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In [[geotechnical engineering]], '''soil structure''' describes the arrangement of the solid parts of the [[soil]] and of the [[Pore space in soil|pore space]] located between them. It is determined by how individual soil granules clump, bind together, and [[Soil aggregate stability|aggregate]], resulting in the arrangement of soil pores between them. Soil has a major influence on water and air movement, [[Soil microbiology|biological activity]], [[root]] growth and [[seedling]] emergence. There are several different types of soil structure. It is inherently a dynamic and complex system that is affected by different factors.
In [[geotechnical engineering]], '''soil structure''' describes the arrangement of the solid parts of the [[soil]] and of the [[Pore space in soil|pore space]] located between them. It is determined by how individual soil granules clump, bind together, and [[Soil aggregate stability|aggregate]], resulting in the arrangement of soil [[Pore space in soil|pores]] between them. Soil has a major influence on water and air movement, [[Soil microbiology|biological activity]], [[root]] growth and [[seedling]] emergence. There are several different types of soil structure. It is inherently a dynamic and complex system that is affected by different biotic and abiotic factors.<ref>{{cite journal |last1=Bronick |first1=C.J. |last2=Lal |first2=Rattan |title=Soil structure and management: a review |journal=Geoderma |date=January 2005 |volume=124 |issue=1–2 |pages=3–22 |doi=10.1016/j.geoderma.2004.03.005 |url=https://www.academia.edu/72307009 |access-date=13 June 2025 }}</ref>


== Overview ==
== Overview ==
Soil structure describes the arrangement of the solid parts of the soil and of the pore spaces located between them (Marshall & Holmes, 1979).<ref name="Dexter1988">{{cite journal |last1=Dexter|first1=A.R.|title=Advances in characterization of soil structure |journal=Soil and Tillage Research|date=June 1988 |volume=11|issue=3–4|pages=199–238|doi=10.1016/0167-1987(88)90002-5|bibcode=1988STilR..11..199D }}</ref> Aggregation is the result of the interaction of soil particles through rearrangement, flocculation and cementation. It is enhanced by:<ref name="Dexter1988"/><ref>{{cite journal|last1=Masoom |first1=Hussain|last2=Courtier-Murias|first2=Denis |last3=Farooq |first3=Hashim|last4=Soong|first4=Ronald|last5=Kelleher|first5=Brian P.|last6=Zhang |first6=Chao|last7=Maas |first7=Werner E. |last8=Fey|first8=Michael|last9=Kumar|first9=Rajeev |last10=Monette|first10=Martine|last11=Stronks|first11=Henry J. |last12=Simpson |first12=Myrna J.|author-link12=Myrna Simpson|last13=Simpson|first13=André J.|title=Soil Organic Matter in Its Native State: Unravelling the Most Complex Biomaterial on Earth|journal=Environmental Science & Technology|date=16 February 2016 |volume=50 |issue=4 |pages=1670–1680 |doi=10.1021/acs.est.5b03410|pmid=26783947|bibcode=2016EnST...50.1670M}}</ref> the precipitation of oxides, hydroxides, carbonates and silicates; the products of biological activity (such as [[biofilms]], [[Hypha|fungal hyphae]] and [[glycoproteins]]); ionic bridging between negatively charged particles (both clay minerals and organic compounds) by multivalent cations; and interactions between organic compounds ([[hydrogen bonding]] and [[hydrophobic]] bonding).
Soil structure describes the arrangement of the solid parts of the soil and of the pore spaces located between them.<ref name="Marshall 1996">{{cite book |last1=Marshall |first1=Theo John |last2=Holmes |first2=John Winspere |last3=Rose |first3=Calvin W. |year=1996 |title=Soil physics |edition=3rd |location=Cambridge, United Kingdom |publisher=[[Cambridge University Press]] |url=https://fr.1lib.sk/book/17121290/0c3a95 |access-date=10 June 2025 }}</ref><ref name="Dexter1988">{{cite journal |last1=Dexter |first1=Anthony Roger |title=Advances in characterization of soil structure |journal=Soil and Tillage Research |date=June 1988 |volume=11 |issue=3–4 |pages=199–238 |doi=10.1016/0167-1987(88)90002-5 |bibcode=1988STilR..11..199D |url=https://fr.1lib.sk/book/34161697/b00cc9 |access-date=10 June 2025 }}</ref> Aggregation is the result of the interaction of soil particles through rearrangement, [[flocculation]] and [[Cementation (geology)|cementation]]. It is enhanced by:<ref name="Dexter1988"/><ref>{{cite journal |last1=Masoom |first1=Hussain |last2=Courtier-Murias |first2=Denis |last3=Farooq |first3=Hashim |last4=Soong |first4=Ronald |last5=Kelleher |first5=Brian P. |last6=Zhang |first6=Chao |last7=Maas |first7=Werner E. |last8=Fey |first8=Michael |last9=Kumar |first9=Rajeev |last10=Monette |first10=Martine |last11=Stronks |first11=Henry J. |last12=Simpson |first12=Myrna J. |author-link12=Myrna Simpson |last13=Simpson |first13=André J. |title=Soil organic matter in its native state: unravelling the most complex biomaterial on Earth |journal=[[Environmental Science & Technology|Environmental Science and Technology]] |date=16 February 2016 |volume=50 |issue=4 |pages=1670–80 |doi=10.1021/acs.est.5b03410|pmid=26783947 |bibcode=2016EnST...50.1670M |url=https://fr.1lib.sk/book/81286326/740889 |access-date=10 June 2025 }}</ref> the precipitation of [[Oxide|oxides]], [[hydroxide]]s, [[Carbonate|carbonates]] and [[silicate]]s; the products of biological activity (such as [[biofilms]], [[Hypha|fungal hyphae]] and [[glycoproteins]]); ionic [[Bridging ligand|bridging]] between [[negatively charged]] particles (both [[Clay mineral|clay minerals]] and organic compounds) by [[multivalent]] [[cations]]; and interactions between organic compounds ([[hydrogen bonding]] and [[hydrophobic]] bonding).


The quality of soil structure will decline under most forms of [[Tillage|cultivation]]—the associated mechanical mixing of the soil compacts and shears aggregates and fills pore spaces; it also exposes organic matter to a greater rate of decay and [[oxidation]].<ref>Young, A &amp; Young R 2001, ''Soils in the Australian landscape'', Oxford University Press, Melbourne. {{page needed|date=January 2018}}</ref> A further consequence of continued cultivation and traffic is the development of [[soil compaction|compacted]], impermeable layers or 'pans' within the profile.
The quality of soil structure will decline under most forms of [[Tillage|cultivation]]; the associated mechanical mixing of the soil compacts and shears aggregates and fills pore spaces;<ref>{{cite journal |last=Skvortsova |first=Elena Borisovna |title=Changes in the geometric structure of pores and aggregates as indicators of the structural degradation of cultivated soils |journal=Eurasian Soil Science |date=November 2009 |volume=42 |issue=11 |pages=1254–62 |doi=10.1134/S1064229309110088 |url=https://fr.1lib.sk/book/43073866/bca2cc |access-date=10 June 2025 }}</ref> it also exposes organic matter to a greater rate of decay and [[oxidation]].<ref>{{cite journal |last1=Golchin |first1=Ahmad |last2=Clarke |first2=Paris |last3=Oades |first3=J. Malcolm |last4=Skjemstad |first4=Jan O. |title=The effects of cultivation on the composition of organic-matter and structural stability of soils |journal=[[Australian Journal of Soil Research]] |date=December 1995 |volume=33 |issue=6 |pages=975–93 |doi=10.1071/SR9950975 |url=https://fr.1lib.sk/book/74834359/6d7e6d |access-date=10 June 2025 }}</ref> A further consequence of continued cultivation and traffic is the development of [[soil compaction|compacted]], impermeable layers or [[Hardpan|hardpans]] within the [[soil profile]].<ref>{{cite book |last1=Reyes |first1=Alam Ramirez |last2=Heitman |first2=Josh |last3=Vepraskas |first3=Michael |last4=Ozlu |first4=Ekrem |year=2023 |chapter=Soil management practices to reduce hardpans and compaction in sandy soils of North Carolina, USA |title=Sandy soils |editor1-last=Hartemink |editor1-first=Alfred E. |editor2-last=Huang |editor2-first=Jingyi |publisher=Springer Nature Switzerland |location=Cham, Switzerland |pages=201–10 |chapter-url=https://archive.org/details/reyes-et-al.-2023 |access-date=11 June 2025 }}</ref>


The decline of soil structure under [[irrigation]] is usually related to the breakdown of aggregates and dispersion of [[clay]] material as a result of rapid wetting. This is particularly so if soils are [[sodic soils|sodic]]; that is, having a high exchangeable sodium percentage (ESP) of the [[cation]]s attached to the clays. High sodium levels (compared to high [[calcium]] levels) cause particles to repel one another when wet, and the associated aggregates to disaggregate and disperse. The ESP will increase if irrigation causes salty water (even of low concentration) to gain access to the soil.
The decline of soil structure under [[irrigation]] is usually related to the breakdown of aggregates and dispersion of [[clay]] material as a result of rapid wetting. This is particularly so if soils are [[sodic soils|sodic]]; that is, having a high [[Sodium adsorption ratio|exchangeable sodium percentage]] (ESP) of the [[cation]]s attached to the clays. High sodium levels (compared to high [[calcium]] levels) cause particles to repel one another when wet, and the associated aggregates to disaggregate and disperse. The ESP will increase if irrigation causes salty water (even of low concentration) to gain access to the soil.<ref>{{cite book |last1=Murray |first1=Robert S. |last2=Grant |first2=Cameron D.  |date=July 2007 |title=The impact of irrigation on soil structure |location=Canberra, Australia |publisher=The National Program for Sustainable Irrigation, [[Land & Water Australia]], Australian Government |url=https://library.dbca.wa.gov.au/static/FullTextFiles/070521.pdf |access-date=11 June 2025 }}</ref>


