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Importance of inorganic carbon in sequestering carbon in soils of the dry regions

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Abstract

The world's most populated ecoregions in the tropics are also the regions where there is a high risk of natural resources and environmental degradation. The con-sequences of this degradation are severe soil degradation, contamination of sur-face and ground waters and emission of greenhouse gases from the soil into the atmosphere. Human activities, driven by socio-economic, political and cultural fac-tors that exacerbate gaseous emissions, include conversion of lands under forest and natural vegetation to agriculture and other uses, biomass burning, lack of nutrient inputs under subsistence agricul-ture and draining of wetlands 1 . Soils in the tropics, especially those in the drier regions have low reserves of organic matter and plant nutrients. The soil carbon (C) pool composed of soil orga-nic C and soil inorganic C is not only critical for the soil to perform its produc-tivity and environmental functions, but also plays an important role in the global C cycle. The sequestration of atmosphe-ric C in the soil and biomass not only redu-ces greenhouse effect but also helps maintain or restore the capacity of the soil to perform its production and envi-ronmental functions on a sustainable basis. Thus, there is a great interest in research on sequestration of atmospheric C into the soils for maintaining or restoring soil fertility and mitigating carbon dioxide emissions to the atmosphere 1 . Calcium carbonate is a common mineral in soils of the dry regions of the world, stretching from sub-humid to arid zones. It is estimated that arid and semi-arid regions cover over 50% of the total geo-graphical area of India. The soils of these regions are calcareous in nature. Accord-ing to an estimate by the National Bureau of Soil Survey and Land Use Planning, calcareous soils occupy about 230 × 10 6 ha and constitute 69% of the total geographical area of the country 2 . Some calcareous soils also occur in the humid and per-humid zones of the country, but the occurrence of calcareous soils in the per-humid zones is as a result of strongly calcareous parent material or in young geomorphic surfaces 3 . The arid and semi-arid regions of India are dominated by calcareous Vertisols and Vertic inter-grades. Despite the dominant role that calcium carbonate plays in modifying the physi-cal, chemical and biological properties and behaviour of plant nutrients in the soil, its role in C sequestration in cal-careous soils is not well researched. The role of soil inorganic carbon (SIC) is important for sequestering C, but the mechanisms involved are not well under-stood 1 . The soils of the arid and semi-arid regions may contain two to five times more SIC than soil organic C (SOC) in the top 1 m soil layer. For example, Bhattacharya et al. 4 estimated that the SOC stock in the top 150 cm depth of the black cotton soils (Vertisols and asso-ciated soils) of Maharashtra is 171 Gg (Gg = 10 9 g) and the stock of SIC is 3051 Gg. These estimates clearly demon-strate the predominance of SIC over SOC. The SIC pool consists of primary inor-ganic carbonates or lithogenic inorganic carbonates, and secondary inorganic car-bonates or pedogenic inorganic carbo-nates. Secondary carbonates are formed through dissolution of primary carbo-nates and re-precipitation of weathering products. The reaction of atmospheric carbon dioxide (CO 2) with water (H 2 O) and calcium (Ca 2+) and magnesium (Mg 2+) in the upper horizons of the soil, leaching into the subsoil and subsequent re-precipitation results in formation of secondary carbonates and in the seque-stration of atmospheric CO 2 . The reac-tions can be represented as follows: CO 2 (g) + H 2 O = H 2 CO 3 , (1)
CORRESPONDENCE
CURRENT SCIENCE, VOL. 84, NO. 7, 10 APRIL 2003 864
Importance of inorganic carbon in sequestering carbon in soils of the
dry regions
The world’s most populated ecoregions
in the tropics are also the regions where
there is a high risk of natural resources
and environmental degradation. The con-
sequences of this degradation are severe
soil degradation, contamination of sur-
face and ground waters and emission of
greenhouse gases from the soil into the
atmosphere. Human activities, driven by
socio-economic, political and cultural fac-
tors that exacerbate gaseous emissions,
include conversion of lands under forest
and natural vegetation to agriculture and
other uses, biomass burning, lack of
nutrient inputs under subsistence agricul-
ture and draining of wetlands1.
