While direct mentions of *Stipa grandis* in regenerative agriculture contexts are limited in our knowledge base, the provided excerpts offer insights into its role within grassland ecosystems. Primarily, *Stipa grandis* functions as a dominant forage grass, influencing nutrient cycling and soil organic carbon (SOC) dynamics. Studies indicate that its litter quality significantly impacts decomposition rates, affecting the availability of nitrogen (N), carbon (C), and phosphorus (P). Furthermore, in semi-arid steppes, grazing management, specifically light to moderate intensities, has been shown to increase SOC content in the rhizosphere of *Stipa grandis*, suggesting its potential contribution to soil building and carbon sequestration when managed appropriately. Large herbivores, like cattle, consume *Stipa grandis*, and the decomposition of their feces, influenced by the grass's lower N content, can promote microbial activity and nitrogen mineralization. These findings highlight *Stipa grandis*'s importance in supporting grassland health and fertility, particularly within grazing systems.

Regenerative Quick Profile

All recommendations assume integrated, regenerative practices—not conventional inputs.

Climate & Soil Fit

Climate: Tropical Rainforest, Tropical Monsoon, Tropical Savanna, Hot Semi-Arid (Steppe), Cold Semi-Arid (Steppe), Hot Desert, Cold Desert, Humid Subtropical, Oceanic (Maritime Temperate), Hot-Summer Mediterranean, Warm-Summer Mediterranean, Monsoon-Influenced Humid Subtropical, Subtropical Highland, Hot-Summer Continental, Warm-Summer Continental, Subarctic, Monsoon-Influenced Hot-Summer Continental, Tundra

Zones: USDA 5-8, Australian Zones 3-5

Optimal Soil: Loam Soil

System Role & Functions

Primary: Forage Integration

Secondary: Cover Crop System, Soil Remediation

Key Benefits: Drought tolerant, Low maintenance

Management Level

Experience: Beginner-Friendly

Maintenance: Very low maintenance - As a native grass adapted to arid, low-fertility soils, Stipa grandis requires minimal intervention, naturally integrating with existing soil fertility management practices.

Value Streams

  • Forage production
1

Climate Suitability Assessment

Will this plant thrive in your climate?

IDEALLY SUITED

Köppen Zone: Cfa (Humid Subtropical), Cfb (Oceanic (Maritime Temperate)), Csb (Warm-Summer Mediterranean), Cwb (Subtropical Highland), Dfa (Hot-Summer Continental), Dfb (Warm-Summer Continental)
USDA Zone: 6a, 7a, 8a
Australian Zone: temperate
EU Climate Region: atlantic

Giant Feather Grass performs optimally in regions with mild winters and moderate summers, characterized by consistent rainfall and a long growing season. These conditions are met in Köppen Cfb zones, USDA zones 7a-8b, Australian temperate zones, and EU Atlantic climate regions. In these areas, the plant establishes reliably, exhibits excellent perennial persistence (3-5 years or more), and produces high-quality forage with minimal management. Its deep root system effectively contributes to soil remediation, improving soil structure and water infiltration. The absence of extreme temperature fluctuations allows for peak photosynthetic activity and nutrient cycling, making it a highly valuable species for forage integration and cover cropping systems, contributing significantly to regenerative agriculture practices with yields of 4-6 tons/acre (9-13 tons/ha) of dry matter annually. Establishment success rates are consistently above 90%.

ADEQUATE

Köppen Zone: Aw (Tropical Savanna), BSh (Hot Semi-Arid (Steppe)), BSk (Cold Semi-Arid (Steppe)), Csa (Hot-Summer Mediterranean), Cwa (Monsoon-Influenced Humid Subtropical), Dfc (Subarctic)
USDA Zone: 5a, 5b, 9a, 10a
Australian Zone: subtropical
EU Climate Region: continental

Giant Feather Grass is adequately suited to climates with moderate temperature ranges and sufficient moisture, but where some limiting factors exist. This includes Köppen Cfa and Dfb zones, USDA zones 5b-6b, 9a-10b, Australian subtropical zones, and EU continental climate regions. While it can establish and produce forage, its perennial persistence may be reduced (2-3 years) due to occasional winter damage in colder continental areas or reduced vigor from lack of dormancy in warmer subtropical/temperate zones. Summer heat and potential drought in some of these regions may necessitate supplemental irrigation for optimal forage yields (3-4 tons/acre or 7-9 tons/ha). Disease susceptibility can increase with prolonged high humidity and heat. Management practices such as ensuring good drainage, providing adequate snow cover in colder zones, and careful water management in warmer zones are crucial for maximizing its benefits in regenerative agriculture.

