Degradation of moist soil aggregates by rapid temperature rise under low intensity fire

Background and aims Soil structure degradation by fire is usually attributed to qualitative and quantitative change of organic and inorganic binding agents, especially in high severity burns (> 300 °C) that last for prolonged periods (> 1 hour). In contrast, controlled burns are typically mana...

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Veröffentlicht in:Plant and soil 2013-01, Vol.362 (1/2), p.335-344
Hauptverfasser: Albalasmeh, Ammar A., Berli, Markus, Shafer, David S., Ghezzehei, Teamrat A.
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creator Albalasmeh, Ammar A.
Berli, Markus
Shafer, David S.
Ghezzehei, Teamrat A.
description Background and aims Soil structure degradation by fire is usually attributed to qualitative and quantitative change of organic and inorganic binding agents, especially in high severity burns (> 300 °C) that last for prolonged periods (> 1 hour). In contrast, controlled burns are typically managed to be low in intensity and severity. Such burns are considered benign to soil structural stability because organic matter and inorganic binding agents (e.g., gypsum) are relatively stable at such low temperatures. Recent observations at a controlled burn site in the eastern Great Basin (Nevada) showed soil aggregate breakdown found in shrub canopies where soil temperatures briefly exceeded 300 °C as well as interspaces between shrubs, where the temperatures were likely lower than beneath shrubs because of less surface biomass. These alterations cannot be explained in terms of thermal alteration of binding agents. This study was designed to test whether pressure created by rapidly vaporized pore water can cause aggregate breakdown. Methods We subjected three different sizes of aggregates (0.25-1, 1-2 and 2-4 mm) of soils derived from the eastern Great Basin burn site as well as from a forest and urban garden in California to rapid and slow (3 °C/min) heating rates. These treatments were conducted at 5 peak temperatures (75,100,125,150 and 175 °C). Results Post-burn water stability of the aggregates showed that rapid heating rate caused more pronounced degradation of aggregate stability than slow heating. Moreover, the heating-rate dependent structural degradation increased with peak temperature. For the majority of the aggregates, the effect also increased with initial water content. In all the soils tested, there was no preferential loss of organic matter in the rapid-heating treatment that can explain the observed enhanced breakdown of aggregates. Conclusions Our observations indicate that soil structural degradation under low-intensity fire occurs as a result of mechanical stresses extorted by rapidly escaping steam from soil pores under rapid heating rate.
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In contrast, controlled burns are typically managed to be low in intensity and severity. Such burns are considered benign to soil structural stability because organic matter and inorganic binding agents (e.g., gypsum) are relatively stable at such low temperatures. Recent observations at a controlled burn site in the eastern Great Basin (Nevada) showed soil aggregate breakdown found in shrub canopies where soil temperatures briefly exceeded 300 °C as well as interspaces between shrubs, where the temperatures were likely lower than beneath shrubs because of less surface biomass. These alterations cannot be explained in terms of thermal alteration of binding agents. This study was designed to test whether pressure created by rapidly vaporized pore water can cause aggregate breakdown. Methods We subjected three different sizes of aggregates (0.25-1, 1-2 and 2-4 mm) of soils derived from the eastern Great Basin burn site as well as from a forest and urban garden in California to rapid and slow (3 °C/min) heating rates. These treatments were conducted at 5 peak temperatures (75,100,125,150 and 175 °C). Results Post-burn water stability of the aggregates showed that rapid heating rate caused more pronounced degradation of aggregate stability than slow heating. Moreover, the heating-rate dependent structural degradation increased with peak temperature. For the majority of the aggregates, the effect also increased with initial water content. In all the soils tested, there was no preferential loss of organic matter in the rapid-heating treatment that can explain the observed enhanced breakdown of aggregates. Conclusions Our observations indicate that soil structural degradation under low-intensity fire occurs as a result of mechanical stresses extorted by rapidly escaping steam from soil pores under rapid heating rate.