Hydrophobicity and aggregate stability in calcareous topsoils from fire-affected pine forests in southeastern Spain

Soil hydrophobicity is known to enhance runoff responses to rainstorms and to increase soil aggregate stability (AS). It has been widely reported for acidic soils particularly under burnt, but also unburnt pine forests following dry periods. Few studies have reported hydrophobicity from alkaline soils, but they have not established whether hydrophobicity also occurs in burnt or unburnt pine forests on alkaline soil. This study examines the wettability and stability of air-dry aggregates and their size fractions ( 30-year-old Aleppo pine {Pinus halepensis} and associated shrub community), geology (limestone), soil type (Lithic Xerorthents), slope angle and aspect (5–8°SW). Included were three sites (A, B, C) burned, respectively, in 1998, 1999 and 2000, and one unburnt for >30 years (D). Hydrophobicity was detected in samples from all sites. Both spatial frequency and persistence of hydrophobicity (Water Drop Penetration Times (WDPT) ranged from 10 to 600 s), however, was lower than reported from studies of acidic soils under pine. This might be associated with a lower susceptibility of alkaline soils to hydrophobicity development and/or the comparatively low biomass production in the region. Probably because it had been most recently affected by severe fire, spatial frequency of hydrophobicity was higher at site B (53% of samples), compared to A, C and D (6%, 33% and 10% of samples, respectively). In contrast to some previous studies, the finest size fraction of the samples consistently had the highest degree of hydrophobicity. Degree of hydrophobicity was positively correlated with organic matter (OM) content (r=0.714). It is speculated that fine, interstitial hydrophobic organic matter accumulating in the finest sieve fraction contributes to this enhanced hydrophobicity. As shown in previous studies on acidic soils, aggregate stability increased with hydrophobicity (r=0.897 in the fraction 0.25–2 mm) for the samples investigated here. This elevated stability occurs despite an already relatively high level of aggregate stability amongst all samples investigated. Hydrophobicity observed at the study sites was not spatially contiguous and it may therefore enhance overland flow and slope wash over only short distances for most, except the very high intensity rainstorms that occur in the region. The increased stability of hydrophobic soil aggregates against slaking, however, may counter an otherwise enhanced susceptibility to erosion.

[1]  D. Richardson,et al.  Water repellency in a dry sclerophyll eucalypt forest — measurements and processes , 1991 .

[2]  R. Shakesby,et al.  Soil hydrophobicity effects on rainsplash: Simulated rainfall and photographic evidence , 1993 .

[3]  W. Degroot,et al.  Effective Heat Content of Green Forest Fuels , 1977 .

[4]  C. Ritsema,et al.  Water repellency of soils; the influence of ambient relative humidity , 2002 .

[5]  R. Shakesby,et al.  Soil hydrophobicity variations with depth and particle size fraction in burned and unburned Eucalypt , 1996 .

[6]  Louis W. Dekker,et al.  Water repellency of sieve fractions from sandy soils and relationships with organic material and soil structure , 1993 .

[7]  S. Cervelli,et al.  WATER‐REPELLENT SUBSTANCES AND AGGREGATE STABILITY IN HYDROPHOBIC SOIL , 1983 .

[8]  A. Piccolo,et al.  Role of hydrophobic components of soil organic matter in soil aggregate stability , 1999 .

[9]  R. Shakesby,et al.  Soil water repellency: its causes, characteristics and hydro-geomorphological significance , 2000 .

[10]  Stefan H. Doerr,et al.  The erosional impact of soil hydrophobicity: current problems and future research directions , 2000 .

[11]  Dominique Arrouays,et al.  Organic Matter Influence on Clay Wettability and Soil Aggregate Stability , 2000 .

[12]  B. Clothier,et al.  Water repellency and its measurement by using intrinsic sorptivity , 1989 .

[13]  Intermountain Forest,et al.  Infiltration and water repellency in granitic soils , 1971 .

[14]  J. Navarro-Pedreño,et al.  Different Patterns of Aggregate Stability in Burned and Restored Soils , 2001 .

[15]  W. Oechel,et al.  A simple method for estimating fire intensity after a burn in california usa chaparral , 1989 .

[16]  J. M. Bremner,et al.  A simple method for determination of ammonium in semimicro‐Kjeldahl analysis of soils and plant materials using a block digester , 1983 .