A wide range of practices are undertaken to preserve and improve soil structure. For example, the NSW Department of Land and Water Conservation advocates: increasing organic content by incorporating pasture phases into [[crop rotation|cropping rotations]]; reducing or eliminating [[tillage]] and cultivation in cropping and pasture activities; avoiding soil disturbance during periods of excessive dry or wet when soils may accordingly tend to shatter or smear; and ensuring sufficient ground cover to protect the soil from raindrop impact. In irrigated agriculture, it may be recommended to: apply gypsum ([[calcium sulfate]]) to displace sodium cations with calcium and so reduce ESP or sodicity, avoid rapid wetting, and avoid disturbing soils when too wet or dry.<ref name=NSW1991/>
A wide range of practices are undertaken to preserve and improve soil structure. For example, the [[New South Wales]] Department of Land and Water Conservation advocates: increasing organic content by incorporating pasture phases into [[crop rotation|cropping rotations]]; reducing or eliminating [[tillage]] in cropping and [[pasture]] activities; avoiding soil disturbance during periods of excessive dry or wet when soils may accordingly tend to shatter or smear; and ensuring sufficient ground cover to protect the soil from [[raindrop]] impact and subsequent [[Slaking (geology)|slaking]]. In [[irrigated agriculture]], it may be recommended to: apply [[gypsum]] ([[calcium sulfate]]) to displace sodium cations with calcium and so reduce ESP or [[sodicity]], avoid rapid wetting, and avoid disturbing soils when too wet or dry.<ref name=NSW1991>{{cite web |year=1991 |title=Field indicators of soil structure decline |url=https://nswdpe.intersearch.com.au/nswdpejspui/bitstream/1/11852/1/detecting-soil-structure-decline.pdf |access-date=11 June 2025 }}</ref>


==Types==
==Types==


The main types of soil structures are:
The main types of soil structures are:
* Platy – The units are flat and platelike. They are generally oriented horizontally.<ref name=USDA>{{cite book |editor=C. Ditzler |editor2=K. Scheffe |editor3=H.C. Monger |date=2017 |title=USDA Soil Survey Manual |chapter=Examination and Description of Soil Profiles §Soil structure |chapter-url=https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_054253#soil_structure |archive-url=https://web.archive.org/web/20180907145549/https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_054253#soil_structure |archive-date=2018-09-07 |publisher=Government Printing Office |location=Washington, D.C. |access-date=2 November 2019}}</ref>
* Platy – The units are flat and platelike. They are generally oriented horizontally.<ref name=USDA>{{cite book |editor=Soil Science Division Staff |date=March 2017 |title=USDA Soil Survey Manual |chapter=Examination and description of soil profiles §Soil structure |chapter-url=https://www.nrcs.usda.gov/sites/default/files/2022-09/SSM-ch3.pdf |pages=155–163 |archive-url=https://web.archive.org/web/20180907145549/https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_054253#soil_structure |archive-date=2018-09-07 |publisher=[[United States Government Publishing Office|Government Printing Office]] |location=Washington, D.C. |access-date=12 June 2025 |url-status=live }}</ref>
* Prismatic – The individual units are bounded by flat to rounded vertical faces. Units are distinctly longer vertically, and the faces are typically casts or molds of adjoining units. Vertices are angular or subrounded; the tops of the prisms are somewhat indistinct and normally flat.<ref name=USDA/>
* Prismatic – The individual units are bounded by flat to rounded vertical faces. Units are distinctly longer vertically, and the faces are typically casts or molds of adjoining units. Vertices are angular or subrounded; the tops of the prisms are somewhat indistinct and normally flat.<ref name=USDA/>
* Columnar – The units are similar to prisms and bounded by flat or slightly rounded vertical faces. The tops of columns, in contrast to those of prisms, are very distinct and normally rounded.<ref name=USDA/>
* Columnar – The units are similar to prisms and bounded by flat or slightly rounded vertical faces. The tops of columns, in contrast to those of prisms, are very distinct and normally rounded.<ref name=USDA/>
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===Platy===
===Platy===


In platy structure, the units are flat and platelike. They are generally oriented horizontally. A special form, lenticular platy structure, is recognized for plates that are thickest in the middle and thin toward the edges. Platy structure is usually found in subsurface soils that have been subject to leaching or compaction by animals or machinery. The plates can be separated with a little effort by prying the horizontal layers with a pen knife. Platy structure tends to impede the downward movement of water and plant roots through the soil.
In platy structure, the units are flat and platelike. They are generally oriented horizontally. A special form, lenticular platy structure, is recognized for plates that are thickest in the middle and thin toward the edges. Platy structure is usually found in subsurface soils that have been subject to compaction by animal trampling<ref>{{cite journal |last1=Martı́nez |first1=Luis Joel |last2=Zinck |first2=Joseph Alfred |title=Temporal variation of soil compaction and deterioration of soil quality in pasture areas of Colombian Amazonia |journal=Soil and Tillage Research |date=January 2004 |volume=75 |issue=1 |pages=3–18 |doi=10.1016/j.still.2002.12.001 |url=https://www.researchgate.net/publication/223786633 |access-date=11 June 2025 }}</ref> or machinery traffic,<ref>{{cite journal |last1=Boizard |first1=Hubert |last2=Yoon |first2=Sung Won |last3=Léonard |first3=Joël |last4=Lheureux |first4=Sylvain |last5=Cousin |first5=Isabelle |last6=Roger-Estrade |first6=Jean |last7=Richard |first7=Guy |title=Using a morphological approach to evaluate the effect of traffic and weather conditions on the structure of a loamy soil in reduced tillage |journal=Soil and Tillage Research |date=March 2013 |volume=127 |pages=34–44 |doi=10.1016/j.still.2012.04.007 |url=https://fr.1lib.sk/book/55919304/258d3a |access-date=11 June 2025 }}</ref> but platy structures may also result from wetting-drying<ref>{{cite journal |last1=Sasal |first1=María Carolina |last2=Léonard |first2=Joël |last3=Andriulo |first3=Adrián |last4=Boizard |first4=Hubert |title=A contribution to understanding the origin of platy structure in silty soils under no tillage |journal=Soil and Tillage Research |date=November 2017 |volume=173 |pages=42–8 |doi=10.1016/j.still.2016.08.017 |url=https://fr.1lib.sk/book/94052079/5f9dfc |access-date=11 June 2025 }}</ref> and [[freeze-thaw]] cycles where they are of the lenticular type.<ref>{{cite journal |last1=Taina |first1=Ioana A. |last2=Heck |first2=Richard J. |last3=Deen |first3=William |last4=Ma |first4=Eddie Y.T. |title=Quantification of freeze-thaw related structure in cultivated topsoils using X-ray computer tomography |journal=[[Canadian Journal of Soil Science]] |date=31 May 2013 |volume=93 |issue=4 |pages=533–53 |doi=10.4141/cjss2012-044 |doi-access=free }}</ref> The plates can be separated with a little effort by prying the horizontal layers with a pen knife. Platy structure tends to impede the downward movement of water<ref>{{cite journal |last=Lilly |first=Allan |title=The relationship between field-saturated hydraulic conductivity and soil structure: development of class pedotransfer functions |journal=Soil Use and Management |date=March 2000 |volume=16 |issue=1 |pages=56–60 |doi=10.1111/j.1475-2743.2000.tb00174.x |url=https://fr.1lib.sk/book/41789601/4a551b |access-date=11 June 2025 }}</ref> and plant roots<ref>{{cite journal |last=McGarry |first=Declan |title=Soil compaction and cotton growth on a vertisol |journal=[[Australian Journal of Soil Research]] |year=1990 |volume=28 |issue=6 |pages=869–77 |doi=10.1071/SR9900869 |url=https://fr.1lib.sk/book/83446175/44e058 |access-date=13 June 2025 }}</ref> through the soil.
 
They are found most frequently in the C, E, Bs and K [[soil horizon|horizon]]s as well as in [[sesquioxide]]s (very old soils that are rich in iron and magnesium).


