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Summary This chapter gives an overview of the distribution, classification and main mineralogical, physical and chemical properties of volcanic soils. It discusses their land use potential and limitations for various uses, ranging from engineering to agricultural, rangeland and forestry uses, as well as to environmental considerations. Many volcanic soils have excellent physical properties that make them highly desirable for a wide range of uses. Chemically, they suffer from a high phosphate retention, and they may be limiting in K and some micronutrients. Nevertheless, these soils are amongst the most fertile lands in the world and are, therefore, very intensively cultivated, even if the users are aware of the risks of volcanic outbursts.
... Ashfalls influence soil formation [4,5] and vegetation [34,35] (volcanic flanks often have no vegetation cover). Major volcanoes in Kamchatka have maximum altitude in the peninsula, level difference and the ruggedness number reach their maximum there, due to the processes of relief reformation. ...
... Volcanic activity particularly affects water runoff and suspended sediment yield variability in the Kamchatsy Krai territory. Active volcanoes are prevalent-there are 42 in Kamchatka [2]-and the radius of ash trails during their strongest eruptions can exceed 2000 km [3], which causes a large amount of friable volcanic deposits [4,5] (up to several tens of thousands of tons per km 2 ) to enter the surface of river basins during eruptions. After the eruptions, the flanks of volcanoes can affect surface flow. ...
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Volcanic soils cover 1% of the Earth's surface but support 10% of the world's population. They are among the most fertile soils in the world, due to their excellent physical properties and richness in available nutrients. The major limiting factor for plant growth in volcanic soils is phosphate fixation, which is mainly attributable to active species of aluminium and iron. The sorption and desorption of phosphate is studied on the surface horizons of two African agricultural soils, a silandic Andosol (Rwanda) and a vitric Andosol (São Tomé and Principe). Both soils are slightly acid. The silandic Andosol is rich in active aluminium forms, while the vitric Andosol has high amounts of crystalline iron and aluminium oxides. Sorption isotherms were determined by equilibrating at 293K soil samples with phosphate solutions of concentrations between 0 and 100 mg P L −1 in NaNO 3 ; phosphate was determined by visible spectrophotometry in the equilibrium solution. To study desorption, the soil samples from the sorption experiment were equilibrated with 0.02 M NaNO 3. The isotherms were adjusted to mathematical models. In almost all the concentration range, the adsorption of phosphate by the silandic Andosol was greater than 90% of the amount added, being lower in the vitric Andosol but always higher than 65%. The high sorption by the silandic Andosol is attributed to its richness in non-crystalline Fe and Al, while in the vitric Andosol crystalline iron species seem to play a relevant role in the adsorption. The sorption isotherms of both soils fitted to the Temkin model, the adjustment to the Langmuir or Freundlich models being unsatisfactory; throughout the range studied, the sorption increases with increasing phosphorus concentration, a maximum sorption is not predictable (as occurs when the sorption is adjusted to the Langmuir model). For an added P concentration of 100 mg L −1 (3.2 mmol L −1), the sorption is 47.7 µmol P g −1 in the silandic Andosol and 41.6 µmol P g −1 in the vitric Andosol. The desorption is low and the comparison of the sorption and desorption isotherms reveals a pronounced hysteresis, that is, the irreversibility of the sorption. The high phosphate sorption and its irreversibility are comparable to those published for other volcanic soils with high contents of allophane, active aluminium and free iron. The strong phosphate adsorption is a serious limiting factor for plant growth, which requires a careful management of phosphorus fertilization.
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Large quantities of wastewater are generated from municipal and industrial sources in New Zealand. More stringent discharge standards and recent improvements in wastewater treatment technology have contributed to the production of large quantities of solid residuals. Increasing public, cultural, and regulatory pressures to protect water quality have resulted in significant interest in applying residuals to plantation forests. In a well-managed land application site, the forest ecosystem can efficiently handle organic contaminants and recycle nutrients provided through the residuals, resulting in significant increase in plant growth. Due to large variations in characteristics of different residuals, land application system design must be tailored to match a particular residual with the assimilation capacities of a particular soil–plant system. In New Zealand, many wastewater irrigation systems are employed in forested land as an alternative treatment of liquid residuals. In recent years, large-scale forested land application of municipal and pulp and paper industrial solid residuals have also increased as a preferred alternative to landfilling. It has been suggested that natural abundance of ¹⁵N can be used to trace the fate of residual-derived N in the ecosystems. This technique can resolve one of the main environmental concerns associated with application of residuals in forested land, namely nitrate leaching. Intensive research indicates that significant economic and social benefits can be achieved with minimal adverse impact on the receiving environment. This paper provides an overview of the research issues associated with application of residuals on forested soils in New Zealand, such as sustainability, beneficial effects, and potential adverse impacts on soil and environmental quality. Performances of 4 case studies, representing application of 2 liquid residuals and 2 solid residuals to forested soils in New Zealand, are discussed.