Soils in the tropics, especially those in
the drier regions have low reserves of
organic matter and plant nutrients. The soil
carbon (C) pool composed of soil orga-
nic C and soil inorganic C is not only
critical for the soil to perform its produc-
tivity and environmental functions, but
also plays an important role in the global
C cycle. The sequestration of atmosphe-
ric C in the soil and biomass not only redu-
ces greenhouse effect but also helps
maintain or restore the capacity of the
soil to perform its production and envi-
ronmental functions on a sustainable basis.
Thus, there is a great interest in research
on sequestration of atmospheric C into
the soils for maintaining or restoring soil
fertility and mitigating carbon dioxide
emissions to the atmosphere1.
Calcium carbonate is a common mineral
in soils of the dry regions of the world,
stretching from sub-humid to arid zones.
It is estimated that arid and semi-arid
regions cover over 50% of the total geo-
graphical area of India. The soils of these
regions are calcareous in nature. Accord-
ing to an estimate by the National Bureau
of Soil Survey and Land Use Planning,
calcareous soils occupy about 230 ×
106 ha and constitute 69% of the total
geographical area of the country2. Some
calcareous soils also occur in the humid
and per-humid zones of the country, but
the occurrence of calcareous soils in the
per-humid zones is as a result of strongly
calcareous parent material or in young
geomorphic surfaces3. The arid and semi-
arid regions of India are dominated by
calcareous Vertisols and Vertic inter-
grades.
Despite the dominant role that calcium
carbonate plays in modifying the physi-
cal, chemical and biological properties
and behaviour of plant nutrients in the
soil, its role in C sequestration in cal-
careous soils is not well researched. The
role of soil inorganic carbon (SIC) is
important for sequestering C, but the
mechanisms involved are not well under-
stood1. The soils of the arid and semi-
arid regions may contain two to five times
more SIC than soil organic C (SOC) in
the top 1 m soil layer. For example,
Bhattacharya et al.4 estimated that the
SOC stock in the top 150 cm depth of
the black cotton soils (Vertisols and asso-
ciated soils) of Maharashtra is 171 Gg
(Gg = 109 g) and the stock of SIC is
3051 Gg. These estimates clearly demon-
strate the predominance of SIC over SOC.
The SIC pool consists of primary inor-
ganic carbonates or lithogenic inorganic
carbonates, and secondary inorganic car-
bonates or pedogenic inorganic carbo-
nates. Secondary carbonates are formed
through dissolution of primary carbo-
nates and re-precipitation of weathering
products. The reaction of atmospheric
carbon dioxide (CO2) with water (H2O)
and calcium (Ca2+) and magnesium
(Mg2+) in the upper horizons of the soil,
leaching into the subsoil and subsequent
re-precipitation results in formation of
secondary carbonates and in the seque-
stration of atmospheric CO2. The reac-
tions can be represented as follows:
CO2 (g) + H2O = H2 CO3, (1)
H2CO3 = H+ + HCO3 , (2)
CaCO3 + H+ = Ca2+ + HCO3 . (3)
The overall reaction that leads to the
dissolution of calcium carbonate at the
soil surface, followed by its leaching in
the soil profile, is as follows:
CO2 + H2O + CaCO3 = Ca2+
+ 2HCO3 . (4)
The pedogenic inorganic C (PIC) formed
from non-carbonate material is a sink for
C and leads to C sequestration. On the
other hand, pedogenic inorganic C formed
from calcareous material may not be
involved in C sequestration in the soil.
Thus dissolution of carbonates and lea-
ching in the soil profile may lead to C
sequestration. Leaching of bicarbonates
into the groundwater is a major mecha-
nism of SIC sequestration. The rate of C
sequestration by this mechanism may be
0.251.0 Mg C/ha/yr5. For SIC seques-
tration to take place, the groundwater is
to be unsaturated with calcium bicarbo-
nate6. The contribution of PIC from non-
carbonate material may be 50–100 kg/ha/
year6.
Enhanced primary productivity of the
vegetation and adoption of salinity con-
trol measures involving the use of gyp-
sum and organic amendments can lead to
leaching of calcium bicarbonate in the
profile under irrigation. This would result
in sequestering carbon and amelioration
of salt-affected soils7. Unlike SOC, the
role of SIC in C sequestration is not only
less researched, but also less well under-
stood. Sequestration of SIC certainly has
implications when groundwaters unsatu-
rated with calcium bicarbonate are used
for irrigation. Reconstruction of carbo-
nate fluxes in soil formed in strongly
calcareous parent material over geological
time periods suggests that this mecha-
nism could account for upward of 1 Mg
ha–1 yr–1 of SIC8. These results provide
definitive estimates of contribution that
SIC can make to C sequestration in cal-
careous soils.