===Prismatic===
===Prismatic===


In the prismatic structure, the individual units are bounded by flat to rounded vertical faces. Units are distinctly longer vertically, and the faces are typically casts or molds of adjoining units. Vertices are angular or subrounded; the tops of the prisms are somewhat indistinct and normally flat. Prismatic structures are characteristic of the B horizons or subsoils. The vertical cracks result from freezing and thawing and wetting and drying as well as the downward movement of water and roots.
In the prismatic structure, the individual units are bounded by flat to rounded vertical faces. Units are distinctly longer vertically, and the faces are typically casts or molds of adjoining units. [[Vertex (geometry)|Vertices]] are angular or subrounded; the tops of the prisms are somewhat indistinct and normally flat. Prismatic structures are characteristic of clay- [[Illuvium|illuviated]] B horizons or [[Subsoil|subsoils]]. The vertical cracks result from freeze-thaw and wetting-drying cycles.<ref>{{cite journal |last=Harper |first=Horace J. |title=Factors which affect the development of prismatic structure in soils of the southern Great Plains |journal=[[Soil Science Society of America Proceedings]] |year=1938 |volume=2 |issue=C |pages=447–53 |doi=10.2136/sssaj1938.036159950002000C0071x |url=https://fr.1lib.sk/book/55334308/f951de |access-date=13 June 2025 }}</ref> They allow the downward movement of water and roots.<ref>{{cite journal |last1=Hasegawa |first1=Shuichi |last2=Sato |first2=Taiichirow |title=Water uptake by roots in cracks and water movement in clayey subsoil |journal=Soil Science |date=May 1987 |volume=143 |issue=5 |pages=381–86 |doi=10.1097/00010694-198705000-00008 |url=https://fr.1lib.sk/book/90571365/a464f0 |access-date=13 June 2025 }}</ref>


===Columnar===
===Columnar===


In the columnar structure, the units are similar to prisms and are bounded by flat or slightly rounded vertical faces. The tops of columns, in contrast to those of prisms, are very distinct and normally rounded. Columnar structure is common in the subsoil of sodium affected soils and soils rich in swelling clays such as the [[smectites]] and the kandite [[Halloysite]]. Columnar structure is very dense and it is very difficult for plant roots to penetrate these layers. Techniques such as deep plowing have helped to restore some degree of fertility to these soils.
In the columnar structure, the units are similar to prisms and are bounded by flat or slightly rounded vertical faces. The tops of columns, in contrast to those of prisms, are very distinct and normally rounded. Columnar structure is common in the subsoil of sodium affected soils<ref>{{cite book |editor=Soil Survey Staff |year=2022 |title=Keys to soil taxonomy |url=https://www.nrcs.usda.gov/sites/default/files/2022-09/Keys-to-Soil-Taxonomy.pdf |page=60 |publisher=[[United States Department of Agriculture]], [[Natural Resources Conservation Service]] |location=Washington, D.C. |edition=13th |access-date=13 June 2025 }}</ref> and soils rich in swelling clays such as the [[smectite]]s and the kandite [[Halloysite]].<ref>{{cite journal |last1=Elsass |first1=Françoise |last2=Dubroeucq |first2=Didier |last3=Thiry |first3=Médard |title=Diagenesis of silica minerals from clay minerals in volcanic soils of Mexico |journal=Clay Minerals |date=June 2000 |volume=35 |issue=3 |pages=477–89 |doi=10.1180/000985500546954 |url=https://www.researchgate.net/publication/249853194 |access-date=13 June 2025 }}</ref> Columnar structure is very dense and it is very difficult for plant roots to penetrate these layers. Techniques such as deep plowing have helped to restore some degree of fertility to these soils.<ref>{{cite journal |last1=Grevers |first1=Mike C.J. |last2=De Jong |first2=Eeltje |title=Soil structure changes in subsoiled solonetzic and chernozemic soils measured by image analysis |journal=Geoderma |date=June 1992 |volume=53 |issue=3–4 |pages=289–307 |doi=10.1016/0016-7061(92)90060-K |url=https://fr.1lib.sk/book/48381793/b438ed |access-date=13 June 2025 }}</ref>


===Blocky===
===Blocky===


In blocky structure, the structural units are blocklike or polyhedral. They are bounded by flat or slightly rounded surfaces that are casts of the faces of surrounding peds. Typically, blocky structural units are nearly equidimensional but grade to prisms and to plates. The structure is described as angular blocky if the faces intersect at relatively sharp angles; as subangular blocky if the faces are a mixture of rounded and plane faces and the corners are mostly rounded. Blocky structures are common in subsoil but also occur in surface soils that have a high clay content. The strongest blocky structure is formed as a result of swelling and shrinking of the clay minerals which produce cracks. Sometimes the surface of dried-up sloughs and ponds shows characteristic cracking and peeling due to clays.
In blocky structure, the structural units are blocklike or polyhedral. They are bounded by flat or slightly rounded surfaces that are casts of the faces of surrounding peds. Typically, blocky structural units are nearly equidimensional but grade to prisms and to plates. The structure is described as angular blocky if the faces intersect at relatively sharp angles; as subangular blocky if the faces are a mixture of rounded and plane faces and the corners are mostly rounded. Blocky structures are common in subsoil but also occur in surface soils that have a high clay content. The strongest blocky structure is formed as a result of swelling and shrinking of the clay minerals which produce cracks.<ref>{{cite journal |last1=Southard |first1=Randal J. |last2=Buol |first2=Stanley W. |title=Subsoil blocky structure formation in some North Carolina paleudults and paleaquults |journal=[[Soil Science Society of America Journal]] |date=July–August 1988 |volume=52 |issue=4 |pages=1069–76 |doi=10.2136/sssaj1988.03615995005200040032x |url=https://fr.1lib.sk/book/55340655/f1e908 |access-date=16 June 2025 }}</ref> Sometimes the surface of dried-up [[Slough (hydrology)|sloughs]] and ponds shows characteristic cracking and peeling due to clays.<ref>{{cite journal |last1=Armenteros |first1=Ildefonso |last2=Daley |first2=Brian |title=Pedogenic modification and structure evolution in palustrine facies as exemplified by the Bembridge Limestone (Late Eocene) of the Isle of Wight, southern England |journal=[[Sedimentary Geology (journal)|Sedimentary Geology]] |date=August 1998 |volume=119 |issue=3–4 |pages=275–95 |doi=10.1016/S0037-0738(98)00067-0 |url=https://www.researchgate.net/publication/223897178 |access-date=16 June 2025 }}</ref>


===Granular===<!-- This section is linked from [[Seedbed]] -->
===Granular===
{{uncited section|date=June 2023}}
 
In the granular structure, the structural units are approximately spherical or [[Polyhedron|polyhedral]] and are bounded by curved or very irregular faces that are not casts of adjoining peds. In other words, they look like cookie crumbs. Granular structure is common in the surface soils of rich [[grasslands]] and highly amended garden soils with high [[organic matter]] content. Soil mineral particles are both separated and bridged by organic matter breakdown products, and [[soil biota]] exudates, making the soil easy to work. [[Tillage|Cultivation]], [[earthworms]], [[frost action]] and rodents [[bioturbation|mix]] the soil and decrease the size of the peds. This structure allows for good [[porosity]] and easy movement of air and water. This combination of ease in [[tillage]], good moisture and air handling capabilities, and good structure for planting and [[germination]], are definitive of the phrase ''good tilth''.
In the granular structure, also called ''crumby'' or ''crumb'' structure, the structural units are approximately spherical or [[Polyhedron|polyhedral]] and are bounded by curved or very irregular faces that are not casts of adjoining peds. In other words, they look like cookie crumbs. Granular structure is common in the surface soils of rich [[grasslands]] and highly amended garden soils with high [[organic matter]] content.<ref>{{cite book |last=Malo |first=Douglas D. |year=2006 |chapter=Grasslands Soils |title=Encyclopedia of soil science |editor-last=Lal |editor-first=Rattan |publisher=[[Taylor & Francis]] |location=Boca Raton, Florida |edition=2nd |pages=777–81 |chapter-url=https://archive.org/details/malo-2006 |access-date=16 June 2025 }}</ref> Soil mineral particles are both separated and bridged by organic matter [[Decomposition|breakdown]] products,<ref>{{cite journal |last1=Hufschmid |first1=Ryan |last2=Newcomb |first2=Christina J. |last3=Grate |first3=Jay W. |last4=De Yoreo |first4=James J. |last5=Browning |first5=Nigel D. |last6=Qafoku |first6=Nikolla P. |title=Direct visualization of aggregate morphology and dynamics in a model soil organic-mineral system |journal=[[Environmental Science & Technology Letters]] |date=30 March 2017 |volume=4 |issue=5 |pages=186–91 |doi=10.1021/acs.estlett.7b00068 |url=https://pendidikankimia.walisongo.ac.id/wp-content/uploads/2018/09/4-1-1.pdf |access-date=16 June 2025 }}</ref> root and microbial [[Exudate|exudates]],<ref>{{cite journal |last1=Shabtai |first1=Itamar A. |last2=Hafner |first2=Benjamin D. |last3=Schweizer |first3=Steffen A. |last4=Höschen |first4=Carmen |last5=Possinger |first5=Angela |last6=Lehmann |first6=Johannes |last7=Bauerle |first7=Taryn |title=Root exudates simultaneously form and disrupt soil organo-mineral associations |journal=[[Communications Earth & Environment]] |date=13 November 2024 |volume=5 |page=699 |doi=10.1038/s43247-024-01879-6 |doi-access=free }}</ref><ref>{{cite journal |last1=Pucetaite |first1=Milda |last2=Hitchcock |first2=Adam |last3=Obst |first3=Martin |last4=Persson |first4=Per |last5=Hammer |first5=Edith C. |title=Nanoscale chemical mapping of exometabolites at fungal-mineral interfaces |journal=[[Geobiology (journal)|Geobiology]] |date=September 2022 |volume=20 |issue=5 |pages=650–66 |doi=10.1111/gbi.12504 |doi-access=free }}</ref> and animal [[excreta]],<ref>{{cite journal |last1=Guhra |first1=Tom |last2=Stolze |first2=Katharina |last3=Schweizer |first3=Steffen |last4=Totsche |first4=Kai Uwe |title=Earthworm mucus contributes to the formation of organo-mineral associations in soil |journal=[[Soil Biology and Biochemistry]] |date=June 2020 |volume=145 |page=107785 |doi=10.1016/j.soilbio.2020.107785 |url=https://www.researchgate.net/publication/339991303 |access-date=16 June 2025 }}</ref> making the soil easy to work. [[Tillage|Cultivation]],<ref>{{cite journal |last1=Berntsen |first1=Rolf |last2=Berre |first2=B. |title=Soil fragmentation and the efficiency of tillage implements |journal=Soil and Tillage Research |date=February 2002 |volume=64 |issue=1–2 |pages=137–47 |doi=10.1016/S0167-1987(01)00251-3 |url=https://fr.1lib.sk/book/36064100/2035e9 |access-date=16 June 2025 }}</ref> [[earthworms]],<ref>{{cite journal |last1=Larink |first1=Otto |last2=Werner |first2=D. |last3=Langmaack |first3=Marcus |last4=Schrader |first4=Stefan |title=Regeneration of compacted soil aggregates by earthworm activity |journal=Biology and Fertility of Soils  |date=May 2001 |volume=33 |pages=395–401 |doi=10.1007/s003740100340 |url=https://fr.1lib.sk/book/39393279/2fe6d9 |access-date=16 June 2025 }}</ref> [[frost action]]<ref name="Leuther2021">{{cite journal |last1=Leuther |first1=Frederic |last2=Schlüter |first2=Steffen |title=Impact of freeze-thaw cycles on soil structure and soil hydraulic properties |journal=Soil |year=2021 |volume=7 |issue=1 |pages=179–91 |doi=10.5194/soil-7-179-2021 |doi-access=free }}</ref> and rodents<ref>{{cite journal |last1=Whitford |first1=Walter G. |last2=Kay |first2=Fenton R. |title=Biopedturbation by mammals in deserts: a review |journal=[[Journal of Arid Environments]] |date=February 1999 |volume=41 |issue=2 |pages=203–30 |doi=10.1006/jare.1998.0482|url=https://www.academia.edu/58874471 |access-date=16 June 2025 }}</ref> [[bioturbation|mix]] the soil and decrease the size of the peds. This structure allows for good [[porosity]] and easy movement of air and water. This combination of ease in [[tillage]], good moisture and air handling capabilities, and good structure for planting and [[germination]], are definitive of the phrase ''good tilth'', a prominent component of ''[[soil health]]''.<ref>{{cite journal |last=Magdoff |first=Fred |title=Concept, components, and strategies of soil health in agroecosystems |journal=Journal of Nematology |year=2002 |volume=33 |issue=4 |pages=169–72 |url=https://journals.flvc.org/jon/article/view/67245/64913 |access-date=17 June 2025 }}</ref>


