Abstract:The effects of an intense fire on the nutrient status of jarrah ^Eucalyptus marginata Donn ex Sm.) forest soils were investigated. At seven experimental sites, representing a range of soil and vegetation types, surface soils were sampled to a maximum depth of 20 cm before, immediately after, and 1 year after the fire.Immediately after the fire, concentrations of total and extracted nutrients in surface (0-3 cm) soils mcreased markedly. One year later, concentrations of extracted nutrients in surface soils had … Show more
“…However, although most nitrogen is volatilized and lost, the remaining ammonia and nitrate nitrogen is settled to the soil surface. This is why some studies report on total N increase on the surface soil, and many studies on increase in inorganic forms of N immediately after the fire (Christensen, 1973;Covington and Sackett, 1986;De Bano et al, 1979;Grove et al, 1986;Hunt and Simpson, 1985;Khanna and Raison, 1986;Kovacik et al, 1986;Schoch and Binkley, 1986;Stock and Lewis, 1986;White, 1986).…”
Section: Discussionmentioning
confidence: 96%
“…All these nutrients, returning to the soil surface, are mostly in mineral and partly in extractable form (Brown and Mitchell, 1986;Christensen, 1977;Covington and Sackett, 1986;De Bano and Klopatek, 1988;Grove et al, 1986;Lewis, 1974;Lloyd, 1971;Walker et al, 1986) and are easily available for the uptake by plants and microorganisms. As most plants and microorganisms are not killed during these low-intensity burnings (Gillon et al, 1987), they are able to immediately utilize these nutrients.…”
Section: Discussionmentioning
confidence: 96%
“…These data give useful indications on nutrient losses during burning, but always under artificial conditions. Attempts in the field were based on differences in the nutrient content of fuels before burning and of the remains after the fire (De Bano and Conrad, 1978;Grove et al 1986;Harwood and Jackson, 1975;Schoch and Binkley, 1986). In these studies, plant and litter nutrient and biomass were sampled before burning and after fire, sometimes with inclusion of the surface soil layer.…”
Losses of N, P, K and Ca were measured during a prescribed burning in a French Mediterranean Pinus halepensis forest, with understorey of Quereus eoceifera. Nutrient loss was measured by difference between the quantity of a nutrient in the fuel before burning and that found in the postfire remains which were harvested or recovered in small trays. Reduction in fuel weight amounted to 77%, losses from initial fuel elements amounted to 77% for N, 54% for K and 35% for P. No significative loss of Ca was measured. Burning resulted in 7 t ha-l fuel reduction and in loss of 55 kg ha-~ N, 8.5 kg ha-l K and 1.0 kg ha-~ P.
“…However, although most nitrogen is volatilized and lost, the remaining ammonia and nitrate nitrogen is settled to the soil surface. This is why some studies report on total N increase on the surface soil, and many studies on increase in inorganic forms of N immediately after the fire (Christensen, 1973;Covington and Sackett, 1986;De Bano et al, 1979;Grove et al, 1986;Hunt and Simpson, 1985;Khanna and Raison, 1986;Kovacik et al, 1986;Schoch and Binkley, 1986;Stock and Lewis, 1986;White, 1986).…”
Section: Discussionmentioning
confidence: 96%
“…All these nutrients, returning to the soil surface, are mostly in mineral and partly in extractable form (Brown and Mitchell, 1986;Christensen, 1977;Covington and Sackett, 1986;De Bano and Klopatek, 1988;Grove et al, 1986;Lewis, 1974;Lloyd, 1971;Walker et al, 1986) and are easily available for the uptake by plants and microorganisms. As most plants and microorganisms are not killed during these low-intensity burnings (Gillon et al, 1987), they are able to immediately utilize these nutrients.…”
Section: Discussionmentioning
confidence: 96%
“…These data give useful indications on nutrient losses during burning, but always under artificial conditions. Attempts in the field were based on differences in the nutrient content of fuels before burning and of the remains after the fire (De Bano and Conrad, 1978;Grove et al 1986;Harwood and Jackson, 1975;Schoch and Binkley, 1986). In these studies, plant and litter nutrient and biomass were sampled before burning and after fire, sometimes with inclusion of the surface soil layer.…”
Losses of N, P, K and Ca were measured during a prescribed burning in a French Mediterranean Pinus halepensis forest, with understorey of Quereus eoceifera. Nutrient loss was measured by difference between the quantity of a nutrient in the fuel before burning and that found in the postfire remains which were harvested or recovered in small trays. Reduction in fuel weight amounted to 77%, losses from initial fuel elements amounted to 77% for N, 54% for K and 35% for P. No significative loss of Ca was measured. Burning resulted in 7 t ha-l fuel reduction and in loss of 55 kg ha-~ N, 8.5 kg ha-l K and 1.0 kg ha-~ P.
“…Other changes to the habitat in the first few years after fire may be more important to plant recruitment in these large seeded species, such as soil properties (Grove et al 1986;Certini 2005). Examination of the conditions in microsites where seedlings have and have not been established may provide insights into other possible mechanisms influencing establishment (e.g., Lamont et al 1993;Garcia and Houle 2005).…”
Section: The Influence Of Litter On Seedling Recruitmentmentioning
Recruitment in plant populations is often tightly coupled to major disturbances such as fires. For species with persistent seed banks, fire-related cues may allow or enhance germination. The litter layer influences germination and may modify the impact of seed predators on seeds and seedlings. The litter layer is obviously affected by fire, providing one mechanism by which disturbance can determine recruitment. We tested the role of litter in the disturbance-recruitment coupling of two species with contrasting seed release timing after fire-Banksia serrata (canopy seed bank) and Telopea speciosissima (transient seed bank) by planting their seeds both early and late in the post-fire recruitment period (PRP) and manipulating litter density in orthogonal treatments. Vertebrate seed predators were excluded. Both species established more seedlings late in the PRP, although results were strongly influenced by very poor establishment at one site. Invertebrate seed predators consumed more T. speciosissima seeds in sites early (69.5%) than late in the PRP (51.2%), while consumption of B. serrata seeds was lower overall and comparable across sites (average 47.3%). Surprisingly, litter had very little effect on establishment and none on invertebrate seed predation, suggesting that other factors are more important. Recruitment was only loosely coupled to disturbance for the canopy seed bank species; for the transient seed bank species, the coupling was tighter but separated in time from the disturbance. Understanding both the strength and temporal aspects of the disturbance-recruitment coupling is necessary for appropriate management of plant functional diversity in fire-prone habitats.
“…Increases in plant availability of the cations and P after fire is one of the most common responses found (Grove et al 1986). In our study, these effects tended to be relatively short lived, with most soil properties returning to their pre-fire levels within the first or second year after fire.…”
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.