</description><identifier>ISSN: 0032-079X</identifier><identifier>EISSN: 1573-5036</identifier><identifier>DOI: 10.1007/s11104-012-1408-z</identifier><identifier>CODEN: PLSOA2</identifier><language>eng</language><publisher>Dordrecht: Springer</publisher><subject>Aggregate stability ; Aggregates ; Agronomy. Soil science and plant productions ; Animal, plant and microbial ecology ; Biological and medical sciences ; Biomedical and Life Sciences ; Burns ; Chemical, physicochemical, biochemical and biological properties ; Ecology ; Forest &amp; brush fires ; Forest soils ; Fundamental and applied biological sciences. Psychology ; General agronomy. Plant production ; Gypsum ; Heating ; Horticultural soils ; Life Sciences ; Low temperature ; Organic matter ; Organic soils ; Physical properties ; Physics, chemistry, biochemistry and biology of agricultural and forest soils ; Plant Physiology ; Plant Sciences ; Pore water ; Prescribed burning ; Rangeland soils ; Regular Article ; Shrubs ; Soil aggregates ; Soil aggregation ; Soil degradation ; Soil erosion ; Soil heating ; Soil mechanics ; Soil organic matter ; Soil science ; Soil Science &amp; Conservation ; Soil sciences ; Soil stability ; Soil structure ; Soil temperature ; Soil testing ; Soil water ; Soil-plant relationships. Soil fertility ; Soil-plant relationships. Soil fertility. Fertilization. Amendments ; Soils ; Structure, texture, density, mechanical behavior. 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In contrast, controlled burns are typically managed to be low in intensity and severity. Such burns are considered benign to soil structural stability because organic matter and inorganic binding agents (e.g., gypsum) are relatively stable at such low temperatures. Recent observations at a controlled burn site in the eastern Great Basin (Nevada) showed soil aggregate breakdown found in shrub canopies where soil temperatures briefly exceeded 300 °C as well as interspaces between shrubs, where the temperatures were likely lower than beneath shrubs because of less surface biomass. These alterations cannot be explained in terms of thermal alteration of binding agents. This study was designed to test whether pressure created by rapidly vaporized pore water can cause aggregate breakdown. Methods We subjected three different sizes of aggregates (0.25-1, 1-2 and 2-4 mm) of soils derived from the eastern Great Basin burn site as well as from a forest and urban garden in California to rapid and slow (3 °C/min) heating rates. These treatments were conducted at 5 peak temperatures (75,100,125,150 and 175 °C). Results Post-burn water stability of the aggregates showed that rapid heating rate caused more pronounced degradation of aggregate stability than slow heating. Moreover, the heating-rate dependent structural degradation increased with peak temperature. For the majority of the aggregates, the effect also increased with initial water content. In all the soils tested, there was no preferential loss of organic matter in the rapid-heating treatment that can explain the observed enhanced breakdown of aggregates. Conclusions Our observations indicate that soil structural degradation under low-intensity fire occurs as a result of mechanical stresses extorted by rapidly escaping steam from soil pores under rapid heating rate.</description><subject>Aggregate stability</subject><subject>Aggregates</subject><subject>Agronomy. Soil science and plant productions</subject><subject>Animal, plant and microbial ecology</subject><subject>Biological and medical sciences</subject><subject>Biomedical and Life Sciences</subject><subject>Burns</subject><subject>Chemical, physicochemical, biochemical and biological properties</subject><subject>Ecology</subject><subject>Forest &amp; brush fires</subject><subject>Forest soils</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General agronomy. Plant production</subject><subject>Gypsum</subject><subject>Heating</subject><subject>Horticultural soils</subject><subject>Life Sciences</subject><subject>Low temperature</subject><subject>Organic matter</subject><subject>Organic soils</subject><subject>Physical properties</subject><subject>Physics, chemistry, biochemistry and biology of agricultural and forest soils</subject><subject>Plant Physiology</subject><subject>Plant Sciences</subject><subject>Pore water</subject><subject>Prescribed burning</subject><subject>Rangeland soils</subject><subject>Regular Article</subject><subject>Shrubs</subject><subject>Soil aggregates</subject><subject>Soil aggregation</subject><subject>Soil degradation</subject><subject>Soil erosion</subject><subject>Soil heating</subject><subject>Soil mechanics</subject><subject>Soil organic matter</subject><subject>Soil science</subject><subject>Soil Science &amp; Conservation</subject><subject>Soil sciences</subject><subject>Soil stability</subject><subject>Soil structure</subject><subject>Soil temperature</subject><subject>Soil testing</subject><subject>Soil water</subject><subject>Soil-plant relationships. Soil fertility</subject><subject>Soil-plant relationships. Soil fertility. Fertilization. Amendments</subject><subject>Soils</subject><subject>Structure, texture, density, mechanical behavior. 