==Improvement==
==Improvement==
The benefits of improving soil structure for the growth of plants, particularly in an agricultural setting, include: reduced [[erosion]] due to greater soil aggregate strength and decreased overland flow; improved [[root penetration]] and access to [[soil moisture]] and nutrients; improved emergence of seedlings due to reduced crusting of the surface; and greater water infiltration, [[water retention curve|retention]] and availability due to improved porosity.


[[Agricultural productivity|Productivity]] from irrigated [[no-till farming|no-tillage]] or minimum tillage soil management in [[horticulture]] usually decreases over time due to degradation of the soil structure, inhibiting root growth and water retention. There are a few exceptions, why such exceptional fields retain structure is unknown, but it is associated with high organic matter. Improving soil structure in such settings can increase yields significantly.<ref>{{cite journal |last1=Cockroft |first1=B. |last2=Olsson |first2=K.A. |date=2000 |title=Degradation of soil structure due to coalescence of aggregates in no-till, no-traffic beds in irrigated crops |journal=Australian Journal of Soil Research |volume=38 |issue=1 |pages=61–70 |doi=10.1071/SR99079 }}</ref> The NSW Department of Land and Water Conservation suggests that in cropping systems, wheat yields can be increased by 10&nbsp;kg/ha for every extra millimetre of rain that is able to infiltrate due to soil structure.<ref name=NSW1991>Department of Land and Water Conservation 1991, [http://www.naturalresources.nsw.gov.au/care/soil/soil_pubs/index.html "Field indicators of soil structure decline"] {{webarchive|url=https://web.archive.org/web/20070914042431/http://www.naturalresources.nsw.gov.au/care/soil/soil_pubs/index.html |date=2007-09-14 }}, viewed May 2007</ref>
The benefits of improving soil structure (i.e. tending to granular structure) for the growth of plants, particularly in an agricultural setting, include: reduced [[erosion]] due to greater [[soil aggregate]] strength<ref>{{cite journal |last1=Abu-Hamdeh |first1=Nidal H. |last2=Abo-Qudais |first2=Saad Ahmad |last3=Othman |first3=Amal M. |title=Effect of soil aggregate size on infiltration and erosion characteristics |journal=European Journal of Soil Science |date=October 2006 |volume=57 |issue=5 |pages=609–16 |doi=10.1111/j.1365-2389.2005.00743.x |url=https://www.academia.edu/27127366 |access-date=17 June 2025 }}</ref> and decreased [[overland flow]];<ref>{{cite journal |last1=Palmer |first1=Robert C. |last2=Smith |first2=Richard C. |title=Soil structural degradation in SW England and its impact on surface-water runoff generation |journal=Soil Use and Management |date=December 2013 |volume=29 |issue=4 |pages=567–75 |doi=10.1111/sum.12068 |url=https://fr.1lib.sk/book/65685941/d40752 |access-date=17 June 2025 }}</ref> improved root penetration and access to [[soil moisture]] and [[Nutrient|nutrients]];<ref>{{cite journal |last1=Gao |first1=Weida |last2=Hodgkinson |first2=Laura |last3=Jin |first3=Kemo |last4=Watts |first4=Chris W. |last5=Ashton |first5=Rhys W. |last6=Shen |first6=Jianbo |last7=Ren |first7=Tusheng |last8=Dodd |first8=Ian C. |last9=Binley |first9=Andrew |last10=Phillips |first10=A. L. |last11=Hedden |first11=Peter |last12=Hawkesford |first12=Malcolm J. |last13=Whalley |first13=W. Richard |title=Deep roots and soil structure |journal=[[Plant, Cell & Environment]] |date=August 2016 |volume=39 |issue=8 |pages=1662–8 |doi=10.1111/pce.12684 |doi-access=free }}</ref> improved emergence of seedlings due to reduced crusting of the surface;<ref>{{cite journal |last1=Taki |first1=Orang |last2=Godwin |first2=Richard John |last3=Leeds-Harrison |first3=Peter B. |title=The creation of longitudinal cracks in shrinking soils to enhance seedling emergence. I. The effect of soil structure |journal=Soil Use and Management |date=March 2006 |volume=22 |issue=1 |pages=1–10 |doi=10.1111/j.1475-2743.2005.00005.x |url=https://fr.1lib.sk/book/41789905/d4e253 |access-date=17 June 2025 }}</ref> and greater [[water infiltration]], [[water retention curve|retention]] and water availability due to improved [[porosity]].<ref>{{cite journal |last1=Pagliai |first1=Marcello |last2=Vignozzi |first2=Nadia |last3=Pellegrini |first3=Sergio |title=Soil structure and the effect of management practices |journal=Soil and Tillage Research |date=December 2004 |volume=79 |issue=2 |pages=131–43 |doi=10.1016/j.still.2004.07.002 |url=https://www.researchgate.net/publication/223089933 |access-date=17 June 2025 }}</ref>
 
[[Agricultural productivity|Productivity]] from irrigated [[no-till farming|no-tillage]] or [[minimum tillage]] soil management in [[horticulture]] usually decreases over time due to degradation of the soil structure, inhibiting root growth and water retention. There are a few exceptions, why such exceptional fields retain structure is unknown, but it is associated with high organic matter. Improving soil structure in such settings can increase yields significantly.<ref>{{cite journal |last1=Cockroft |first1=Bruce |last2=Olsson |first2=Kenneth A. |year=2000 |title=Degradation of soil structure due to coalescence of aggregates in no-till, no-traffic beds in irrigated crops |journal=[[Australian Journal of Soil Research]] |volume=38 |issue=1 |pages=61–70 |doi=10.1071/SR99079 |url=https://fr.1lib.sk/book/78314552/0d0d3c |access-date=17 June 2025 }}</ref> The New South Wales Department of Land and Water Conservation suggests that in cropping systems, wheat yields can be increased by 10&nbsp;kg/ha for every extra millimetre of rain that is able to infiltrate due to soil structure.<ref name=NSW1991/>
 