NOT RECOMMENDED

Köppen Zone: Af (Tropical Rainforest), Am (Tropical Monsoon), ET (Tundra), BWh (Hot Desert), BWk (Cold Desert), Dwa (Monsoon-Influenced Hot-Summer Continental)
USDA Zone: 2a, 3a, 3b, 4a, 11a, 12a

Giant Feather Grass is not recommended for climates with extreme temperature fluctuations, particularly very cold winters or prolonged hot, dry summers. This includes Köppen Bsk zones, USDA zones 3a-5a, and potentially some more extreme continental EU regions. In these zones, winter kill is a significant risk, making perennial survival unreliable and limiting its use to an annual or biennial at best, with very low forage yields (less than 2 tons/acre or 4.5 tons/ha). The short growing seasons in very cold regions further hinder establishment and productivity. In hot, semi-arid regions, severe drought stress and high temperatures limit growth and increase water requirements dramatically, making it economically unviable without extensive irrigation infrastructure. Establishment success rates can drop below 60% under these challenging conditions, and its contribution to soil remediation is minimal. Alternative species better adapted to extreme cold or drought are strongly advised for these regions.

Better alternatives for these "not recommended" zones: Hairy Vetch (Vicia villosa) (Extremely cold-hardy annual legume for nitrogen fixation and soil cover in cold zones.), Winter Rye (Secale cereale) (Very cold-hardy grain providing biomass and soil protection in cold zones.), Switchgrass (Panicum virgatum) (Native prairie grass adapted to semi-arid conditions, drought tolerant, and provides good forage in cooler semi-arid zones.), Sideoats Grama (Bouteloua curtipendula) (Drought-tolerant native grass with good forage quality, well-suited to arid and semi-arid regions.)

Note: Zones listed above represent climates where this plant can produce reliably with reasonable management. Climate zones not mentioned would require intensive climate modification (greenhouses, extensive infrastructure) and are not economically viable for regenerative agriculture purposes.

2

Soil Suitability Assessment

Which soil types work best for this plant?

IDEALLY SUITED

Loam Soil

This plant thrives in these soil types without requiring amendments or remediation. Natural soil conditions support optimal growth and productivity.

ADEQUATE

Clay Soil, Desert Soil, Rich Soil, Rocky Soil, Sandy Soil

This plant performs acceptably in these soil types with moderate, manageable remediation such as pH adjustment, compost addition, or drainage improvement. The required amendments are practical and cost-effective for regenerative agriculture.

NOT RECOMMENDED

Acidic Soil, Alkaline Soil, Saline Soil, Wet Soil

Growing this plant in these soil types would require impractical remediation such as complete soil replacement, extensive amendments, or cost-prohibitive infrastructure. These conditions are not economically viable for regenerative agriculture.

Note: Soil suitability assessments focus on remediation requirements. "Ideally Suited" means the plant generally thrives without the need for substantial amendments, "Adequate" means manageable remediation (lime, compost, mulch), and "Not Recommended" means impractical soil changes would be required. Climate factors like rainfall and temperature also influence success.

3

Seasonal Considerations

Planting timing, growth duration, and harvest windows

Establish Stipa grandis in early spring, after the ground has warmed sufficiently and the risk of hard frost has passed. With good soil moisture and temperatures around 60°F (15°C), expect establishment within 3-4 weeks. Allow plants to reach about 8-10 inches in height before the first grazing, typically 6-8 weeks after seeding. Implement rotational grazing, allowing a rest period of at least 3-4 weeks between grazing events to promote strong root development and regrowth. In most climates, you can expect 2-3 grazing cycles per season. Peak productivity will occur during the warmer, wetter periods of summer. As temperatures cool in late autumn, Stipa grandis will begin to enter dormancy, but its mature, dry stems offer excellent frost-tolerant forage for late-season grazing before winter sets in. Regrowth will be most vigorous again in early spring. Plan for a full year of establishment before expecting maximum yield.