It has been postulated that aridity in
the climate is responsible for the forma-
tion of pedogenic calcium bicarbonate and
this is a reverse process to the enhance-
ment in SOC. Thus increase in C seque-
stration via SOC enhancement in the soil
would induce dissolution of native calcium
carbonate and its leaching4, resulting in
SIC sequestration. Thus there may be a
synergy in SOC and SIC sequestration.
Initial estimates on SIC sequestration in
soils should stimulate future research on
its role in C sequestration for enhancing
C stock in impoverished and degraded
calcareous soils in the arid and semi-arid
regions and mitigating the greenhouse
effect.
1. Lal, R., Adv. Agron., 2002, 76, 130.
2. Velayutham, M., Mandal, D. K., Mandal,
C. and Sehgal, J. L., National Bureau of
CORRESPONDENCE
CURRENT SCIENCE, VOL. 84, NO. 7, 10 APRIL 2003 865
Soil Survey and Land Use Planning Bulle-
tin No. 35, NBSS and LUP, Nagpur,
1999.
3. Pal, D. K., Dasog, S., Vadivelu, S., Ahuja,
R. L. and Bhattacharya, T., in Global Cli-
mate Change and Pedogenic Carbontes (eds
Lal, R. et al.), CRC/Lewis Publishers,
Boca Raton, Florida, 2000, pp. 149185.
4. Bhattacharya, T., Pal, D. K., Velayutham,
M., Chandran, P. and Mandal, C., Clay Res.,
2001, 20, 1120.
5. Wilding, L. P., in Carbon Sequestration in
Soils: Science, Monitoring and Beyond
(eds Rosenberg, N. J. et al.), Battelle Press,
Columbus, 1999, pp. 146149.
6. Nordt, L. C., Wilding, L. P. and Drees,
L. R., in Global Climate Change and
Pedogenic Carbonates (eds Lal, R. et al.),
CRC/Lewis Publishers, Boca Raton,
Florida, 2000, pp. 4364.
7. Gupta, R. K. and Abrol, I. P., in Advances
in Soil Science: Soil Degradation (eds Lal,
R. and Stewart, B. A.), Springer-Verlag,
Berlin, 1990, pp. 223288.
8. Izaurralde, R. C., Rosenberg, N. J. and
Lal, R., Adv. Agron., 2001, 70, 175.
K. L. SAHRAWAT
International Crops Research Institute
for the Semi-Arid Tropics,
Patancheru 502 324, India
e-mail: klsahrawat@yahoo.com
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... The Ca 2+ and Mg 2+ in irrigation water and the Ca 2+ and Mg 2+ produced by the SIC dissolution will be leached with surplus irrigation water. Because of evapotranspiration, Ca 2+ and Mg 2+ will recombine deeper in the soil profile with CO 2 to form PIC (Pan, 1999), and this will cause SIC accumulation in the deeper soil (Entry et al., 2004;Sahrawat, 2003). The restored arable land in our study is located in a humid region of Germany, where the annual rainfall is moderate and evenly distributed. ...
... The topsoil SIC loss (0.61 Mg C ha − 1 y − 1 ) in this reclaimed arable land in Germany exceeds values measured for carbonate-containing agricultural soils in China; although, China is recognized as a country with high N fertilizer application rates (Potter et al., 2010) that are at least 2-3 times those in Germany (Löw et al., 2021). We speculate that there are two main reasons for this: (1) the SIC content in the arable soil in our study was twice that at the beginning of restoration in Chinese carbonate soils (~6-8 g C kg − 1 soil) (Bughio et al., 2015;Bughio et al., 2017;Zhao et al., 2022); and (2) in the arid and semi-arid regions of China, part of the CO 2 produced after carbonate decomposition will be bound again in the form of PIC (Bughio et al., 2015;Entry et al., 2004;Sahrawat, 2003). However, in our study, almost all of the carbonate present in the surface soil of the reclaimed arable land was decomposed to CO 2 and released to the atmosphere. ...