Several techniques exist or have been suggested to improve soil structure, all of them tending to increase either porosity, organic matter content and/or soil microbial and faunal activity, i.e. all features associated with good granular/crumb structure.<ref>{{cite journal |last1=Arocena |first1=Joselito M. |last2=Van Mourik |first2=Jan M. |last3=Cano |first3=Ángel Faz |title=Granular soil structure indicates reclamation of degraded to productive soils: a case study in southeast Spain |journal=[[Canadian Journal of Soil Science]] |date=1 January 2012 |volume=92 |issue=1 |pages=243–51 |doi=10.4141/cjss2011-017 |doi-access=free }}</ref> Incorporating or depositing organic matter (e.g. [[mulch]], [[manure]], [[compost]]) has been practiced since the beginning of sedentary agriculture,<ref>{{cite journal |last=Wallin |first=Jan-Erik |date=December 1996 |title=History of sedentary farming in Ångermanland, northern Sweden, during the Iron Age and Medieval period based on pollen analytical investigations |journal=Vegetation History and Archaeobotany |volume=5 |issue=4 |pages=301–12 |doi=10.1007/BF00195298 |url=https://fr.1lib.sk/book/44162751/3ad946 |access-date=18 June 2025 }}</ref> favouring aggregation through the formation of stable bridges between mineral particles.<ref>{{cite book |last1=Kleber |first1=Markus |last2=Eusterhues |first2=Karin |last3=Keiluweit |first3=Marco |last4=Mikutta |first4=Christian |last5=Mikutta |first5=Robert |last6=Nico |first6=Peter S. |year=2015 |chapter=Mineral–organic associations: formation, properties, and relevance in soil environments |title=Advances in agronomy |volume=130 |editor-last=Sparks |editor-first=Donald L. |publisher=Elsevier |location=Amsterdam, The Netherlands |pages=1–140 |chapter-url=https://www.researchgate.net/publication/274372312 |doi=10.1016/bs.agron.2014.10.005 |access-date=18 June 2025 }}</ref> In tropical areas, the fast rate of organic matter [[Mineralization (soil science)|mineralization]] under warm/moist climate prevents using manure, mulch or compost for improving soil structure.<ref>{{cite journal |last=Ross |first=Sheila M. |date=September 1993 |title=Organic matter in tropical soils: current conditions, concerns andprospects for conservation |journal=[[Progress in Physical Geography]] |volume=17  |issue=3 |pages=265–305 |doi=10.1177/030913339301700301 |url=https://fr.1lib.sk/book/66355218/08ecbb |access-date=19 June 2025 }}</ref> Organic matter was favourably replaced by [[charcoal]], a source of [[black carbon]], known for its longevity and stable links with clay minerals.<ref>{{cite journal |last1=Czimczik |first1=Claudia I. |last2=Masiello |first2=Caroline A. |title=Controls on black carbon storage in soils |journal=Global Biogeochemical Cycles |date=September 2007 |volume=21 |issue=3 |doi=10.1029/2006GB002798 |doi-access=free }}</ref> Charcoal addition has been practiced by [[Indigenous peoples of the Americas|Amerindians]] during [[Pre-Columbian era|Pre-colombian]] times in the so-called [[Terra preta]] areas, also known as [[Amazonian dark earths|Amazonian Dark Earths]].<ref>{{cite journal |last1=Glaser |first1=Bruno |last2=Haumaier |first2=Ludwig |last3=Guggenberger |first3=Georg |last4=Zech |first4=Wolfgang |title=The 'Terra Preta' phenomenon: a model for sustainable agriculture in the humid tropics |journal=[[Naturwissenschaften]] |date=7 February 2014 |volume=88 |issue=1 |pages=37–41 |doi=10.1007/s001140000193 |url=https://www.researchgate.net/publication/12032464 |access-date=19 June 2025 }}</ref> [[Biochar]] is a present-day application of this ancestral technique.<ref>{{cite journal |last1=Schmidt |first1=Hans-Peter |last2=Kammann |first2=Claudia |last3=Hagemann |first3=Nikolas |last4=Leifeld |first4=Jens |last5=Bucheli |first5=Thomas D. |last6=Monedero |first6=Miguel Angel Sánchez |last7=Cayuela |first7=Maria Luz |title=Biochar in agriculture: a systematic review of 26 global meta-analyses |journal=Global Change Biology Bioenergy |date=November 2021 |volume=13 |issue=11 |pages=1708–30 |doi=10.1111/gcbb.12889 |doi-access=free }}</ref> [[Liming (soil)|Liming]], either practised alone<ref>{{cite journal |last1=Schack-Kirchner |first1=Helmer |last2=Hildebrand |first2=Ernst E. |title=Changes in soil structure and aeration due to liming and acid irrigation |journal=[[Plant and Soil]] |date=7 February 1998 |volume=199 |issue=1 |pages=167–76 |doi=10.1023/A:1004290226402 |url=https://fr.1lib.sk/book/43161440/69009a |access-date=19 June 2025 }}</ref> or in association with organic matter,<ref>{{cite journal |last1=Wuddivira |first1=Mark N. |last2=Camps-Roach |first2=Geremy |title=Effects of organic matter and calcium on soil structural stability |journal=European Journal of Soil Science |date=June 2007 |volume=58 |issue=3 |pages=722–27 |doi=10.1111/j.1365-2389.2006.00861.x |url=https://www.researchgate.net/publication/230281333 |access-date=19 June 2025 }}</ref> increases soil porosity and aggregation thanks to the bridging capacity of the divalent [[calcium]] cation towards negatively charged clay particles and organic molecules.<ref>{{cite journal |last1=Conradi |first1=Elio Jr |last2=Gonçalves |first2=Affonso Celso |last3=Seidel |first3=Edleusa Pereira |last4=Ziemer |first4=Guilherme Lindner |last5=Zimmermann |first5=Juliano |last6=Dias de Oliveira |first6=Vinícius Henrique |last7=Schwantes |first7=Daniel |last8=Zeni |first8=Carlos Daniel |title=Effects of liming on soil physical attributes: a review |journal=[[The Journal of Agricultural Science|Journal of Agricultural Science]] |year=2020 |volume=12 |issue=10 |page=278 |doi=10.5539/jas.v12n10p278 |doi-access=free }}</ref> Calcium also protects organic matter from mineralization, stabilizing it within aggregates.<ref>{{cite journal |last1=Rowley |first1=Mike C. |last2=Grand |first2=Stéphanie |last3=Verrecchia  |first3=Éric P. |title=Calcium-mediated stabilisation of soil organic carbon |journal=Biogeochemistry |date=19 December 2017 |volume=137 |issue=1–2 |pages=27–49 |doi=10.1007/s10533-017-0410-1 |url=https://www.researchgate.net/publication/321916954 |access-date=19 June 2025 }}</ref> Several cultural techniques have been employed for a long time to stimulate aeration and soil biological activty in [[waterlogged]] soils, thereby shifting soil structure from compact types (e.g. lenticular) to granular along rows where crops were planted or sown. Although they differ according to countries and epochs, all of them allow the cultivated part of the soil profile to be at distance from the [[phreatic zone]] and thus better aerated: ridge-tillage,<ref>{{cite journal |last1=Tisdall |first1=Judith M. C. |last2=Hodgson |first2=John Michael |title=Ridge tillage in Australia: a review |journal=Soil and Tillage Research |date=November 1990 |volume=18 |issue=2–3 |pages=127–44 |doi=10.1016/0167-1987(90)90055-I |url=https://fr.1lib.sk/book/34161912/b9b42f |access-date=19 June 2025 }}</ref> a form of conservation [[tillage]], is an example. The penetration of burrowing earthworms in areas deprived of them (e.g. in recent [[Polder|polders]]) has been observed to improve soil structure.<ref>{{cite journal |last=Marinissen |first=Joke C. Y. |title=Earthworm populations and stability of soil structure in a silt loam soil of a recently reclaimed polder in the Netherlands |journal=[[Agriculture, Ecosystems & Environment]] |date=November 1994 |volume=51 |issue=1–2 |pages=75–87 |doi=10.1016/0167-8809(94)90035-3 |url=https://fr.1lib.sk/book/45318438/e0f58e |access-date=19 June 2025 }}</ref> The introduction of European earthworms in earthworm-free areas improved soil structure and increased to a great extent the productivity of New Zealand pastures.<ref>{{cite journal |last=Stockdill |first=S. M. J. |title=Effects of introduced earthworms on the productivity of New Zealand pastures |journal=Pedobiologia |date=January 1982 |volume=24 |issue=1 |pages=29–35 |doi=10.1016/S0031-4056(23)05863-8 |url=https://archive.org/details/stockdill-1982 |access-date=19 June 2025 }}</ref> The Earthworm Inoculation Unit (EIU) technique has been suggested as an efficient and cost-friendly method to become an integral component of sustainable [[land restoration]] practice.<ref>{{cite journal |last1=Butt |first1=Kevin R. |last2=Frederickson |first2=James |last3=Morris  |first3=Richard M. |title=The Earthworm Inoculation Unit technique: an integrated system for cultivation and soil-inoculation of earthworms |journal=[[Soil Biology and Biochemistry]] |date=March–April 1997 |volume=29 |issue=3–4 |pages=251–7 |doi=10.1016/S0038-0717(96)00053-3 |url=https://www.researchgate.net/publication/240417293 |access-date=19 June 2025 }}</ref>  


==Hardsetting soil==
==Hardsetting soil==
Hardsetting soils lose their structure when wet and then set hard as they dry out to form a structureless mass that is very difficult to cultivate. They can only be tilled when their moisture content is within a limited range. When they are tilled the result is often a very cloddy surface (poor [[tilth]]). As they dry out the high soil strength often restricts seedling and root growth. Infiltration rates are low and runoff of rain and irrigation limits the productivity of many hardsetting soils.<ref name="Daniells2012">{{cite journal|last1=Daniells |first1=Ian G. |title=Hardsetting soils: a review |journal=Soil Research |date=2012 |volume=50 |issue=5 |pages=349–359 |doi=10.1071/SR11102}}</ref>
 
Hardsetting soils lose their structure when wet and then set hard as they dry out to form a structureless mass that is very difficult to cultivate. They can only be tilled when their moisture content is within a limited range. When they are tilled the result is often a very cloddy surface (poor [[tilth]]). As they dry out the high soil strength often restricts seedling and root growth. Infiltration rates are low and [[Runoff (hydrology)|runoff]] of rain and irrigation limits the productivity of many hardsetting soils.<ref name="Daniells2012">{{cite journal |last=Daniells |first=Ian G. |title=Hardsetting soils: a review |journal=[[Soil Research]] |date=8 August 2012 |volume=50 |issue=5 |pages=349–59 |doi=10.1071/SR11102 |url=https://fr.1lib.sk/book/78053287/c508ec |access-date=20 June 2025 }}</ref>


