What is pinyon-juniper encroachment?

Pinyon-juniper encroachment is the expansion of pinyon-juniper woodlands into ecosystems that historically were shrublands or grasslands. These tree species have increased in abundance due to fire suppression, land use and favorable climate. A significant portion of this encroachment occurs in sagebrush rangelands and affects many processes within these ecosystems.

Key Points

  • » Fire exclusion has facilitated pinyon-juniper expansion into sagebrush ecosystems, changing the fuel amount and structure, leading to more severe fires.
  • » It is easier for invasive species, such as cheatgrass, to establish after more severe fires. Cheatgrass not only outcompetes native vegetation and changes species composition but is also highly flammable, which increases the likelihood of areas transitioning to an annual grassland that is more prone to future fire.
  • » Management of encroached sagebrush rangelands through tree removal can reduce fire severity and potentially lower the risk of non-native species invasion.

Altered fire regimes

Historically, fire in grasslands and sagebrush shrublands occurred often enough to maintain low tree densities and consume the smaller fuels, which resulted in minimal fuel accumulation When fires burned, they were less intense, likely remained smaller in size, and had fewer adverse ecological effects. In the mid-1800s, however, wildfire declined for two primary reasons: 1) overgrazing by livestock reduced fine fuels (e.g., grasses and forbs), which reduced fire spread, and 2) fire from both natural ignitions and indigenous burning was suppressed. The reduction of fire over time, combined with substantially smaller populations of perennial grasses and forbs, likely facilitated pinyon-juniper encroachment into sagebrush rangelands. As trees dominate sagebrush ecosystems fuel amount, structure, and continuity change, altering fire behavior and effects in these systems. Total fuel loads in encroached sagebrush ecosystems can be almost six times more than sagebrush ecosystems that have not been encroached, which causes significant changes in how fires burn.

 The change in fuel type and arrangement in encroached sagebrush ecosystems results in more fires that can burn more easily through the crowns of trees instead of patchy, low-lying fires that stay close to the ground. This shift in fire type influences fire frequency, behavior and severity, which are all key components of a fire regime. In encroached shrublands, the low-lying fuels (e.g., shrubs and grasses) and canopy fuels (e.g., larger shrubs and trees) have better connectivity, creating a ladder of fuels. It is much easier for fires that start in fine grasses on the ground to spread into tree crowns and move quickly across the landscape in these altered systems. Over time, the encroached sagebrush ecosystem can have such high tree cover that it converts to a woodland and has completely different fire dynamics altogether, with a preponderance of high-severity crown fires. In the last few decades, these crown fires in pinyon-juniper woodlands have increased in size and frequency. Contributing factors include increasingly hotter and drier conditions that cause tree mortality, which leads to more fuel and greater invasion of non-native annual grasses that alter fire regimes.

The implications of high-severity fires National Park Service. Evidence shows that tree-encroached ecosystems have higher-severity fires than ecosystems that are not encroached, and these more severe fires alter the landscape in a way that is favorable for invasion by nonnative annual grasses. Even before fire, as tree cover increases, understory plants decline, which leads to a greater likelihood of invasive growth post fire. Fire itself can also reduce the amount of native perennial species in the understory. An increase in litter and downed wood causes fires to be hotter and last longer than they historically would, killing the perennial herbaceous plants that would return after more moderate fire. When there are fewer native perennials, there is less competition for sunlight, nutrients and water, making it easier for non-native invasives to establish. Fire also volatilizes nutrients, increasing their availability to invasive species that can regenerate rapidly after fire. Robust populations of native, perennial herbaceous plants in the understory help ecosystems withstand annual grass invasion, and their survival after fire is crucial to resist non-native establishment. Therefore, when fire occurs at high tree cover and low perennial understory plant cover, a recovery threshold can be crossed and a healthy native ecosystem is not expected after fire. This shift to a different type of ecosystem causes post-fire plant community composition to become unpredictable and can transition the site permanently to non-native grasses.

Additionally, high-severity fires that can occur in encroached sagebrush ecosystems are likely to further influence soils and alter nutrient cycling, which have already changed due to encroachment. Greater loss of vegetation under high-severity fire can result in larger amounts of bare ground that can further increase runoff and soil erosion. The degree of fire severity also influences nutrient and organic matter levels, as fires that result in very high soil temperatures can volatize nutrients, losing

them to the atmosphere. High-severity fires, therefore, can decrease nutrient availability in the soil. Further, trees redistribute nutrients that can become more easily threatened by fire. The increased biomass from pinyon-juniper encroachment results in greater pools of aboveground nutrients, namely carbon, that are susceptible to loss from fire.

Pinyon-juniper management for wildfire risk reduction Management of pinyon-juniper encroached shrublands can help reduce the risk of high-severity wildfire. Treatments to reduce fuel loads can lessen wildfire severity and are often the first step toward restoring resiliency to the ecosystem. These may include prescribed fire and mechanical removal (e.g., mowing, mastication or cutting), which is then often followed by herbicide and reseeding of native perennials. Site conditions play an important role in driving both the health of the understory and the degree of tree encroachment and invasion of non-native grasses, which can then influence the effectiveness of the treatment. However, with thoughtful management, goals of reducing wildfire risk and improving the health of sagebrush shrublands are both attainable.

Putz, T., Restaino, C. 2021, Pinyon-Juniper Encroachment: Effects on Wildfire, Extension | University of Nevada, Reno, FS-21-117

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Also of Interest:

Pinyon-Juniper Encroachment: Effects on Hydrology
Pinyon-juniper encroachment of sagebrush ecosystems alters water processes. This fact sheet details how this change in hydrology occurs and describes the effects of increased water runoff and soil erosion.
Putz, T., Restaino, C. 2021, Extension | University of Nevada, Reno, FS-21-115
hand holding weeds
Pinyon-Juniper Encroachment: Effects on Invasive Species
This fact sheet provides information on the relationship between pinyon-juniper encroachment of sagebrush rangelands and invasive species, such as non-native annual grasses. Learn how encroachment and non-native grasses interact to influence ecosystem functioning and health.
Putz, T., Restaino, C. 2021, Extension | University of Nevada, Reno, FS-21-116
Pinyon-Juniper Encroachment: Effects on Sagebrush-Dependent Wildlife
Pinyon-juniper encroachment of sagebrush ecosystems impacts many wildlife species through loss of habitat. This fact sheet provides information on how decreasing food and cover with encroachment harms sagebrush-dependent wildlife.
Putz, T., Restaino, C. 2021, Extension | University of Nevada, Reno, FS-21-119
undergrowth encroachment
Pinyon-Juniper Encroachment: Effects on Carbon and Nutrient Cycling
The encroachment of pinyon-juniper woodlands into sagebrush ecosystems alters nutrient cycling. This fact sheet details how encroachment affects nutrient availability and carbon sequestration.
Putz, T., Restaino, C. 2021, Extension | University of Nevada, Reno, FS-21-118

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