Article
Replanting of mining soils is necessary for utilizing soil resources and increasing cultivated land areas. However, limited information exists on the long-term temporal trends of carbon accrual in agricultural systems containing carbonate-rich soil material. We examined changes in soil organic carbon (SOC), soil inorganic carbon (SIC), and total carbon (TC) stocks in an agricultural soil containing carbonate over a 62-year recultivation chronosequence. The most critical differences in the SOC, SIC, and TC stocks were observed in the 0–30 cm soil layer. The results revealed that the SOC stock increased rapidly during the first 10–20 years, but only slowly thereafter. The SIC stock decreased over 62-year from approximately 40 Mg C ha⁻¹ to 2 Mg C ha⁻¹. According to soil δ¹³CTC data, the SIC to TC ratio decreased from 83% (year 0) to 7% (year 62). Overall, the average sequestration rates were 0.30 Mg C ha⁻¹ y⁻¹ for SOC and −0.61 Mg C ha⁻¹ y⁻¹ for SIC over the 62 years after recultivation. Total carbon ultimately declined by approximately 19.5 Mg C ha⁻¹ in recultivated carbonate soils. Topsoil SOC model (Rothamsted Carbon Model) outputs predicted an equilibrium value of 38.6 Mg C ha⁻¹ after 197 years, which was less than the SIC stock lost in the first 70 years. Therefore, an overall TC increase in these carbonate-containing agricultural soils will only occur (i) during the initial rapid SOC sequestration accumulation phase (first 20 years of recultivation); and (ii) after the soils are fully decalcified (after ∼62 years), but when SOC still slowly increases before SOC stocks reached full equilibrium (after ∼197 years). However, compared with starting TC stocks, when we consider periods over a semicentennial and beyond, we will likely lose more TC than we gain in these recultivated agricultural soils if there are no additional TC sequestration measures.
... In recent times, though the role of SOC (Bhattacharyya et al., 2000) and inorganic C (Sahrawat, 2003) have been highlighted in sequestering C in drylands, relatively little data are available on it. Soil C content mostly depends on, climate, soil type, and land use (Wani et al.,2003). ...
... In semi-arid to sub humid zones relatively less amount of water available for chemical weathering, pedogenic carbonates are formed. In recent times, though the role of SOC (Bhattacharyya et al., 2000) and inorganic C (Sahrawat, 2003) have been highlighted in sequestering C in arid and semi-arid climate comparatively available data are less on SIC. ...
... In recent times, though the role of SOC (Bhattacharyya et al., 2000) and inorganic C (Sahrawat, 2003) have been highlighted in sequestering C in drylands, relatively little data are available on it. Soil C content mostly depends on, climate, soil type, and land use (Wani et al.,2003). ...
... In semi-arid to sub humid zones relatively less amount of water available for chemical weathering, pedogenic carbonates are formed. In recent times, though the role of SOC (Bhattacharyya et al., 2000) and inorganic C (Sahrawat, 2003) have been highlighted in sequestering C in arid and semi-arid climate comparatively available data are less on SIC. ...
Book
A study was undertaken across different agro-climatic zones(ACZ)of Karnataka, with an objective to assess the vertical distribution of soil carbon stock in coconut and arecanut plantations. The higher soil carbon stock was found in arecanut (2.71 kg m-2) as compared to coconut (2.32 kg m-2) plantations. Significantly higher soil carbon stock was observed in hilly zone(3.25kg m-2) followed by southern transitional zone(2.52kg m-2), coastal zone (2.51kg m-2), southern dry zone (2.3kg m-2), and eastern dry zone(1.96kg m-2). Irrespective of crops and zones, arecanut soils had higher carbon content than coconut soils. The pooled data revealed that surface (0-30cm) soil depth had 35.7 and 36.4 per cent higher carbon stock in arecanut and coconut, respectively as compared to sub-surface soil depth. In sub-surface soil (30-120 cm), 64.3 and 63.6 per cent soil carbon stock was noticed in arecanut and coconut, respectively. Significantly (p<0.05) higher soil carbon stock was recorded within 0–30cm (3.63kg m-2) soil depth and it was found to decline with depth. The interaction effect between crops, zones and depthswas found to be significant. However, zone and depth (Z×D) crop and depth (C×D), crop and zone (C×Z), crop zone and depth (C×Z×D) for soil organic carbon in coconut and arecanut crops across different ACZ was found to be non-significant. Significant difference was observed for dehydrogenase (DHA), alkaline phosphatase (ALP) and acid phosphatase (ACP) in arecanut and coconut soils but no difference was observed for available N, P2O5 and K2O. A significant positive correlation was observed for different carbon pools with pH, clay, CEC, available N, P2O5 and K2O, DHA, ALP and ACP activity and negative correlation with sand and bulk density of soil. In general low management attained less soil carbon status in whole soil profile (0-120 cm) than the high level management in both crops representing all agro climatic zones.
