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The '''soil matrix''' is the solid phase of [[soil]]s, and comprise the solid particles that make up soils. Soil particles can be classified by their chemical composition ([[mineralogy]]) as well as their size. The particle size distribution of a soil, its [[soil texture|texture]], determines many of the properties of that soil, in particular [[hydraulic conductivity]] and [[water potential]],<ref>{{cite journal |last1=Saxton |first1=Keith E. |last2=Rawls |first2=Walter J. |name-list-style=amp |journal=Soil Science Society of America Journal |volume=70 |issue=5 |title=Soil water characteristic estimates by texture and organic matter for hydrologic solutions |url=https://pdfs.semanticscholar.org/5e63/c886c4f68af5e5c242c006d2d882f0a65bfe.pdf |year=2006 |pages=1569–78 |doi=10.2136/sssaj2005.0117 |accessdate=2 September 2018 |citeseerx=10.1.1.452.9733 |bibcode=2006SSASJ..70.1569S }}</ref> but the mineralogy of those particles can strongly modify those properties. The mineralogy of the finest soil particles, clay, is especially important.<ref>{{cite web |last=College of Tropical Agriculture and Human Resources |title=Soil Mineralogy |url=https://www.ctahr.hawaii.edu/mauisoil/a_factor_mineralogy.aspx |website=cms.ctahr.hawaii.edu/ |publisher=University of Hawai‘i at Mānoa |accessdate=2 September 2018}}</ref>
The '''soil matrix''' is the solid phase of [[soil]]s, and comprise the solid particles that make up soils. Soil particles can be classified by their chemical composition ([[mineralogy]]) as well as their size. The particle size distribution of a soil, its [[soil texture|texture]], determines many of the properties of that soil, in particular [[hydraulic conductivity]] and [[water potential]],<ref>{{cite journal |last1=Saxton |first1=Keith E. |last2=Rawls |first2=Walter J. |name-list-style=amp |journal=Soil Science Society of America Journal |volume=70 |issue=5 |title=Soil water characteristic estimates by texture and organic matter for hydrologic solutions |url=https://pdfs.semanticscholar.org/5e63/c886c4f68af5e5c242c006d2d882f0a65bfe.pdf |archive-url=https://web.archive.org/web/20180902183902/https://pdfs.semanticscholar.org/5e63/c886c4f68af5e5c242c006d2d882f0a65bfe.pdf |url-status=dead |archive-date=2 September 2018 |year=2006 |pages=1569–78 |doi=10.2136/sssaj2005.0117 |accessdate=2 September 2018 |citeseerx=10.1.1.452.9733 |bibcode=2006SSASJ..70.1569S }}</ref> but the mineralogy of those particles can strongly modify those properties. The mineralogy of the finest soil particles, clay, is especially important.<ref>{{cite web |last=College of Tropical Agriculture and Human Resources |title=Soil Mineralogy |url=https://www.ctahr.hawaii.edu/mauisoil/a_factor_mineralogy.aspx |website=cms.ctahr.hawaii.edu/ |publisher=University of Hawai‘i at Mānoa |accessdate=2 September 2018}}</ref>


==Gravel, sand and silt==
==Gravel, sand and silt==
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Before the advent of [[X-ray diffraction]] clay was thought to be very small particles of [[quartz]], [[feldspar]], [[mica]], [[hornblende]] or [[augite]], but it is now known to be (with the exception of mica-based clays) a precipitate with a mineralogical composition that is dependent on but different from its parent materials and is classed as a secondary mineral.<ref>{{cite web |last1=Bergaya |first1=Faïza |last2=Beneke |first2=Klaus |last3=Lagaly |first3=Gerhard |title=History and perspectives of clay science |url=http://www.uni-kiel.de/anorg/lagaly/group/klausSchiver/clayhistory.pdf |publisher=[[University of Kiel]] |accessdate=20 October 2018 }}</ref> The type of clay that is formed is a function of the parent material and the composition of the minerals in solution.