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Long-term application of wastewater adds large amounts of carbon (C), nitrogen (N), and phosphorus (P) to soils, and their effects on soil quality are not fully known. We compared the distribution of C, N, P, and Olsen P in the top 0.75 m of an allophanic soil after 22 years irrigation with dairy factory effluent with that in a non-irrigated soil. Earthworm species, biomass and distribution, microbial biomass, microbial activity, and relative use of substrates were measured to evaluate the contribution of biological processes to cycling and redistribution of total C. Total C did not differ between irrigated and non- irrigated soil, although there was less total C in the 0–0.1 m layer and more total C at 0.1–0.5 m in the effluent-irrigated soil. Microbial biomass C and basal respiration activity were increased by 4- and 1.6- fold, respectively, in the 0–0.1 m layer of the irrigated soil. Measurements of relative use of substrates indicated that the greater microbial biomass in the effluent-irrigated soil was supported by the inputs of available C (particularly lactose) in the effluent rather than by greater decomposition of the organic C in the soil. Irrigation increased total N storage by 2.1 t/ha and total P was increased by 11.5 t/ha. Most of the increase in total N occurred in the 0.1–0.5 m layers, whereas total P was greater at all depths. Olsen P also increased at all depths by 1.3- to 23-fold. Approximately 8% of the N and 91% of the P applied during the past 22 years was stored in the 0–0.75 m layer of the profile, with the potential for further P storage. Effluent irrigation increased the total soil nutrient stores, without detrimental effects on total C storage. Changes in nutrient distribution at the irrigated site can be partially attributed to leaching and the dominance (155 g/m² ) of the earthworm Aporrectodea longa, which forms permanent burrows to lower depths.
A book dedicated to the morphology, genesis, classification, mineralogy, chemical and physical characteristics, productivity and utilization of volcanic ash soils
  • Amsterdam Elsevier
Elsevier, Amsterdam. [ A book dedicated to the morphology, genesis, classification, mineralogy, chemical and physical characteristics, productivity and utilization of volcanic ash soils.]
Distribution and Classification of Volcanic Ash Soils [This paper gives a broad review of the different systems used to classify volcanic soils
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Takahashi, T. and Shoji, S. (2002). Distribution and Classification of Volcanic Ash Soils. Global Environmental Research 6 : 83-97. [This paper gives a broad review of the different systems used to classify volcanic soils.]
Andisols of New Zealand and Australia [A review paper summarizing the classification and use of the volcanic soils in New Zealand with a small area near Mt
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  • D J Palmer
Lowe, D.J. and Palmer, D.J. (2005). Andisols of New Zealand and Australia. Journal of Integrated Field Science 2 (Field Science Center, Graduate School of Agricultural Science, Tohoku University) : 39-65. [A review paper summarizing the classification and use of the volcanic soils in New Zealand with a small area near Mt. Gambier in Australia.]
Use of Tephra for Removal of Dissolved Inorganic Phosphate from Sewage Effluent [A seminal paper on the use of the high phosphate retention of allophane in volcanic soils to remove phosphate from effluents
  • J C Ryden
  • J K Syers
Ryden, J.C. and Syers, J.K. (1975). Use of Tephra for Removal of Dissolved Inorganic Phosphate from Sewage Effluent. New Zealand Journal of Science 18 (1) : 3-16. [A seminal paper on the use of the high phosphate retention of allophane in volcanic soils to remove phosphate from effluents.]
The Andisol Proposal International Committee on Andisols: Final Report
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Smith, G.D. (1978). The Andisol Proposal. Republished in: Leamy, M.L., Kinloch, D.I. and Parfitt, R.L., eds. (1990). International Committee on Andisols: Final Report. Technical Monograph No. 20. Soil Management Support Services, Washington D.C.), 16pp. [This publication was the key publication that led to the establishment of ICOMAND, charged with reviewing the status of volcanic soils within Soil Taxonomy (1975).]
Soil Map of the WorldNow available as a CD-Rom). [This publication details the classification and distribution of the volcanic soils of the world
  • Fao Unesco
FAO/UNESCO (1974). Soil Map of the World. Volume 1. Legend. UNESCO Press, Paris.(Now available as a CD-Rom). [This publication details the classification and distribution of the volcanic soils of the world.]
Proceedings of the Fourth International Classification Workshop, Rwanda 2 to 12
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Beinroth, F.H., Neel, H. and Eswaran, H., eds. (1981). Proceedings of the Fourth International Classification Workshop, Rwanda 2 to 12 June 1981. Part 1: Papers. 518 pp. [Papers within this workshop include information on the volcanic soils of Rwanda, Cameroon, Central and South America, and Hawaii.]
Volcanic-ash Soils in New Zealand. D.S.I.R. Information series, 65. 39 p. [A review publication designed for the general public, detailing the volcanic soils of New Zealand
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Gibbs, H.S. (1968). Volcanic-ash Soils in New Zealand. D.S.I.R. Information series, 65. 39 p. [A review publication designed for the general public, detailing the volcanic soils of New Zealand.]