[17]  A. Roldán,et al.  AN INCUBATION EXPERIMENT TO DETERMINE FACTORS INVOLVING AGGREGATION CHANGES IN AN ARID SOIL RECEIVING URBAN REFUSE , 1994 .

[18]  E. Paul,et al.  Soil microbiology and biochemistry. , 1998 .

[19]  Bessel D. van't Woudt Particle coatings affecting the wettability of soils , 1959 .

[20]  A. Walkley,et al.  AN EXAMINATION OF THE DEGTJAREFF METHOD FOR DETERMINING SOIL ORGANIC MATTER, AND A PROPOSED MODIFICATION OF THE CHROMIC ACID TITRATION METHOD , 1934 .

[21]  C. Ritsema,et al.  Wetting patterns and moisture variability in water repellent Dutch soils. , 2000 .

[22]  D. Hubbell,et al.  High Humidity-induced Increase in Water Repellency in Some Sandy Soils1 , 1985 .

[23]  K. H. Tan,et al.  High pH Treatments and the Alleviation of Soil Hydrophobicity on Golf Greens , 1993 .

[24]  A. C. Imeson,et al.  The effects of fire and water repellency on infiltration and runoff under Mediterranean type forest , 1992 .

[25]  J. Oades,et al.  Extraction and characterization of water–repellent materials from Australian soils , 1988 .

[26]  Louis W. Dekker,et al.  Water repellency in the dunes with special reference to the Netherlands , 1990 .

[27]  C. Ritsema,et al.  Water Repellency and Critical Soil Water Content in a Dune Sand , 2001 .

[28]  J. Stednick,et al.  Strength and persistence of fire‐induced soil hydrophobicity under ponderosa and lodgepole pine, Colorado Front Range , 2001 .

[29]  V. Calzada,et al.  Regeneración de los montes quemados , 1996 .

[30]  V. Calzada La restauración de la cubierta vegetal en la Comunidad Valenciana , 1996 .

[31]  L. Debano Water repellent soils: a state-of-the-art , 1981 .

[32]  A. Wessel On using the effective contact angle and the water drop penetration time for classification of water repellency in dune soils , 1988 .

[33]  D. Scott,et al.  Soil wettability in forested catchments in South Africa; as measured by different methods and as affected by vegetation cover and soil characteristics , 2000 .

[34]  D. A. Hamilton,et al.  Translocation of Hydrophobic Substances into Soil by Burning Organic Litter , 1970 .

[35]  D. Mcghie,et al.  The Effect of Plant Top Material on the Water Repellence of Fired Sands and Water Repellent Soils , 1981 .

[36]  J. Navarro-Pedreño,et al.  Soil organic matter and aggregates affected by wildfire in a Pinus halepensis forest in a Mediterranean environment , 2002 .

[37]  I. Moore,et al.  Soil hydrophobic effects on infiltration and catchment runoff , 1989 .

[38]  R. Shakesby,et al.  Spatial variability of soil hydrophobicity in fire-prone eucalyptus and pine forests, Portugal , 1998 .

[39]  R. Shakesby,et al.  Soil water repellency as a potential parameter in rainfall‐runoff modelling: experimental evidence at point to catchment scales from Portugal , 2003 .

[40]  G. Giovannini,et al.  THE NATURAL EVOLUTION OF A BURNED SOIL: A THREE‐YEAR INVESTIGATION , 1987 .

[41]  W. G. Wells The effects of fire on the generation of debris flows in southern California , 1987 .

[42]  D. Hamilton,et al.  The Transfer of Heat and Hydrophobic Substances During Burning1 , 1976 .

[43]  G. Sposito The Chemistry of Soils , 2008 .

[44]  John A. Matthews Quantitative and Statistical Approaches to Geography: A Practical Manual , 1981 .

[45]  R. Miller,et al.  Nature of the Organic Coating on Sand Grains of Nonwettable Golf Greens1 , 1977 .

[46]  D. Horne,et al.  Soil Water Repellency , 1992 .

[47]  D. Robinson A comparison of soil-water distribution under ridge and bed cultivated potatoes , 1999 .

[48]  P. Hallett,et al.  Subcritical water repellency of aggregates from a range of soil management practices , 2001 .