Effects of fuel reduction treatments on a gorse shrubland soil seed bank in the north of Spain: Comparing mastication and prescribed burning

2013 ◽  
Vol 57 ◽  
pp. 79-87 ◽  
Author(s):  
Cristina Fernández ◽  
José A. Vega ◽  
Teresa Fonturbel
2016 ◽  
Vol 25 (9) ◽  
pp. 946 ◽  
Author(s):  
Susana Zuloaga-Aguilar ◽  
Alma Orozco-Segovia ◽  
Oscar Briones ◽  
Enrique Jardel Pelaez

Prescribed burning is a management instrument applied to reduce the risk of fire and favour revegetation. Our objective was to generate information about the dynamics of post-fire regeneration via the soil seed bank (SSB), for fire management in subtropical forests. Samples taken at soil depths of 0–3cm, 3–6 cm and 6–10 cm before and 5 h after a prescribed burn showed that the fire immediately increased the number of germinable seeds and species in a Mexican pine–oak forest. Most of the germinable seeds were from species in genera with small seeds exhibiting physical or physiological dormancy, and that are tolerant or require fire for germination. Fire increased the number of germinable seeds during the wet season and the number of species was greater in the area control at 0–6-cm soil depth after 1 year; so that the fire modified the SSB seasonal pattern. Species diversity was not altered and was dominated by perennial herbaceous and shrub species both before and 2 years after the fire. Although fire completely eliminated the aboveground biomass of the understorey vegetation, the SSB can promote regeneration and persistence of understorey vegetation following a prescribed surface fire of low severity for the ecosystem studied.


2010 ◽  
Vol 26 (5) ◽  
pp. 714-719
Author(s):  
Ming LI ◽  
De-ming JIANG ◽  
Yong-ming LUO ◽  
Xiu-mei WANG ◽  
Bo LIU ◽  
...  

2012 ◽  
Author(s):  
T. R. Huggins ◽  
B. A. Prigge ◽  
M. R. Sharifi ◽  
P. W. Rundel

1996 ◽  
Vol 36 (3) ◽  
pp. 299 ◽  
Author(s):  
TS Andrews ◽  
RDB Whalley ◽  
CE Jones

Inputs and losses from Giant Parramatta grass [GPG, Sporobolus indicus (L.) R. Br. var. major (Buse) Baaijens] soil seed banks were quantified on the North Coast of New South Wales. Monthly potential seed production and actual seed fall was estimated at Valla during 1991-92. Total potential production was >668 000 seeds/m2 for the season, while seed fall was >146000 seeds/m2. Seed fall >10000 seeds/m2.month was recorded from January until May, with further seed falls recorded in June and July. The impact of seed production on seed banks was assessed by estimating seed banks in the seed production quadrats before and after seed fall. Seed banks in 4 of the 6 sites decreased in year 2, although seed numbers at 1 damp site increased markedly. Defoliation from mid-December until February, April or June prevented seed production, reducing seed banks by 34% over 7 months. Seed banks in undefoliated plots increased by 3300 seeds/m2, although seed fall was estimated at >114 000 seeds/m2. Emergence of GPG seedlings from artificially established and naturally occurring, persistent seed banks was recorded for 3 years from bare and vegetated treatment plots. Sown seeds showed high levels of innate dormancy and only 4% of seeds emerged when sown immediately after collection. Longer storage of seeds after collection resulted in more seedlings emerging. Estimates of persistent seed banks ranged from 1650 to about 21260 seeds/m2. Most seedlings emerged in spring or autumn and this was correlated with rainfall but not with ambient temperatures. Rates of seed bank decline in both bare and vegetated treatment plots was estimated by fitting exponential decay curves to seed bank estimates. Assuming no further seed inputs, it was estimated that it would take about 3 and 5 years, respectively, for seed banks to decline to 150 seeds/m2 in bare and vegetated treatments.


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