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International Journal of Mediterranean Ecology - Ecologia ...

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AMINE HABIB BORSALI, KHELOUFI BENABDELI, RAPHAËL GROS<br />

60<br />

microbiological properties (basal respiration,<br />

microbial biomass, enzymatic activities) <strong>of</strong><br />

burned soils. The soil properties were analysed<br />

on 25 soil samples sampled in the Forest <strong>of</strong><br />

Fénouane (wilaya <strong>of</strong> Saïda, Algeria) along a<br />

chonosequence 2, 4, 8, 13 and 20 years after the<br />

last fire (i.e. 5 times since fire x 5 sampling<br />

plots). Compared to an unburned soil since<br />

20 years, the moisture content as well as urease<br />

and FDA hydrolase activities were significantly<br />

reduced 2 years after the last fire. A peak <strong>of</strong><br />

microbial activity, due to a stimulation <strong>of</strong> microbial<br />

growth probably by manure, was measured<br />

8 years after the last fire. These unburned soils<br />

since 8 years are also characterized by very low<br />

organic carbon contents (0.5 %) probably resulting<br />

from a strong erosion concomitant to a<br />

priming-effect <strong>of</strong> recalcitrant organic matter.<br />

This study showed the vulnerability <strong>of</strong> semi-arid<br />

forest soils to a frequency <strong>of</strong> fires over one fire<br />

every 20 years.<br />

Abridged english version<br />

Since 1965, Algerian’s forest patrimony is<br />

menaced by renewed fires that destroy<br />

48,000 ha per year (i.e. 12% <strong>of</strong> the forest surfaces).<br />

An increase in fire frequency associated<br />

to climate warming (IPCC, 2007) could<br />

affect the equilibrium between ecosystem<br />

functioning and ancestral wildfire regime and<br />

lead an instable state in which ecosystem<br />

functions and services may to be not correctly<br />

ensured. In Algeria, the studies about effects<br />

<strong>of</strong> fire on soil quality are rare. The aim <strong>of</strong> this<br />

study was to assess post-fire recovery at short<br />

and long term <strong>of</strong> some soil physico-chemical<br />

(water holding capacity and moisture content<br />

at sampling time, contents in organic carbon,<br />

total nitrogen, ammonium, nitrate and inorganic<br />

phosphorus, pH) and microbiological<br />

properties (microbial basal respiration and<br />

biomass, FDA hydrolase, alkaline phosphomonoesterase,<br />

urease and phenol oxydase<br />

activities).<br />

The study area was located in the forest <strong>of</strong><br />

Fénouane (Sidi M’barek, wilaya <strong>of</strong> Saïda,<br />

Algeria). This forest <strong>of</strong> the southern foothills<br />

<strong>of</strong> the Tell Atlas Mountain can be compared<br />

to others semi-arid fresh bioclimatic stages <strong>of</strong><br />

Algeria with recurrent fires and difficulties to<br />

reafforestation. In this region, the average fire<br />

frequency is close to 1 fire every 25 years.<br />

The study area (2,537 ha) presents an altitude<br />

close to 850 m above sea level and is characterized<br />

by a <strong>Mediterranean</strong> climate. The mean<br />

annual temperature is 16,5 oC and the mean<br />

annual precipitation is 350 mm. At the early<br />

stage <strong>of</strong> succession (i.e. following forest<br />

fires), plant communities are dominated by<br />

herbaceous and fast growing species such as<br />

Pistacia lentiscus, Stipa tenacissima and Cistus<br />

villosus. At the later successional stage<br />

(i.e. with no fire for at least 20 years), close<br />

forest is dominated by a tree stratum <strong>of</strong> Pinus<br />

halepensis and Tetraclinis articulata. In this<br />

forest, 25 sampling plots (400 m2 ) were<br />

selected taking into account the year <strong>of</strong> the<br />

last fire. To assure five replicates <strong>of</strong> each<br />

“time since fire”, 25 sampling plots (400 m2 )<br />

were selected along a chronosequence <strong>of</strong> 2, 4,<br />

8, 13 and 20 years since fire. Soils were sampled<br />

at the top 5 cm and their physico-chemical<br />

properties (water holding capacity and<br />

moisture content at sampling time, contents<br />

in organic carbon, total nitrogen, ammonium,<br />

nitrate, inorganic phosphorus and CaCO3 , pH)<br />

and microbial properties (basal respiration,<br />

microbial biomass, enzymatic activities) were<br />

analysed.<br />

Our results showed lowest soil moisture content<br />

(2 %) in the soils unburned since 2 years.<br />

The destruction <strong>of</strong> arboreous vegetation and<br />

it substitution two years after the fire by an<br />

herbaceous stratum are hypothesized to<br />

increase evapotranspiration and thus soil<br />

drought. Similar organic carbon contents in<br />

the recently burned soils and unburned soil<br />

since 20 years suggested inputs <strong>of</strong> charred<br />

material from carbonized vegetation. In comparison<br />

with soils unburned since 20 years,<br />

FDA hydrolase and phosphomonoestreases<br />

activities remained weaker two years after the<br />

last fire in spite <strong>of</strong> the recovery <strong>of</strong> microbial<br />

biomass. These results are coherent with those<br />

<strong>of</strong> Boerner and Brinkman (2003) who have<br />

shown a decrease in the short term <strong>of</strong><br />

hydrolytic activities due to an alteration <strong>of</strong> the<br />

quality <strong>of</strong> the organic matter. However, concomitant<br />

increase in total nitrogen content to<br />

black carbon also suggested inputs <strong>of</strong> inorganic<br />

nitrogen <strong>of</strong> fresh organic matter. These<br />

inputs <strong>of</strong> available resources, probably originated<br />

from grazing sheep, have stimulated the<br />

recovery 8 years after fire <strong>of</strong> microbial biomass<br />

and some enzyme activities (FDA<br />

hydrolase and phenol-oxydase). Indeed, fire<br />

is frequently used by breeders to promote the<br />

development <strong>of</strong> grasslands and thus allow the<br />

grazing <strong>of</strong> sheep. Either traditional or intensive<br />

grazing is then practiced for 5 years with,<br />

in average, 20 or 150 sheep per hectare<br />

respectively (DSA, 2010). The stimulation <strong>of</strong><br />

microbial growth and activities may have generated<br />

a priming effect <strong>of</strong> the black carbon<br />

ecologia mediterranea – Vol. 38 (1) – 2012

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