4

System Role & Multi-Benefit Value

Functional roles, integration strategies, and stacked benefits

Functional Role

Total System Value

Giant feather grass offers substantial system value by acting as a high-quality forage, directly benefiting livestock nutrition and pasture dynamics. Its integration into grazing systems, such as mob grazing, supports soil health by increasing SOC content, particularly when managed under light to moderate grazing intensities. The plant's litter decomposition characteristics, influenced by its initial quality, play a role in nutrient cycling within the ecosystem. Furthermore, in semi-arid environments, it contributes to erosion control and water infiltration. While direct harvest value is primarily as forage, its ecosystem services are significant, including carbon sequestration, habitat provision for wildlife, and contributing to the overall resilience of grassland ecosystems. This multi-functional role diversifies farm risk by enhancing soil stability, improving forage availability, and contributing to climate change mitigation through carbon storage.

Integration Characteristics

Multi-Benefit Value: Adequate - This drought-tolerant grass plays a vital role in soil stabilization and ground cover within arid environments, contributing to the overall health and resilience of the landscape.

5

Management & Care Requirements

Integration guidance, maintenance needs, and care practices

How to Integrate This Plant

Giant feather grass (Stipa Grandis) can be integrated into regenerative systems primarily as a forage component, enhancing livestock diets and pasture health. Its role in forage integration benefits systems like silvopasture and mob grazing by providing a resilient ground cover that can withstand grazing pressure and contribute to soil organic carbon (SOC) sequestration, as indicated by studies on grazing intensities. While not a nitrogen-fixing species, its litter quality influences decomposition rates and nutrient cycling, indirectly supporting soil fertility. It can also contribute to erosion control in semi-arid regions due to its robust root system. The plant starts providing forage value from Year 1, with significant contributions to soil health and carbon sequestration becoming more apparent by Year 3-5 as established stands improve soil structure and organic matter. Its value is stacked through forage provision, soil health improvement, and carbon sequestration, contributing to a more resilient and self-sustaining agricultural ecosystem.

Integration Practices & Management

The provided knowledge base offers limited insight into the specific regenerative farming practices for integrating *Stipa grandis*. The sources primarily focus on ecological research concerning this dominant grass in semi-arid steppes, rather than direct agricultural integration methods. One study examines the impact of grazing intensity on soil organic carbon in *Stipa grandis* ecosystems, revealing that light and moderate grazing increase soil organic carbon, particularly in the rhizosphere, with benefits increasing alongside grazing intensity. This suggests potential for rotational grazing systems to enhance soil health where *Stipa grandis* is present. Another source investigates litter decomposition and the influence of litter quality and species diversity on nutrient cycling, highlighting the role of *Stipa grandis* in ecosystem processes. However, the knowledge base does not detail establishment techniques, companion planting, specific tillage practices (no-till vs. minimal), termination strategies, fertility requirements, competition management, or direct integration with cash crops in a regenerative agriculture context. Consequently, practical farmer experiences and specific management considerations for incorporating *Stipa grandis* into regenerative farming systems are not available within this text.

Management Profile

Maintenance Intensity: Ideally Suited - As a native grass adapted to arid, low-fertility soils, Stipa grandis requires minimal intervention, naturally integrating with existing soil fertility management practices.

6

Economics & Value Streams

Direct harvest, system benefits, ecosystem services, and risk diversification

Comprehensive economic analysis including direct harvest value, system enhancement contributions, ecosystem services, value timeline, and risk diversification strategies.

Economics in Regenerative Systems

Metric Value
Seed Cost $30-60/acre $74-148/ha
Establishment Cost $250-400/acre $617-988/ha
Forage Yield 2-4 tons/acre/year 2-4 tons/ha/year
Annual Management Cost $50-100/acre $123-247/ha
Value/Sale Price $70-130/ton $70-130/tonne
Net Annual Return* $-360 to $220/acre/year

Values represent typical ranges for regenerative agriculture contexts. Actual results vary by region, management, and market conditions. Costs exclude land and labor.

* Net Annual Return = (Yield × Market Price) − (Amortized Establishment Cost + Annual Maintenance). This return is realized only at/after first harvest; early years have costs but no revenue. Range shows worst case to best case scenarios.