... The excessive production of calcium carbonate (CaCO 3 ) caused by too much salt and sodicity in the soil has a negative impact on soil characteristics . In the arid-semiarid region, the amount of soil inorganic carbon (SIC) is twice to thrice more than SOC up to a depth of 1 m (Sahrawat 2003). India has calcareous soil covering almost 229 million hectares, and SIC contributing to C storage essential for maintaining soil nutrient status (Sahrawat et al. 2005). ...
Chapter
Land use changes from forestry to agriculture result in an increase in the mineralization of soil organic matter (SOM) and a decrease in woody biomass, which serves as a source of carbon dioxide (CO2). It is imperative to adopt mechanisms that act as carbon sinks in order to reduce atmospheric CO2 emissions emanating from the sources through recycling into terrestrial pool. To minimize the negative effects of climate change on the quality and quantity of soil resources and land degradation, an increase in food production must always be supported by sustainable management of agricultural land. As farming, forestry, and land use change can contribute for up to 25% of human-induced GHG emissions, these practices must be adopted in order to decline the climate change effects on agriculture. The potential for soil C storage in India is significant, with estimates ranging from 39 to 49 (44 ± 5) Tg C year−1 on average for restoring damaged ecosystems and soils, preventing erosion, and implementing recommended management practices (RMPs) on agricultural soils and secondary carbonates. In this chapter, we discuss the functions and effects of these various GHGs, agricultural farming technologies that can be used to reduce GHG emissions under different cropping systems and their role on carbon sequestration under different land uses, decarbonization strategies towards meeting the growing demand for carbon-free agriculture, as well as the potential to sequester C under diverse ecological conditions for sustainability of soil resources.
... The development of secondary carbonates and the Carbon Management in Rainfed Agroecosystem sequestration of atmospheric CO 2 occur as a result of the interaction of atmospheric CO 2 with water (H 2 O) and calcium (Ca 2+ ) in the top layers of soil, leaching into the subsurface, and subsequent reprecipitation. Because of this, most profiles revealed that deeper layers contained more inorganic C than surface soils (Sahrawat, 2003). It will continue to be a possible hazard for C sequestration in tropical soils of the Indian subcontinent given the current situation of varying climatic factors, such as temperature and annual rainfall in some areas of the country. ...
Article
Full-text available
Rainfed agriculture, which accounts for about 40% of India’s food basket, plays a critical role in ensuring the country’s food security and in achieving sustainable development goals (SDGs). Soil organic carbon (SOC) is a critical factor that determines soil health and crop productivity. Declining SOC content in rainfed ecosystems has become a serious challenge to sustainable rainfed agriculture. Shallow soils, soil erosion, poor soil fertility, low biomass output and poor residue recycling in the soil-crop system are common features of rainfed agriculture. Uncertainty of rainfall, frequent droughts and intense rains and overall fragile ecosystem results in poor carrying capacity of rainfed agriculture systems. Whatever little biomass is added to soil in these environments is rapidly decomposed, making soil carbon management a serious challenge. Large part of rainfed agriculture in India is monocropped for a short period, leaving a long fallow period during which the land has little or no vegetative cover, making it vulnerable to loss of soil carbon due to various forms of erosion. The two options available in overall carbon management in rainfed agriculture are i) To maintain current levels of SOC and ii) To enhance the SOC with various best agriculture practices. Carbon sequestration, the process of transferring photosynthetically fixed carbon into soil profile, contributes to climate change mitigation besides maintaining or improving SOC. Since SOC is a critical requirement for soil health and overall sustainability of rainfed ecosystems, various location specific technological options need to be implemented with active community participation. In this article, the carbon sequestration processes, pathways and strategies for overall soil health improvement and agriculture productivity are discussed.