===Definition===
===Definition===


Hardsetting has been defined this way: "A hardsetting soil is one that sets to an almost homogeneous mass on drying. It may have occasional cracks, typically at a spacing of >0.1 m. Air dry hardset soil is hard and brittle, and it is not possible to push a forefinger into the profile face. Typically, it has a tensile strength of 90 kN<sup>–2</sup>. Soils that crust are not necessarily hardsetting since a hardsetting horizon is thicker than a crust. (In cultivated soils the thickness of the hardsetting horizon is frequently equal to or greater than that of the cultivated layer.) Hardsetting soil is not permanently cemented and is soft when wet. The clods in a hardsetting horizon that has been cultivated will partially or totally disintegrate upon wetting. If the soil has been sufficiently wetted, it will revert to its hardset state on drying. This can happen after flood irrigation or a single intense rainfall event."<ref name="Mullins1997">{{cite book |last1=Mullins |first1=CE |editor1=R Lal |editor2=WH Blum |editor3=C Valentin |editor4=BA Stewart |title=Methods for assessment of soil degradation |date=1997 |publisher=CRC Press |location=Boca Raton, FL |isbn=978-0-8493-7443-2 |chapter=Hardsetting |page=121 |url=https://books.google.com/books?id=4gv5HEOrX8YC |access-date=18 August 2016}}</ref>
Hardsetting has been defined this way: "A hardsetting horizon is one that sets to an almost homogeneous mass on drying. It may have occasional cracks, typically at a spacing of >0.1 m. Air dry hardset soil is hard and brittle, and it is not possible to push a forefinger into the profile face. Typically, it has a tensile strength of 90 kN<sup>–2</sup>. Soils that crust are not necessarily hardsetting since a hardsetting horizon is thicker than a crust. (In cultivated soils the thickness of the hardsetting horizon is frequently equal to or greater than that of the cultivated layer.) Hardsetting soil is not permanently cemented and is soft when wet. The clods in a hardsetting horizon that has been cultivated will partially or totally disintegrate upon wetting. If the soil has been sufficiently wetted, it will revert to its hardset state on drying. This can happen after flood irrigation or a single intense rainfall event."<ref name="Mullins1997">{{cite book |last=Mullins |first=Chris E. |year=1997 |chapter=Hardsetting |title=Methods for assessment of soil degradation |editor-last1=Lal |editor-first1=Ratan |editor-last2=Blum |editor-first2=Winfried H. |editor-last3=Valentin |editor-first3=Christian |editor-last4=Stewart |editor-first4=Bobby Alton |series=Advances in soil science |volume=9 |publisher=CRC Press |location=Boca Raton, Florida |page=121 |isbn=978-0-8493-7443-2 |url=https://books.google.com/books?id=4gv5HEOrX8YC |access-date=20 June 2025 }}</ref>


== Soil structure dynamics ==
== Soil structure dynamics ==
Soil structure is inherently a [[wikt:dynamic|dynamic]] and [[complex system]] that is affected by different factors such as [[tillage]], wheel traffic, [[root]]s, biological activities in soil, rainfall events, [[Aeolian processes|wind erosion]], shrinking, swelling, freezing and thawing. In turn, reciprocally soil structure interacts and affects the root growth and function, [[Soil biology|soil fauna]] and biota, water and solute transport processes, [[gas exchange]], [[thermal conductivity]] and [[Electrical resistivity and conductivity|electrical conductivity]], traffic [[bearing capacity]], and many other aspects in relation with soil. Ignoring soil structure or viewing it as "static" can lead to poor predictions of soil properties and might significantly affect the [[soil management]].<ref>{{Cite book|last1=Logsdon|first1=Sally|last2=Berli|first2=Markus|last3=Horn|first3=Rainer|date=January 2013|title= Quantifying and Modeling Soil Structure Dynamics|language=en|pages=vii–ix|doi=10.2134/advagricsystmodel3.frontmatter|issn=2163-2790|chapter=Front Matter|series=Advances in Agricultural Systems Modeling|isbn=978-0-89118-957-2}}</ref>
Soil structure is inherently a [[wikt:dynamic|dynamic]] and [[complex system]] that is affected by different factors such as [[tillage]],<ref>{{cite journal |last1=Pires |first1=Luiz F. |last2=Borges |first2=Jaqueline A. R. |last3=Rosa |first3=Jadir A. |last4=Cooper |first4=Miguel |last5=Heck |first5=Richard J. |last6=Passoni |first6=Sabrina |last7=Roque |first7=Waldir L. |title=Soil structure changes induced by tillage systems |journal=Soil and Tillage Research |date=January 2017 |volume=165 |pages=66–79 |doi=10.1016/j.still.2016.07.010 |url=https://www.academia.edu/94557402 |access-date=20 June 2025 }}</ref> wheel traffic,<ref>{{cite journal |last1=Voorhees |first1=Ward B. |last2=Senst |first2=C. G. |last3=Nelson |first3=W. W. |title=Compaction and soil structure modification by wheel traffic in the northern Corn Belt |journal=[[Soil Science Society of America Journal]] |date=March–April 1978 |volume=42 |issue=2 |pages=344–9 |doi=10.2136/sssaj1978.03615995004200020029x |url=https://fr.1lib.sk/book/55338019/10e2e4 |access-date=20 June 2025 }}</ref> [[root]], [[Microorganism|microbial]] and [[Fauna|faunal]] activities in soil,<ref>{{cite journal |last1=Mueller |first1=Carsten W. |last2=Baumert |first2=Vera |last3=Carminati |first3=Andrea |last4=Germon |first4=Amandine |last5=Holz |first5=Maire |last6=Kögel-Knabner |first6=Ingrid |last7=Peth |first7=Stephan |last8=Schlüter |first8=Steffen |last9=Uteau |first9=Daniel |last10=Vetterlein |first10=Doris |last11=Teixeira |first11=Pedro |last12=Vidal |first12=Alix |title=From rhizosphere to detritusphere: soil structure formation driven by plant roots and the interactions with soil biota |journal=[[Soil Biology and Biochemistry]] |date=June 2024 |volume=193 |page=109396 |doi=10.1016/j.soilbio.2024.109396 |url=https://www.researchgate.net/publication/378853838 |access-date=20 June 2025 }}</ref><ref>{{cite journal |last1=Lee |first1=Kenneth Ernest |last2=Foster |first2=R. C. |title=Soil fauna and soil structure |journal=[[Australian Journal of Soil Research]] |date=December 1991 |volume=29 |issue=6 |pages=745–75 |doi=10.1071/SR9910745 |url=https://www.academia.edu/102507924 |access-date=20 June 2025 }}</ref> rainfall events,<ref>{{cite journal |last=Rose |first=Calvin W. |title=Rainfall and soil structure |journal=Soil Science |date=January 1961 |volume=91 |issue=1 |pages=49–54 |url=https://fr.1lib.sk/book/91288631/538fda |access-date=20 June 2025 }}</ref> [[Aeolian processes|wind erosion]],<ref>{{cite journal |last1=Lyles |first1=Leon |last2=Tatarko |first2=John |title=Wind erosion effects on soil texture and organic matter |journal=[[Journal of Soil and Water Conservation]] |date=May–June 1986 |volume=41 |issue=3 |pages=191–3 |doi=10.1080/00224561.1986.12455968 |url=https://www.researchgate.net/publication/235642195 |access-date=20 June 2025 }}</ref> [[Soil aggregate stability|wetting and drying]],<ref>{{cite journal |last1=Diel |first1=Julius |last2=Vogel |first2=Hans-Jörg |last3=Schlüter |first3=Steffen |title=Impact of wetting and drying cycles on soil structure dynamics |journal=Geoderma |date=1 July 2019 |volume=345 |pages=63–71 |doi=10.1016/j.geoderma.2019.03.018 |url=https://archive.org/details/diel-et-al.-2019 |access-date=23 June 2025 }}</ref> freezing and thawing.<ref name="Leuther2021"/> In turn, reciprocally soil structure interacts and affects the root growth and function,<ref>{{cite journal |last=Passioura |first=John B. |title=Soil structure and plant growth |journal=[[Australian Journal of Soil Research]] |year=1991 |volume=29 |issue=6 |pages=717–28 |doi=10.1071/SR9910717 |url=https://fr.1lib.sk/book/62707630/752ee7 |access-date=23 June 2025 }}</ref> [[Soil biology|soil fauna and microorganisms]],<ref>{{cite journal |last=Mikhail |first=Wafai Z. A. |title=Effect of soil structure on soil fauna in a desert wadi in Southern Egypt |journal=[[Journal of Arid Environments]] |date=May 1993 |volume=24 |issue=4 |pages=321–31 |doi=10.1006/jare.1993.1028 |url=https://www.academia.edu/57993269 |access-date=23 June 2025 }}</ref><ref>{{cite book |last=Holden |first=Patricia A. |year=2011 |chapter=How do the microhabitats framed by soil structure impact soil bacteria and the processes that they regulate? |title=The architecture and biology of soils: life in inner space |editor-last1=Ritz |editor-first1=Karl |editor-last2=Young |editor-first2=Iain |publisher=[[Commonwealth Agricultural Bureaux International]] |location=Wallingford, United Kingdom |pages=118–148 |isbn=978-1-84593-532-0 |doi=10.1079/9781845935320.0118 |chapter-url=https://www.cabidigitallibrary.org/doi/pdf/10.5555/20113333038 |access-date=23 June 2025 }}</ref> water and solute transport processes,<ref>{{cite journal |last1=Bejat |first1=Ligia |last2=Perfect |first2=Edmund |last3=Quisenberry |first3=Virgil E. |last4=Coyne |first4=Mark S. |last5=Haszler |first5=Gerald R. |title=Solute transport as related to soil structure in unsaturated intact soil blocks |journal=[[Soil Science Society of America Journal]] |date=May 2000 |volume=64 |issue=3 |pages=818–26 |doi=10.2136/sssaj2000.643818x |url=https://fr.1lib.sk/book/55344096/832666 |access-date=23 June 2025 }}</ref> [[gas exchange]],<ref>{{cite journal |last1=Bakker |first1=Gerben W. |last2=Hidding |first2=A. P. |title=The influence of soil structure and air content on gas diffusion in soils |journal=Netherlands Journal of Agricultural Science |date=February 1970 |volume=18 |issue=1 |pages=37–48 |doi=10.18174/njas.v18i1.17354 |doi-access=free }}</ref> [[thermal conductivity]]<ref>{{cite journal |last=Smith |first=W. O. |title=The thermal conductivity of dry soil |journal=Soil Science |date=June 1942 |volume=53 |issue=6 |pages=435–60 |url=https://fr.1lib.sk/book/90919556/b97e63 |access-date=23 June 2025 }}</ref> and [[Electrical resistivity and conductivity|electrical conductivity]],<ref>{{cite journal |last=Friedman |first=Shmulik P. |title=Soil properties influencing apparent electrical conductivity: a review |journal=Computers and Electronics in Agriculture |date=March 2005 |volume=46 |issue=1–3 |page=45–70 |doi=10.1016/j.compag.2004.11.001 |url=https://www.academia.edu/128527477 |access-date=24 June 2025 }}</ref> traffic [[bearing capacity]],<ref>{{cite journal |last1=Noda |first1=Toshihiro |last2=Asaoka |first2=Akira |last3=Yamada |first3=Shotaro |title=Some bearing capacity characteristics of a structured naturally deposited clay soil |journal=Soils and Foundations |date=April 2007 |volume=47 |issue=2 |pages=285–301 |doi=10.3208/sandf.47.285 |url=https://www.jstage.jst.go.jp/article/sandf/47/2/47_2_285/_pdf |access-date=24 June 2025 }}</ref> and many other aspects in relation with soil. Ignoring soil structure or viewing it as "static" can lead to poor predictions of soil properties and might significantly affect the [[soil management]].<ref>{{cite book |last1=Logsdon |first1=Sally |last2=Berli |first2=Markus |last3=Horn |first3=Rainer |date=January 2013 |title=Quantifying and modeling soil structure dynamics |language=en |pages=vii–ix |doi=10.2134/advagricsystmodel3.frontmatter |issn=2163-2790 |chapter=Front matter |series=Advances in Agricultural Systems Modeling |isbn=978-0-89118-957-2 |chapter-url=https://acsess.onlinelibrary.wiley.com/doi/epdf/10.2134/advagricsystmodel3.frontmatter |access-date=24 June 2025 }}</ref>