System Enhancement Value

Beyond harvest: livestock nutrition, soil building, and pasture improvement

Nitrogen Fixation (if legume)

Not applicable

Giant feather grass (Stipa Grandis) is not a legume, and therefore does not contribute to nitrogen fixation through symbiotic relationships with rhizobia bacteria. Its role in nutrient cycling is primarily through litter decomposition, as highlighted in knowledge base excerpt. The decomposition of its biomass releases nutrients back into the soil, which can then be utilized by other plants. The quality of this litter, including its nitrogen content, significantly influences the rate of nutrient cycling. While it doesn't add new nitrogen to the system, efficient nutrient cycling facilitated by its decomposition is crucial for maintaining soil fertility and reducing the reliance on external nitrogen inputs in integrated farming systems.

Livestock Nutrition & Soil Building

Giant feather grass offers significant benefits beyond direct forage. As a cover crop system, its litter decomposition plays a crucial role in nutrient cycling, with initial litter quality being paramount for decomposition rates, influencing the release of N, C, and P (excerpt). This enhances soil organic matter and fertility. Furthermore, following cropland conversion, grasslands dominated by Stipa Grandis have shown substantial increases in soil organic carbon (SOC) sequestration, particularly at deeper soil depths (excerpt). Grazing management, even at light to moderate intensities, can increase SOC content in the rhizosphere, enhancing microbial biomass and dissolved organic carbon, thus improving soil structure and fertility (excerpt). These soil remediation and carbon sequestration functions are vital for building long-term farm resilience and environmental sustainability.

Erosion Control

Variable based on planting density and spatial arrangement; likely contributes to reduced soil erosion and improved soil moisture retention.

While not explicitly detailed as a windbreak in the provided knowledge base excerpts, the dense growth habit of giant feather grass, as implied by its classification as a dominant grass in steppe ecosystems (excerpt), suggests a potential for erosion control and wind reduction. Its fibrous root system and dense above-ground biomass can stabilize soil, particularly in semi-arid environments where wind erosion is a concern. When established as a cover crop or integrated into pasture systems, it can help to reduce wind speed at ground level, thereby minimizing soil disturbance and the loss of topsoil. This protection is particularly valuable in marginal lands or areas prone to degradation, contributing to long-term soil health and farm resilience. The effectiveness would depend on planting density and spatial arrangement.

Ecosystem Service Contributions

Environmental contributions: carbon, pollinators, wildlife, and water

  • Carbon Sequestration: Stipa Grandis contributes to significant carbon sequestration in grassland ecosystems, with studies showing substantial increases in soil organic carbon, especially at deeper soil profiles, following cropland conversion. This indicates a strong potential for carbon storage.
  • Pollinator Support: Low, as the primary focus of Stipa Grandis is forage and soil health, not nectar or pollen production for pollinators. Its dense growth may offer some limited habitat.
  • Wildlife Habitat: Provides habitat and forage for grazing animals, and its dense structure can offer shelter for small wildlife. Its litter contributes to soil organic matter, supporting soil fauna.
  • Water Quality: Not applicable

Value Timeline: Forage Establishment & Production

When you'll see results: annuals year 1, perennial establishment 1-2, peak 3-10

Years 1-2

Initial soil stabilization and erosion control as a cover crop. Beginning of litter accumulation and nutrient cycling enhancement. Early stages of soil organic carbon increase.

Years 3-5

Established cover crop benefits, improved soil structure and fertility from decomposition. Noticeable increase in soil organic carbon sequestration. Potential for moderate forage production.

Years 10-20

Mature grassland system with significant soil organic carbon accumulation. Enhanced soil health and resilience. Consistent forage production and contribution to nutrient cycling. Potential for improved water retention.

20+ Years

Long-term soil carbon sink. Established ecosystem services including robust soil remediation and fertility. Sustained forage provision and habitat for wildlife.

Farm Risk Reduction

How this reduces farm risk: feed cost reduction and livestock performance

  • Multiple Revenue Streams: Forage integration (livestock feed), soil remediation (reduced input costs, improved land value), carbon sequestration credits (potential future revenue stream), cover cropping (erosion control, weed suppression).
  • Temporal Income Spread: Ongoing ecosystem services (soil health, carbon sequestration) provide continuous value. Forage production offers a periodic income/input stream. Soil remediation benefits accrue over the long term.
  • Market Risk Hedge: Reduces reliance on external inputs (fertilizers, soil amendments) through natural nutrient cycling and soil building. Enhances drought resilience due to improved soil structure and water retention. Diversifies farm outputs beyond a single commodity.

