Controlling Non-native Cool-season Grasses (NCGs) Prairie Remnants and Restorations

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Controlling Non-native Cool-season Grasses (NCGs) in Prairie Remnants and Restorations

What is a cool-season plant? C3 photosynthetic pathway Prefer moist and cool conditions Most plant species

What is a warm-season plant? C4 photosynthetic pathway Efficient in hot and dry conditions Relatively few plant species

Photosynthesis CO 2 + H 2 O + Sunlight = Sugar + O 2 Sugar = chains of carbon C3 plants = make 3-atom carbon-chain sugars C4 plants = make 4-atom carbon-chain sugars

C3 plants most efficient at making sugar under Cool temperatures (heat reduces efficiency of their enzymes) Moist conditions (transpire more water per sugar made) Moderate light levels (high light reduces their enzyme efficiency) Productive in spring and fall

C4 plants more efficient under high light and heat conditions Extra enzyme Faster photosynthesis at high light and heat Therefore, less water loses per calorie of sugar made Productive in heat and drought of summer

Invasive, non-native, cool-season grasses Kentucky bluegrass Smooth brome Quack-grass Red-top, bent-grass Reed canary-grass Timothy (Poa pratensis) (Bromus inermis) (Elytigia [Agropyron] repens) (Phleum pratense) (Agrostis spp.) (Phalaris arundinacea) Not foxtails

Using Fire Photo by K. Agee To Control NCGs Photo by R. Oberle

Direct Effects of Fire Kills above ground tissue Removes accumulated litter layer (sun light) Volatilizes N & S Leaves behind P, K, and other nutrients

Indirect Effects of Fire Reduced soil moister Increased soil/micro-climate temperature Shortened cool-season Lengthened warm-season Reduced available N over time

Fire Variables that Determine Fire Effect Intensity Frequency of Occurrence Seasonal Timing

Kentucky bluegrass Flowering after one burn in a dry-mesic prairie Inflorescences / m 2 180 160 140 120 100 80 60 40 20 0 a Control burn) (no a Late March Burn b Mid May Burn (Henderson et al. 1982)

Kentucky bluegrass Frequency after burning 8 out of 10 years in a dry prairie % occurrence per ¼ m 2 60 50 40 30 20 10 0 a a a a a b b c Control (no burns) Late Nov. Burns Late March Burns Mid May Burns 1980 1989 (Henderson 1990)

Smooth Brome after an Early-May Burn Burned Un-burned

Reed canarygrass Cordgrass October 24 Reed canary-grass early-spring burns annually 20 years cord-grass invading @ 6 per year

Reed canary-grass after a late-spring burn Un-burned August 5 Burned June 3

Caution There are many native coolseason species in prairie All sedges, most forbs, and some grasses They too can be harmed and eliminated by mid- and late-spring fire

Bromus kalmii Flowering after one burn in dry-mesic prairie % of inviduals flowering 80 60 40 a a 20 0 Control (no Late burns) March Mid Burns May Burns b 1980 Prairie Restorations, Inc. (Henderson 1981)

% of individuals flowering Panicum leibergii-oligosanthes Flowering annual burning for 3 years 70 60 50 40 30 20 10 0 Control (no Late burns) Nov. Late Burns March Mid Burns May Burns 1980 1981 1982 (Henderson et al. 1982)

Panicum leibergii-oligosanthes Density after burning 8 out of 10 years in a dry prairie Individuals per ¼ m 2 3.5 3 2.5 2 1.5 1 0.5 a a a a a a a b 1980 1989 0 Control (no burns) Late Nov. Burns Late March Burns Mid May Burns (Henderson 1990)

Mid Summer Fires? Greatest stress to trees & shrubs Suppress/weaken warm-season grasses Can increase growth/vigor of cool-season species: native & non-native July 27 burn *Releases suppressed, non-native, coolseason grasses

Herbicide Application Glyphosate Can release natives when timed right & natives hidden under NCGs and litter Prairie remnants over taken by invasive cool-season grasses New plantings affected by non-native cool-season grasses May kill early-season natives Some natives over winter with green leaves Some natives green up with the non-native cool-season grasses

Example early-season natives overwintering with green rosettes or leaves Antennaria spp. (pussy-toes) Geum triflorum (prairie smoke) Panicum spp. (panic-grasses) Stipa spartea (needle-grass) Valeriana edulis (valerian) Viola pedata (bird s-foot violet)

Example early-season natives with early green-up, but no overwintering leaves Bromus spp. (native brome grasses) Camassia scilloides (wild hyacinth) Carex spp. (sedges) Dodecatheon meadia (shooting star) Pedicularis candensis (wood betony) Ranunculus spp. (buttercups) Zizia spp. (golden Alexanders)

Fire vs. Timed Herbicide Fire can be as effective, but slower (takes years) Fire has less risk to early-season natives

Grazing To control cool-season grasses In simple systems? In remnants & diverse restorations?

Restoration by Inter-Seeding Requires weakening of invasive coolseason grasses by fire facilitates establishment of native seedlings stimulates/releases latent/suppressed plants Requires repeated burning Requires repeated seeding Seasonal timing of fire is important

Sugar River Savanna A 30-year trial case of inter-seeding

Sugar River Savanna - 1975 Never plowed Grazed hard for 130 years 85% of the native plant species either gone, or only a few individuals remaining Dominated by non-native cool-season grasses Kentucky bluegrass Quack-grass Red-top Timothy Smooth brome

Inter-seeding Experiment Begins 1976 Burned in early spring annually for 33 years (missed 1 out of 33) Seed scattered by hand seed planted, as collected or some held over to next spring, after each burn repeated seeding over 15 years No herbicide No raking the soil No mowing Hand pulling of parsnip and sweet-clover

30 years later

Keystone species? Wood betony (Pedicualris canadensis) Northern bedstraw (Galium boreale) False toadflax (Comandra umbellata) Stop burning and non-native cool-season grasses will come back! But, does not have to be annual burning to maintain.

Controlling non-native cool-season grass is the first step in bringing back prairie & savanna