==See also==
==See also==
Line 78: Line 80:
* Leeper, GW & Uren, NC 1993, 5th edn, ''Soil science, an introduction'', Melbourne University Press, Melbourne
* Leeper, GW & Uren, NC 1993, 5th edn, ''Soil science, an introduction'', Melbourne University Press, Melbourne
* Marshall, TJ & Holmes JW, 1979, ''Soil Physics'', Cambridge University Press
* Marshall, TJ & Holmes JW, 1979, ''Soil Physics'', Cambridge University Press
* {{cite web | author= Soil Survey Division Staff | year= 1993 | url= http://soils.usda.gov/technical/manual/contents/chapter3.html | title= Examination and Description of Soils | work= Handbook 18. Soil survey manual | publisher= Soil Conservation Service. U.S. Department of Agriculture | access-date= 2006-04-11 | archive-url= https://web.archive.org/web/20110514151830/http://soils.usda.gov/technical/manual/contents/chapter3.html | archive-date= 2011-05-14 }}
* {{cite web | author= Soil Survey Division Staff | year= 1993 | url= https://www.nrcs.usda.gov/conservation-basics/natural-resource-concerns/soil/soil-science | title= Examination and Description of Soils | work= Handbook 18. Soil survey manual | publisher= Soil Conservation Service. U.S. Department of Agriculture | access-date= 2006-04-11 | url-status= live | archive-url= https://web.archive.org/web/20110514151830/http://soils.usda.gov/technical/manual/contents/chapter3.html | archive-date= 2011-05-14 }}
* Charman, PEV & Murphy, BW 1998, 5th edn, ''Soils, their properties and management'', Oxford University Press, Melbourne
* Charman, PEV & Murphy, BW 1998, 5th edn, ''Soils, their properties and management'', Oxford University Press, Melbourne
* Firuziaan, M. and Estorff, O., (2002), "Simulation of the Dynamic Behavior of Bedding-Foundation-Soil in the Time Domain", Springer Verlag.
* Firuziaan, M. and Estorff, O., (2002), "Simulation of the Dynamic Behavior of Bedding-Foundation-Soil in the Time Domain", Springer Verlag.
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* {{cite web|url=http://passel.unl.edu/pages/informationmodule.php?idinformationmodule=1130447039&amp;topicorder=4&amp;maxto=10|title=Soils - Part 2: Physical Properties of Soil and Soil Water|publisher=unl.edu}}
* {{cite web|url=http://passel.unl.edu/pages/informationmodule.php?idinformationmodule=1130447039&amp;topicorder=4&amp;maxto=10|title=Soils - Part 2: Physical Properties of Soil and Soil Water|publisher=unl.edu}}
* Jordán, Antonio. 2013. [http://blogs.egu.eu/divisions/sss/2013/08/19/what-is-soil-structure/ What is soil structure?]  European Geosciences Union Blog. Accessed 11 June 2017.
* Jordán, Antonio. 2013. [http://blogs.egu.eu/divisions/sss/2013/08/19/what-is-soil-structure/ What is soil structure?]  European Geosciences Union Blog. Accessed 11 June 2017.
* Soil Survey Division Staff. 1993. [https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?soil syu tycid=nrcs142p2_054253 Soil Survey Manual, Chapter 3: Examination and Description of Soils.] USDA NRCS. Accessed 11 June 2017.
* Soil Survey Division Staff. 1993. [https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?soil syu tycid=nrcs142p2_054253 Soil Survey Manual, Chapter 3: Examination and Description of Soils.]{{dead link|date=June 2025|bot=medic}}{{cbignore|bot=medic}} USDA NRCS. Accessed 11 June 2017.
{{soil science topics}}
{{soil science topics}}
{{Authority control}}
{{Authority control}}

Latest revision as of 06:52, 29 June 2025

Template:Short description Template:Multiple issues

In geotechnical engineering, soil structure describes the arrangement of the solid parts of the soil and of the pore space located between them. It is determined by how individual soil granules clump, bind together, and aggregate, resulting in the arrangement of soil pores between them. Soil has a major influence on water and air movement, biological activity, root growth and seedling emergence. There are several different types of soil structure. It is inherently a dynamic and complex system that is affected by different biotic and abiotic factors.[1]

Overview

Soil structure describes the arrangement of the solid parts of the soil and of the pore spaces located between them.[2][3] Aggregation is the result of the interaction of soil particles through rearrangement, flocculation and cementation. It is enhanced by:[3][4] the precipitation of oxides, hydroxides, carbonates and silicates; the products of biological activity (such as biofilms, fungal hyphae and glycoproteins); ionic bridging between negatively charged particles (both clay minerals and organic compounds) by multivalent cations; and interactions between organic compounds (hydrogen bonding and hydrophobic bonding).

The quality of soil structure will decline under most forms of cultivation; the associated mechanical mixing of the soil compacts and shears aggregates and fills pore spaces;[5] it also exposes organic matter to a greater rate of decay and oxidation.[6] A further consequence of continued cultivation and traffic is the development of compacted, impermeable layers or hardpans within the soil profile.[7]

The decline of soil structure under irrigation is usually related to the breakdown of aggregates and dispersion of clay material as a result of rapid wetting. This is particularly so if soils are sodic; that is, having a high exchangeable sodium percentage (ESP) of the cations attached to the clays. High sodium levels (compared to high calcium levels) cause particles to repel one another when wet, and the associated aggregates to disaggregate and disperse. The ESP will increase if irrigation causes salty water (even of low concentration) to gain access to the soil.[8]

A wide range of practices are undertaken to preserve and improve soil structure. For example, the New South Wales Department of Land and Water Conservation advocates: increasing organic content by incorporating pasture phases into cropping rotations; reducing or eliminating tillage in cropping and pasture activities; avoiding soil disturbance during periods of excessive dry or wet when soils may accordingly tend to shatter or smear; and ensuring sufficient ground cover to protect the soil from raindrop impact and subsequent slaking. In irrigated agriculture, it may be recommended to: apply gypsum (calcium sulfate) to displace sodium cations with calcium and so reduce ESP or sodicity, avoid rapid wetting, and avoid disturbing soils when too wet or dry.[9]

Types

The main types of soil structures are:

  • Platy – The units are flat and platelike. They are generally oriented horizontally.[10]
  • Prismatic – The individual units are bounded by flat to rounded vertical faces. Units are distinctly longer vertically, and the faces are typically casts or molds of adjoining units. Vertices are angular or subrounded; the tops of the prisms are somewhat indistinct and normally flat.[10]
  • Columnar – The units are similar to prisms and bounded by flat or slightly rounded vertical faces. The tops of columns, in contrast to those of prisms, are very distinct and normally rounded.[10]
  • Blocky – The units are blocklike or polyhedral. They are bounded by flat or slightly rounded surfaces that are casts of the faces of surrounding peds. Typically, blocky structural units are nearly equidimensional but grade to prisms and plates. The structure is described as angular blocky if the faces intersect at relatively sharp angles and as subangular blocky if the faces are a mixture of rounded and plane faces and the corners are mostly rounded.[10]
  • Granular – The units are approximately spherical or polyhedral. They are bounded by curved or very irregular faces that are not casts of adjoining peds.[10]
  • Wedge – The units are approximately elliptical with interlocking lenses that terminate in acute angles. They are commonly bounded by small slickensides.[10]
  • Lenticular —The units are overlapping lenses parallel to the soil surface. They are thickest in the middle and thin towards the edges. Lenticular structure is commonly associated with moist soils, texture classes high in silt or very fine sand (e.g., silt loam), and high potential for frost action.[10]

Platy

In platy structure, the units are flat and platelike. They are generally oriented horizontally. A special form, lenticular platy structure, is recognized for plates that are thickest in the middle and thin toward the edges. Platy structure is usually found in subsurface soils that have been subject to compaction by animal trampling[11] or machinery traffic,[12] but platy structures may also result from wetting-drying[13] and freeze-thaw cycles where they are of the lenticular type.[14] The plates can be separated with a little effort by prying the horizontal layers with a pen knife. Platy structure tends to impede the downward movement of water[15] and plant roots[16] through the soil.