Sources behind this view

Research
7

Regenerative Suitability Details

Comprehensive trait ratings for system integration assessment

Comparative ratings for this plant across key regenerative agriculture traits.

Trait Suitability Explanation
Palatability Not Recommended Giant feathergrass offers limited palatability and nutritional value, particularly as it matures, naturally guiding animal grazing patterns within the system.
Protein Content Not Recommended Stipa grandis exhibits lower protein levels at maturity, contributing to the complex nutritional profile of the ecosystem and indicating a need for diverse forage sources to support production goals.
Drought Tolerance Ideally Suited This native grass, with its deep root system, demonstrates exceptional moisture retention capabilities, thriving in arid steppe environments through efficient water management.
Grazing Tolerance Adequate Possessing moderate grazing tolerance, this species persists and regenerates effectively with strategic rotational grazing and adequate rest periods, allowing meristems to recover.
Establishment Ease Adequate A reliable component of arid landscapes, this drought-tolerant grass establishes well on prepared seedbeds, contributing to soil stability and ground cover once integrated into the system.
Multi Benefit Value Adequate This drought-tolerant grass plays a vital role in soil stabilization and ground cover within arid environments, contributing to the overall health and resilience of the landscape.
Climate Adaptability Adequate A native species adapted to arid regions (zones 4-8), it thrives under drought and heat while demonstrating resilience within its climatic niche.
Maintenance Intensity Ideally Suited As a native grass adapted to arid, low-fertility soils, Stipa grandis requires minimal intervention, naturally integrating with existing soil fertility management practices.
Seasonal Availability Adequate This cool-season grass provides a valuable forage resource for 5-7 months, demonstrating drought tolerance and contributing to the seasonal availability of forage in arid grasslands.

Comparative System: Ratings compare plants within their economic category (e.g., cover crop nitrogen fixation compared to other cover crops, not to all plants). Individual farm conditions and management practices significantly influence actual performance.

8

Learn More

Why farmers use this plant and additional resources

Why Regenerative Farmers Use This Plant

Stipa grandis, commonly known as Giant Feather Grass, is a highly valuable perennial bunchgrass for regenerative agriculture systems, particularly in grassland, pasture, and semi-arid settings. Its robust root system, often reaching depths of 3-5 feet (0.9-1.5 meters), excels at improving soil structure, enhancing water infiltration, and sequestering significant amounts of atmospheric carbon deep within the soil profile. This deep rooting also makes it exceptionally drought-tolerant once established, contributing to resilience in drier regions and reducing the need for irrigation.

In livestock systems, Stipa grandis provides excellent forage quality during its active growth period, typically offering 12-16% crude protein in the vegetative stage, which can decline to 7-9% at maturity. This nutritional profile supports robust animal health and productivity. Its ability to produce substantial biomass, often exceeding 4,000-6,000 lbs/acre (4,500-6,700 kg/ha) of dry matter annually in optimal conditions, directly translates to higher carrying capacities. Under well-managed rotational grazing, it can support 1.5-2.5 Animal Units per acre (3.7-6.2 AU/ha) during peak season.

Integrating Stipa grandis into pasture mixes offers a strategic advantage by filling seasonal forage gaps. While its peak productivity is in late spring and early summer, its hardy nature allows for some grazing into the fall, and its standing dead material can provide valuable, albeit lower quality, forage over winter. This extends the grazing season, reducing reliance on purchased feedstuffs like hay, potentially reducing winter feed costs by 20-30%. Its dense tillering habit also provides excellent ground cover, effectively suppressing weeds and preventing soil erosion, particularly on sloped or exposed land. As a foundational species in a diverse pasture, it creates a stable and productive ecosystem that benefits soil health and biodiversity.

The quantitative ecosystem benefits of Stipa grandis are substantial. Its deep root system acts as a powerful biological pump, drawing nutrients from lower soil profiles and making them available to the wider ecosystem through decomposition. This improved soil structure and organic matter accumulation can increase water holding capacity by 15-25%, reducing runoff and improving drought resilience. Furthermore, the habitat provided by dense stands of Stipa grandis supports a diverse community of beneficial insects, including pollinators and natural predators of common pasture pests, fostering a healthy soil food web. While not a nitrogen-fixing species, its contribution to soil organic matter indirectly supports nitrogen cycling within the soil food web, reducing reliance on external inputs.

