Minimal effectiveness of native and non-native seeding following three high-severity wildfires
Ken A. Stella A C , Carolyn H. Sieg B and Pete Z. Fulé AA School of Forestry and Ecological Restoration Institute, Northern Arizona University, PO Box 15018, Flagstaff, AZ 86011, USA.
B USDA Forest Service, Rocky Mountain Research Station, 2500 South Pine Knoll Drive, Flagstaff, AZ 86001, USA.
C Corresponding author. Email: kstella@fs.fed.us
International Journal of Wildland Fire 19(6) 746-758 https://doi.org/10.1071/WF09094
Submitted: 1 September 2009 Accepted: 24 January 2010 Published: 17 September 2010
Abstract
The rationale for seeding following high-severity wildfires is to enhance plant cover and reduce bare ground, thus decreasing the potential for soil erosion and non-native plant invasion. However, experimental tests of the effectiveness of seeding in meeting these objectives in forests are lacking. We conducted three experimental studies of the effectiveness of seeding with non-native and native species following three Arizona wildfires. Seeding treatments were largely ineffective in increasing vegetative cover or decreasing exposed bare ground. At one treatment at one fire, wheat seeding at the Warm Fire, senesced seeded annuals increased litter cover and resulted in lower bare ground values than unseeded controls. Only on one fire, the Warm Fire, did seeded non-native annuals establish well, resulting in 20–29% vegetative cover. On the other two fires, seeded cereal grains accounted for <3% cover. At all fires, native seeded species contributed between <1 and ∼12% vegetative cover. Vegetative cover on all treatments, including unseeded treatments, was at or near 40% the first year following fire, at all three study sites. Non-native species richness and abundance did not differ among treatments at any fire. This study adds to growing evidence that post-fire seeding is ineffective in enhancing post-fire plant cover and reducing invasive non-native plants.
Additional keywords: annual ryegrass, Burned Area Emergency Rehabilitation, exotic plants, fire rehabilitation, ponderosa pine, wheat.
Acknowledgements
This project was funded by the National Fire Plan – Restoration/Rehabilitation of Burned Areas EBLI (NFN3) for the development and use of native plant materials, 2006, USDA Forest Service Rocky Mountain Research Station Challenge Cost Share Agreement 06-CS-11221616–27. Field crews from the Forest Service Rocky Mountain Research Station and the Northern Arizona University Ecological Restoration Institute provided invaluable help in data collection, data entry, and plant identification.
Amaranthus MP, Trappe JM , Perry DA (1993) Soil moisture, native regeneration and Pinus lambertiana seedling survival, growth, and mycorrhiza formation following wildfire and grass seeding. Restoration Ecology 12, 188–195.
Crawford JA, Wahren CH, Kyle S , Moir WH (2001) Responses of exotic plant species to fires in Pinus ponderosa forests in northern Arizona. Journal of Vegetation Science 12, 261–268.
| Crossref | GoogleScholarGoogle Scholar |
Daniels ML, Springer JD, McGlone CM , Wilkerson W (2008) Seeding as part of forest restoration promotes native species establishment in Grand Canyon–Parashant National Monument (Arizona). Ecological Research 26, 188–190.
| Crossref | GoogleScholarGoogle Scholar |
Elseroad AC, Fulé PZ , Covington WW (2003) Forest road revegetation: effects of seeding and soil amendments. Ecological Research 21, 180–185.
| Crossref | GoogleScholarGoogle Scholar |
Gill RA, Kelly RH, Parton WJ, Day KA, Jackson RB, Morgan JA, Scurlock JMO, Tieszen LL, Castle JV, Ojima DS , Zhang XS (2002) Using simple environmental variables to estimate belowground productivity in grasslands. Global Ecology and Biogeography 11, 79–86.
| Crossref | GoogleScholarGoogle Scholar |
Griffin JR (1982) Pine seedlings, native ground cover, and Lolium multiflorum on the Marble-Cone burn, Santa Lucia Range, California. Madrono 29, 177–188.
Groen AH , Woods SW (2008) Effectiveness of aerial seeding and straw mulch for reducing post-wildfire erosion, north-western Montana, USA. International Journal of Wildland Fire 17, 559–571.
| Crossref | GoogleScholarGoogle Scholar |
McKay JK, Christian CE, Harrison S , Rice KJ (2005) ‘How local is local?’ A review of practical and conceptual issues in the genetics of restoration. Restoration Ecology 13, 432–440.
| Crossref | GoogleScholarGoogle Scholar |
Moore MM, Casey CA, Bakker JD, Springer JD, Fulé PZ, Covington WW , Laughlin DC (2006) Herbaceous vegetation responses (1992–2004) to restoration treatments in a ponderosa pine forest. Rangeland Ecology and Management 59, 135–144.
| Crossref | GoogleScholarGoogle Scholar |
Robichaud PR, Lillybridge TR , Wagenbrenner JW (2006) Effects of post-fire seeding and fertilizing on hillslope erosion in north-central Washington, USA. Catena 67, 56–67.
| Crossref | GoogleScholarGoogle Scholar |
Schoennagel TL , Waller DM (1999) Understory responses to fire and artificial seeding in an eastern Cascades Abies grandis forest, USA. Canadian Journal of Forest Research 29, 1393–1401.
| Crossref | GoogleScholarGoogle Scholar |
Wagenbrenner JW, MacDonald LH , Rough D (2006) Effectiveness of three post-fire rehabilitation treatments in the Colorado Front Range. Hydrological Processes 20, 2989–3006.
| Crossref | GoogleScholarGoogle Scholar |
Wienk CL, Sieg CH , McPherson GR (2004) Evaluating the role of cutting treatments, fire, and soil seed banks in an experimental framework in ponderosa pine forests of the Black Hills, South Dakota. Forest Ecology and Management 192, 375–393.
| Crossref | GoogleScholarGoogle Scholar |
Wolfson BAS, Kolb TE, Sieg CH , Clancy KM (2005) Effects of post-fire conditions on germination and seedling success of diffuse knapweed in northern Arizona. Forest Ecology and Management 216, 342–358.
| Crossref | GoogleScholarGoogle Scholar |