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Soil science and plant productions</topic><topic>Animal, plant and microbial ecology</topic><topic>Biological and medical sciences</topic><topic>Biomedical and Life Sciences</topic><topic>Burns</topic><topic>Chemical, physicochemical, biochemical and biological properties</topic><topic>Ecology</topic><topic>Forest &amp; brush fires</topic><topic>Forest soils</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General agronomy. Plant production</topic><topic>Gypsum</topic><topic>Heating</topic><topic>Horticultural soils</topic><topic>Life Sciences</topic><topic>Low temperature</topic><topic>Organic matter</topic><topic>Organic soils</topic><topic>Physical properties</topic><topic>Physics, chemistry, biochemistry and biology of agricultural and forest soils</topic><topic>Plant Physiology</topic><topic>Plant Sciences</topic><topic>Pore water</topic><topic>Prescribed burning</topic><topic>Rangeland soils</topic><topic>Regular Article</topic><topic>Shrubs</topic><topic>Soil aggregates</topic><topic>Soil aggregation</topic><topic>Soil degradation</topic><topic>Soil erosion</topic><topic>Soil heating</topic><topic>Soil mechanics</topic><topic>Soil organic matter</topic><topic>Soil science</topic><topic>Soil Science &amp; Conservation</topic><topic>Soil sciences</topic><topic>Soil stability</topic><topic>Soil structure</topic><topic>Soil temperature</topic><topic>Soil testing</topic><topic>Soil water</topic><topic>Soil-plant relationships. Soil fertility</topic><topic>Soil-plant relationships. Soil fertility. Fertilization. Amendments</topic><topic>Soils</topic><topic>Structure, texture, density, mechanical behavior. 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In contrast, controlled burns are typically managed to be low in intensity and severity. Such burns are considered benign to soil structural stability because organic matter and inorganic binding agents (e.g., gypsum) are relatively stable at such low temperatures. Recent observations at a controlled burn site in the eastern Great Basin (Nevada) showed soil aggregate breakdown found in shrub canopies where soil temperatures briefly exceeded 300 °C as well as interspaces between shrubs, where the temperatures were likely lower than beneath shrubs because of less surface biomass. These alterations cannot be explained in terms of thermal alteration of binding agents. This study was designed to test whether pressure created by rapidly vaporized pore water can cause aggregate breakdown. Methods We subjected three different sizes of aggregates (0.25-1, 1-2 and 2-4 mm) of soils derived from the eastern Great Basin burn site as well as from a forest and urban garden in California to rapid and slow (3 °C/min) heating rates. These treatments were conducted at 5 peak temperatures (75,100,125,150 and 175 °C). Results Post-burn water stability of the aggregates showed that rapid heating rate caused more pronounced degradation of aggregate stability than slow heating. Moreover, the heating-rate dependent structural degradation increased with peak temperature. For the majority of the aggregates, the effect also increased with initial water content. In all the soils tested, there was no preferential loss of organic matter in the rapid-heating treatment that can explain the observed enhanced breakdown of aggregates. Conclusions Our observations indicate that soil structural degradation under low-intensity fire occurs as a result of mechanical stresses extorted by rapidly escaping steam from soil pores under rapid heating rate.</abstract><cop>Dordrecht</cop><pub>Springer</pub><doi>10.1007/s11104-012-1408-z</doi><tpages>10</tpages></addata></record>
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subjects Aggregate stability
Aggregates
Agronomy. Soil science and plant productions
Animal, plant and microbial ecology
Biological and medical sciences
Biomedical and Life Sciences
Burns
Chemical, physicochemical, biochemical and biological properties
Ecology
Forest & brush fires
Forest soils
Fundamental and applied biological sciences. Psychology
General agronomy. Plant production
Gypsum
Heating
Horticultural soils
Life Sciences
Low temperature
Organic matter
Organic soils
Physical properties
Physics, chemistry, biochemistry and biology of agricultural and forest soils
Plant Physiology
Plant Sciences
Pore water
Prescribed burning
Rangeland soils
Regular Article
Shrubs
Soil aggregates
Soil aggregation
Soil degradation
Soil erosion
Soil heating
Soil mechanics
Soil organic matter
Soil science
Soil Science & Conservation
Soil sciences
Soil stability
Soil structure
Soil temperature
Soil testing
Soil water
Soil-plant relationships. Soil fertility
Soil-plant relationships. Soil fertility. Fertilization. Amendments
Soils
Structure, texture, density, mechanical behavior. Heat and gas exchanges
Water content
title Degradation of moist soil aggregates by rapid temperature rise under low intensity fire
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