendix B: Characteristics of grasses

Plant Species Growth Habit Growth Season Origin Moisture Minimum Soil Adaptation Seedling Vigor Yield potential Longevity Drought Tolerance Grazing Tolerance Recovery Rate Salt tolerance
Kentucky bluegrass Sod Cool Europe Irrigated si, c fair low exc. fair good good fair
Big Bluestem sod warm native 14”-18” s, c fair high exc. fair fair fair Fair/poor
Little bluestem bunch warm native 14” s, si, c fair high exc. fair fair Fair/good Fair/poor
Sand bluestem sod warm native 14”- 30” s fair high exc. fair fair good poor
Meadow brome bunch cool Eurasia 16” s, si, c exc. medium good fair good good poor
Smooth brome sod cool Europe 16” s, si, c good medium fair/good fair fair fair/poor fair
Tall fescue bunch cool Europe irrigated s, si, c good high good fair good good good
Blue grama bunch warm native 10” s, si, c fair low exc. exc. good good fair
Sideoats grama bunch warm native 12” si, c fair medium good good fair fair/good fair/good
Yellow Indiangrass Bunch, moderate sod warm native 14” – 18” s, si, c fair medium good fairi fair/good fair fair
Green needlegrass bunch cool native 12”-18” si, c fair medium good fair fair fair fair
Orchardgrass bunch cool Eurasia irrigated s, si, c exc. medium fair fair fair exc. fair
Alkali sacaton bunch warm native 12” -18” si, c poor medium good poor fair/good fair/good exc.
Prairie sandreed sod warm native 10-16” s fair/poor high good fair fair good poor
switchgrass sod warm native 14”-16” s, si, c poor good exc. fair fair good fair
Crested wheatgrass bunch cool Asia 8”-12” s, si, c exc. medium good exc. good exc. fair
Int/pub wheatgrass sod cool Eurasia 12”-15” s, si, c good high fair fair/good fair/good good good
NewHy sod cool Developed in the U.S. 13” si, c Fair/good medium exc. fair/good good good exc.
Tall wheatgrass bunch cool Eurasia 12” – 14” s, si, c fair/poor high good fair fair/good fair exc.
Thickspike wheatgrass sod cool native 8”-20” s, si fair medium Good/fair Exc. good good Fair
Western wheatgrass sod cool native 10” – 14” si, c fair medium good Exc. good good fair
Wildrye Russian bunch cool N. Asia 8” S, si, c poor medium Exc. Exc. good Exc. good
Teff – warm Africa 3 ”/monht during growing season S, si, c good good – Exc. poor Exc. fair
s= sand, si = silt, c = clay, exc.= excellent

Appendix C: Characteristics of legumes

Plant species Moisture Requirements Seedling Vigor Yield Potential Stand Longevity Recovery Rate Drought Tolerance Poor Drainage Tolerance Causes Bloat Salt Tolerance
Alfalfa a good high good a a a yes fair
Red clover high Exc. high Poor/fair fair poor good yes Poor
White clover high Exc. a good good poor fair yes Poor
Milkvetch cicer low poor high Exc. fair fair fair no Fair
Sainfoin Low/medium good medium good Fair/poor fair poor no poor
Trefoil birdsfoot low poor medium fair Fair/poor fair good no Fair/poor
a = depends on variety, exc. = excellent

Photo gallery of grasses in this guide

Photo Credits

  • Retta Bruegger: Kentucky bluegrass, green needlegrass, pubescent wheatgrass
  • Karla Melgar Velis: Smooth brome, leafy spurge
  • Alissa Zurbuchen: Alkali sacaton, big bluestem, sideoats grama, blue grama

References

Author info

Authors: Jennifer L. Cook, Joe E. Brummer, Paul J. Meiman, and Thaddeous Gourd

Updated by: Karla Melgar Velis (2026 edition)

Adapted from the Front Range Guide for the Northern Colorado Front Range, by Ron Jepson, Colorado State University Cooperative Extension, 1997.

Special thanks to USDA NRCS and CSU Extension.

extension.colostate.edu/usda-non-discrimination-statement