Prismatic

In the prismatic structure, the individual units are bounded by flat to rounded vertical faces. Units are distinctly longer vertically, and the faces are typically casts or molds of adjoining units. Vertices are angular or subrounded; the tops of the prisms are somewhat indistinct and normally flat. Prismatic structures are characteristic of clay- illuviated B horizons or subsoils. The vertical cracks result from freeze-thaw and wetting-drying cycles.[17] They allow the downward movement of water and roots.[18]

Columnar

In the columnar structure, the units are similar to prisms and are bounded by flat or slightly rounded vertical faces. The tops of columns, in contrast to those of prisms, are very distinct and normally rounded. Columnar structure is common in the subsoil of sodium affected soils[19] and soils rich in swelling clays such as the smectites and the kandite Halloysite.[20] Columnar structure is very dense and it is very difficult for plant roots to penetrate these layers. Techniques such as deep plowing have helped to restore some degree of fertility to these soils.[21]

Blocky

In blocky structure, the structural units are blocklike or polyhedral. They are bounded by flat or slightly rounded surfaces that are casts of the faces of surrounding peds. Typically, blocky structural units are nearly equidimensional but grade to prisms and to plates. The structure is described as angular blocky if the faces intersect at relatively sharp angles; as subangular blocky if the faces are a mixture of rounded and plane faces and the corners are mostly rounded. Blocky structures are common in subsoil but also occur in surface soils that have a high clay content. The strongest blocky structure is formed as a result of swelling and shrinking of the clay minerals which produce cracks.[22] Sometimes the surface of dried-up sloughs and ponds shows characteristic cracking and peeling due to clays.[23]

Granular

In the granular structure, also called crumby or crumb structure, the structural units are approximately spherical or polyhedral and are bounded by curved or very irregular faces that are not casts of adjoining peds. In other words, they look like cookie crumbs. Granular structure is common in the surface soils of rich grasslands and highly amended garden soils with high organic matter content.[24] Soil mineral particles are both separated and bridged by organic matter breakdown products,[25] root and microbial exudates,[26][27] and animal excreta,[28] making the soil easy to work. Cultivation,[29] earthworms,[30] frost action[31] and rodents[32] mix the soil and decrease the size of the peds. This structure allows for good porosity and easy movement of air and water. This combination of ease in tillage, good moisture and air handling capabilities, and good structure for planting and germination, are definitive of the phrase good tilth, a prominent component of soil health.[33]

Improvement

The benefits of improving soil structure (i.e. tending to granular structure) for the growth of plants, particularly in an agricultural setting, include: reduced erosion due to greater soil aggregate strength[34] and decreased overland flow;[35] improved root penetration and access to soil moisture and nutrients;[36] improved emergence of seedlings due to reduced crusting of the surface;[37] and greater water infiltration, retention and water availability due to improved porosity.[38]

Productivity from irrigated no-tillage or minimum tillage soil management in horticulture usually decreases over time due to degradation of the soil structure, inhibiting root growth and water retention. There are a few exceptions, why such exceptional fields retain structure is unknown, but it is associated with high organic matter. Improving soil structure in such settings can increase yields significantly.[39] The New South Wales Department of Land and Water Conservation suggests that in cropping systems, wheat yields can be increased by 10 kg/ha for every extra millimetre of rain that is able to infiltrate due to soil structure.[9]

Several techniques exist or have been suggested to improve soil structure, all of them tending to increase either porosity, organic matter content and/or soil microbial and faunal activity, i.e. all features associated with good granular/crumb structure.[40] Incorporating or depositing organic matter (e.g. mulch, manure, compost) has been practiced since the beginning of sedentary agriculture,[41] favouring aggregation through the formation of stable bridges between mineral particles.[42] In tropical areas, the fast rate of organic matter mineralization under warm/moist climate prevents using manure, mulch or compost for improving soil structure.[43] Organic matter was favourably replaced by charcoal, a source of black carbon, known for its longevity and stable links with clay minerals.[44] Charcoal addition has been practiced by Amerindians during Pre-colombian times in the so-called Terra preta areas, also known as Amazonian Dark Earths.[45] Biochar is a present-day application of this ancestral technique.[46] Liming, either practised alone[47] or in association with organic matter,[48] increases soil porosity and aggregation thanks to the bridging capacity of the divalent calcium cation towards negatively charged clay particles and organic molecules.[49] Calcium also protects organic matter from mineralization, stabilizing it within aggregates.[50] Several cultural techniques have been employed for a long time to stimulate aeration and soil biological activty in waterlogged soils, thereby shifting soil structure from compact types (e.g. lenticular) to granular along rows where crops were planted or sown. Although they differ according to countries and epochs, all of them allow the cultivated part of the soil profile to be at distance from the phreatic zone and thus better aerated: ridge-tillage,[51] a form of conservation tillage, is an example. The penetration of burrowing earthworms in areas deprived of them (e.g. in recent polders) has been observed to improve soil structure.[52] The introduction of European earthworms in earthworm-free areas improved soil structure and increased to a great extent the productivity of New Zealand pastures.[53] The Earthworm Inoculation Unit (EIU) technique has been suggested as an efficient and cost-friendly method to become an integral component of sustainable land restoration practice.[54]

Hardsetting soil

Hardsetting soils lose their structure when wet and then set hard as they dry out to form a structureless mass that is very difficult to cultivate. They can only be tilled when their moisture content is within a limited range. When they are tilled the result is often a very cloddy surface (poor tilth). As they dry out the high soil strength often restricts seedling and root growth. Infiltration rates are low and runoff of rain and irrigation limits the productivity of many hardsetting soils.[55]

Definition

Hardsetting has been defined this way: "A hardsetting horizon is one that sets to an almost homogeneous mass on drying. It may have occasional cracks, typically at a spacing of >0.1 m. Air dry hardset soil is hard and brittle, and it is not possible to push a forefinger into the profile face. Typically, it has a tensile strength of 90 kN–2. Soils that crust are not necessarily hardsetting since a hardsetting horizon is thicker than a crust. (In cultivated soils the thickness of the hardsetting horizon is frequently equal to or greater than that of the cultivated layer.) Hardsetting soil is not permanently cemented and is soft when wet. The clods in a hardsetting horizon that has been cultivated will partially or totally disintegrate upon wetting. If the soil has been sufficiently wetted, it will revert to its hardset state on drying. This can happen after flood irrigation or a single intense rainfall event."[56]

Soil structure dynamics

Soil structure is inherently a dynamic and complex system that is affected by different factors such as tillage,[57] wheel traffic,[58] root, microbial and faunal activities in soil,[59][60] rainfall events,[61] wind erosion,[62] wetting and drying,[63] freezing and thawing.[31] In turn, reciprocally soil structure interacts and affects the root growth and function,[64] soil fauna and microorganisms,[65][66] water and solute transport processes,[67] gas exchange,[68] thermal conductivity[69] and electrical conductivity,[70] traffic bearing capacity,[71] and many other aspects in relation with soil. Ignoring soil structure or viewing it as "static" can lead to poor predictions of soil properties and might significantly affect the soil management.[72]

See also

References

Template:Reflist

Sources

Template:USGovernment

  • Australian Journal of Soil Research, 38(1) 61 – 70. Cited in: Land and Water Australia 2007, ways to improve soil structure and improve the productivity of irrigated agriculture, viewed May 2007, <https://web.archive.org/web/20070930071224/http://npsi.gov.au/>
  • Department of Land and Water Conservation 1991, "Field indicators of soil structure decline", viewed May 2007
  • Leeper, GW & Uren, NC 1993, 5th edn, Soil science, an introduction, Melbourne University Press, Melbourne
  • Marshall, TJ & Holmes JW, 1979, Soil Physics, Cambridge University Press
  • Script error: No such module "citation/CS1".
  • Charman, PEV & Murphy, BW 1998, 5th edn, Soils, their properties and management, Oxford University Press, Melbourne
  • Firuziaan, M. and Estorff, O., (2002), "Simulation of the Dynamic Behavior of Bedding-Foundation-Soil in the Time Domain", Springer Verlag.

External links

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  60. Script error: No such module "Citation/CS1".
  61. Script error: No such module "Citation/CS1".
  62. Script error: No such module "Citation/CS1".
  63. Script error: No such module "Citation/CS1".
  64. Script error: No such module "Citation/CS1".
  65. Script error: No such module "Citation/CS1".
  66. Script error: No such module "citation/CS1".
  67. Script error: No such module "Citation/CS1".
  68. Script error: No such module "Citation/CS1".
  69. Script error: No such module "Citation/CS1".
  70. Script error: No such module "Citation/CS1".
  71. Script error: No such module "Citation/CS1".
  72. Script error: No such module "citation/CS1".