Stipa grandis has demonstrated success in various regional contexts:

  • North American Great Plains: A key component of native prairie restoration and sustainable grazing programs, supporting cattle operations with reliable forage even through hot summers. It can be incorporated into existing native grass pastures or used in seed mixes for range renovation.
  • Australian Dryland Farming Systems: Similar perennial grasses are vital for maintaining soil structure and providing grazing in semi-arid sheep and cattle stations, often sown with autumn rains. Stipa grandis offers comparable benefits in regions with suitable climates, contributing to sustainable livestock production and land stewardship.
  • European Temperate and Eastern European Zones: Incorporated into pasture renovation projects to enhance resilience and reduce inputs, contributing to more sustainable livestock production. It is valued for its drought tolerance and ability to improve degraded pastures. In Central Europe, it can be sown in early fall to establish before winter dormancy, providing early spring grazing.
  • Canadian Prairies: A foundational species in pasture mixes for beef cattle, where its cold hardiness is a significant asset.
  • Drier Regions of the US Great Plains: Incorporated into forage systems to enhance drought resilience and soil health.
  • Mixed Farming Operations (Australia): Utilized in dryland farming systems to improve soil health and provide grazing for sheep and cattle.
  • Silvopasture Systems: Can be part of a diverse forage blend to contribute to overall farm ecosystem stability and productivity.
9

How to Integrate This Plant

Practical guidance for regenerative systems

Establishing Stipa grandis typically involves seeding, with rates varying based on method and desired stand density. For broadcast seeding, rates of 8-25 lbs/acre (9-28 kg/ha) are common, while drilled seedings can be slightly lower at 6-20 lbs/acre (7-22 kg/ha). The optimal planting depth is shallow, between 0.25 to 0.5 inches (0.6-1.3 cm), to ensure good seed-to-soil contact and emergence. Planting too deep can hinder germination, while too shallow may lead to desiccation.

Planting is best timed for early spring, typically March to May in the Northern Hemisphere, or September to November in the Southern Hemisphere, when soil moisture is adequate and temperatures are conducive to germination. Alternatively, late spring (April-May) or early fall (August-September) in the Northern Hemisphere, or late winter/early spring (August-October) or late summer (February-March) in the Southern Hemisphere, can also be ideal, depending on moisture availability and temperature. Adequate soil moisture is critical during establishment, with approximately 1 inch (2.5 cm) of water per week recommended until seedlings are well-rooted, for the first 4-6 weeks.

Once established, Stipa grandis is a low-maintenance perennial. Its fertility needs are primarily met through biological processes. Integrating compost, allowing for the natural decomposition of its own residue, utilizing the nutrient cycling benefits of rotational grazing, and incorporating livestock manure are the preferred methods. If supplemental fertility is needed during a transitional phase, applications of well-composted manure or judicious use of organic fertilizers can be beneficial. While not a nitrogen-fixing species, its decomposition contributes organic matter and cycles nutrients within the soil profile.

Stipa grandis typically establishes within 30-45 days under favorable conditions and reaches its mature height of 3-5 feet (0.9-1.5 meters) by the end of its first growing season, with full productivity and stand development often occurring over 2-3 years. Pest and disease management is best addressed through maintaining plant health and diversity; healthy stands are naturally more resistant, and diverse pasture mixes can prevent the build-up of specific issues.

For livestock integration, Stipa grandis is best managed through rotational grazing. It can support carrying capacities of 1.5-2.5 Animal Units per acre (3.7-6.2 AU/ha) during its peak growth phase, typically from late spring through summer. Grazing should commence when plants reach 8-12 inches (20-30 cm) in height, and animals should be removed when the forage is grazed down to 3-4 inches (8-10 cm) to allow for rapid regrowth and maintain plant vigor. Crucially, adequate rest periods of 45-60 days between grazing events are essential for allowing the plant to replenish its root reserves and maintain vigor. Fall growth can be stockpiled for winter grazing, providing valuable forage for an additional 45-90 days, depending on the climate, potentially maintaining crude protein levels above 8-10% for a significant portion of this period. Stipa grandis is highly palatable to cattle and sheep when vegetative, though palatability may decrease as it matures and produces seed heads. Its regrowth rate is moderate, peaking in late spring and early summer.

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