... SOM forms a major pool of SOC. SOC governs the global carbon cycle, making the soil productive and regulating the physical, chemical and biological properties of the soil (Sahrawat 2003, Woomer et al. 1994. The SOM and SOC showed a similar trend as soil moisture and ST except for Chakrata, where SOM and SOC contents were lower under the soil with moss cover than soil without moss cover in monsoon season. ...
Article
Full-text available
Mosses are one of the most important and dominant plant communities, especially in the temperate biome, and play a significant role in ecosystem function and dynamics. They influence the water, energy and element cycle due to their unique ecology and physiology. The present study was undertaken in three different temperate forest sites in the Garhwal Himalayas, viz., Triyuginarayan (Kedarnath Wildlife Sanctuary (KWLS)), Chakrata, and Kanasar forest range. The study was focused on understanding the influence of mosses on soil physical properties and nutrient availability. Different physico-chemical properties were analysed under two different substrata, that is, with and without moss cover in two different seasons, viz., monsoon and winter. We observed mosses to influence and alter the physical properties and nutrient status of soil in both seasons. All soil physical and chemical properties, except magnesium, showed significant difference within the substrates, among all the sites and across the two seasons. Besides the soil characteristics underneath the moss vegetation, the study also highlights the diversity of mosses found in the area. Mosses appear to create high nutrient microsites via a high rate of organic matter accumulation and retain nutrients for longer periods thus, maintaining ecosystem stability.
... Soil carbon pool comprises of two components: Soil organic carbon (SOC) and soil inorganic carbon (SIC). The SOC pool includes highly active humus to relatively inert charcoal C. The SIC pool includes the elemental C and carbonate minerals (eg: gypsum, calcite, dolomite, aragonite and siderite) (Sahrawat, 2003). The high temperature coupled with high degree of diurnal variation hastened the organic matter decomposition in the soil and quit possible to an increased emission of CO2 to the atmosphere when it accompanied with frequent disturbance of top soil by way of tillage operations. ...
... It has been postulated that aridity in the climate is responsible for the formation of pedogenic calcium carbonate and this is a reverse process to the enhancement in SOC. Thus, increase in C sequestration via SOC enhancement in the soil would induce dissolution of native calcium carbonate and the leaching of SIC would result in carbon sequestration (Sahrawat 2003). In the present scenario of differing climatic parameters such as temperature and annual rainfall in some areas of the country, it will continue to remain as a potential threat for carbon sequestration in tropical soils of the Indian subcontinent. ...
Article
Full-text available
45th Dr. R.V. Tamhane Memorial Lecture of Indian Society of Soil Science "Soil Carbon Sequestration: Research, Technology and Policy Implementation Needs in India"
Chapter
In dryland soil ecosystem, soil inorganic carbon (SIC) is a hidden treasure, which refers to the parent rock carbonate formed during weathering process of silicate carbon, commonly occurring in the form of calcite or dolomite. Generally, in dryland regions, high evapotranspiration along with moisture deficient situation promotes formation of SIC. Apart from its (SIC) potential as atmospheric CO2 sink, it may play an indirect positive role in soil aggregation through the interaction between carbonates and soil organic matter. During the amelioration of sodic soils in dryland regions, SIC acts as a modifier or ecosystem engineer. Anthropogenic activities including unsustainable land use practices and injudicious use of water are the major driving forces for increasing the coverage of global dry lands. The largest accumulation of carbonates occurs in the soils of arid and semiarid areas because of the conducive environment created under dryland ecosystem due to calcification and formation of secondary carbonates. As a result, SIC plays an important role in soil C sequestration and global C cycle. Soil erosion and arid conditions coupled with climate change (drought and heat waves) are posing challenges to dry lands, which strongly influence the carbon cycle due to erosion-induced loss of carbon. Therefore, to unlock the potential of dryland SIC and climate change mitigation, desertification must be controlled to achieve land degradation neutrality.
Chapter
Drylands play a significant role in the global biogeochemical cycling of nutrients (carbon, nitrogen, and phosphorus) through abiotic (geological, atmospheric, and hydrological) and biotic (animals, insects, plants, and microorganisms) pathways. They act as important carbon reservoirs and are estimated to store over 30% of the global soil organic carbon reserve. However, nitrogen and phosphorus availability are major limiting factors for biological activity in these oligotrophic environments, affecting community structure, species diversity, and other ecosystem functions (e.g., nutrient cycling and productivity). Nutrient cycling in desert soils is primarily achieved by plant and microbial communities, in particular soil microbial communities, biological soil crusts, hypoliths, and endoliths. Drylands are highly sensitive and prone to disturbance and land degradation resulting from desertification. Changes induced by climate (e.g., precipitation and temperature), structural and temporal variability (nutrient accumulation and distribution of minerals, seasonal variation, and differences in turnover rates), and human activity often alter nutrient cycles that negatively affect the structure and function of these ecosystems (e.g., decreasing carbon storage capacity, increasing NOx emissions, and reducing phosphorus cycling). Comprehending the extent, nature, magnitude, and reversibility of such changes is urgent, given the global importance of drylands in terms of carbon sequestration, greenhouse gas emissions, ecology and biodiversity, and human habitation.
Book
The purpose of Advances in Soil Science is to provide a forum for leading scientists to analyze and summarize the available scientific information on a subject, assessing its importance and identifying additional research needs. A wide array of subjects has been addressed by authors from many countries in the initial ten volumes of the series. The quick acceptance of the series by both authors and readers has been very gratifying and confirms our perception that a need did exist for a medium to fill the gap between the scientific journals and the comprehensive reference books. This volume is the first of the series devoted entirely to a single topic­ soil degradation. Future volumes will include both single-topic volumes as well as volumes containing reviews of different topics of soil science, as in the case of the first ten volumes. There are increasing concern and attention about managing natural re­ sources, particularly soil and water. Soil degradation is clearly one of the most pressing problems facing mankind. Although the spotlight regarding soil degradation in recent years has focused on Africa, concern about the degradation of soil and water resources is worldwide. The widespread con­ cern about global environmental change is also being linked to severe problems of soil degradation. Therefore, we are indeed pleased that the first volume of the series devoted to a single topic addresses such an impor­ tant issue. The current volume is also the first of the series involving a guest editor.
Article
The tropics cover 8.2 billion hectares or approximately 40% of the world's land area. These regions are characterized by a large portion of the world's rapidly increasing population, high risks of soil and environmental degradation because of harsh climate and resource-poor farmers, and rapid decomposition of soil organic matter because of continuously high temperatures. Predominant soils of the tropics include Oxisols, Aridisols, Ultisols, and Alfisols. Soil and ecosystem degradation lead to emissions of greenhouse gases (e.g., carbon dioxide, methane, and nitrous oxide) into the atmosphere. Anthropogenic activities that exacerbate gaseous emissions include deforestation and biomass burning, low- or no-input subsistence agriculture, plowing, drainage of wetlands, and elimination or shortening of restorative fallows. Soils of the tropics contain about 496 Pg of soil organic carbon (SOC) or 32% of the global pool. The historic loss of the SOC pool, due to land-use change and cultivation, may be 17–39 Pg compared with the global loss of 66–90 Pg. If 60–80% of the SOC lost can be resequestered through land-use change and adoption of recommended management practices, the potential of SOC sequestration in the tropics is 12–27 Pg over a 25-to 50-year period. Important strategies of SOC sequestration include reduction in emission of greenhouse gases and sequestration of carbon (C) in biomass and soils. The potential of C sequestration in soils and biomass of the tropics is estimated at 10.0–25.0 Pg by effective erosion control, 5.7–10.8 Pg through restoration of degraded soils and ecosystems, 58–115 Pg through biofuel offset, 2.2–4.1 Pg through adoption of recommended practices on croplands, and 6.0–12.0 Pg through adoption of recommended practices on grazing lands. Of this, the potential of SOC sequestration is only 13.9–26.9 Pg over the 50-year period. Realization of this vast potential is a challenge for researchers, land managers, and policymakers.
  • T Bhattacharya
  • D K Pal
  • M Velayutham
  • P Chandran
  • C Mandal
Bhattacharya, T., Pal, D. K., Velayutham, M., Chandran, P. and Mandal, C., Clay Res., 2001, 20, 11–20.
  • R C Izaurralde
  • N J Rosenberg
  • R Lal
Izaurralde, R. C., Rosenberg, N. J. and Lal, R., Adv. Agron., 2001, 70, 1-75.