<ref>{{cite journal |last=Wilson |first=M. Jeff |year=1999 |title=The origin and formation of clay minerals in soils: past, present and future perspectives |journal=Clay Minerals |volume=34 |issue=1 |pages=7–25 |url=http://www.minersoc.org/pages/Archive-CM/Volume_34/34-1-7.pdf |doi=10.1180/000985599545957 |accessdate=20 October 2018 |archive-url=https://web.archive.org/web/20180329061907/http://www.minersoc.org/pages/Archive-CM/Volume_34/34-1-7.pdf |archive-date=29 March 2018 |url-status=dead |bibcode=1999ClMin..34....7W }}</ref> Clay minerals continue to be formed as long as the soil exists.{{sfn|Simonson|1957|p=19}} Mica-based clays result from a modification of the primary mica mineral in such a way that it behaves and is classed as a clay.<ref>{{cite journal |last=Churchman |first=G. Jock |year=1980 |title=Clay minerals formed from micas and chlorites in some New Zealand soils |journal=Clay Minerals |volume=15 |issue=1 |pages=59–76 |url=https://www.researchgate.net/publication/249852539 |doi=10.1180/claymin.1980.015.1.05 |accessdate=20 October 2018 |format=[[Portable Document Format|PDF]]|bibcode=1980ClMin..15...59C }}</ref> Most clays are crystalline, but some clays or some parts of clay minerals are amorphous.<ref>{{cite journal |last1=Wada |first1=Koji |last2=Greenland |first2=Dennis J. |year=1970 |title=Selective dissolution and differential infrared spectroscopy for characterization of 'amorphous' constituents in soil clays |journal=Clay Minerals |volume=8 |issue=3 |pages=241–54 |doi=10.1180/claymin.1970.008.3.02 |citeseerx=10.1.1.624.1439 |bibcode=1970ClMin...8..241W }}</ref> The clays of a soil are a mixture of the various types of clay, but one type predominates.{{sfn|Donahue|Miller|Shickluna|1977|p=102}}
Before the advent of [[X-ray diffraction]] clay was thought to be very small particles of [[quartz]], [[feldspar]], [[mica]], [[hornblende]] or [[augite]], but it is now known to be (with the exception of mica-based clays) a precipitate with a mineralogical composition that is dependent on but different from its parent materials and is classed as a secondary mineral.<ref>{{cite web |last1=Bergaya |first1=Faïza |last2=Beneke |first2=Klaus |last3=Lagaly |first3=Gerhard |title=History and perspectives of clay science |url=http://www.uni-kiel.de/anorg/lagaly/group/klausSchiver/clayhistory.pdf |publisher=[[University of Kiel]] |accessdate=20 October 2018 }}</ref> The type of clay that is formed is a function of the parent material and the composition of the minerals in solution.<ref>{{cite journal |last=Wilson |first=M. Jeff |year=1999 |title=The origin and formation of clay minerals in soils: past, present and future perspectives |journal=Clay Minerals |volume=34 |issue=1 |pages=7–25 |url=http://www.minersoc.org/pages/Archive-CM/Volume_34/34-1-7.pdf |doi=10.1180/000985599545957 |accessdate=20 October 2018 |archive-url=https://web.archive.org/web/20180329061907/http://www.minersoc.org/pages/Archive-CM/Volume_34/34-1-7.pdf |archive-date=29 March 2018 |url-status=dead |bibcode=1999ClMin..34....7W }}</ref> Clay minerals continue to be formed as long as the soil exists.{{sfn|Simonson|1957|p=19}} Mica-based clays result from a modification of the primary mica mineral in such a way that it behaves and is classed as a clay.<ref>{{cite journal |last=Churchman |first=G. Jock |year=1980 |title=Clay minerals formed from micas and chlorites in some New Zealand soils |journal=Clay Minerals |volume=15 |issue=1 |pages=59–76 |url=https://www.researchgate.net/publication/249852539 |doi=10.1180/claymin.1980.015.1.05 |accessdate=20 October 2018 |format=[[Portable Document Format|PDF]]|bibcode=1980ClMin..15...59C }}</ref> Most clays are crystalline, but some clays or some parts of clay minerals are amorphous.<ref>{{cite journal |last1=Wada |first1=Koji |last2=Greenland |first2=Dennis J. |year=1970 |title=Selective dissolution and differential infrared spectroscopy for characterization of 'amorphous' constituents in soil clays |journal=Clay Minerals |volume=8 |issue=3 |pages=241–54 |doi=10.1180/claymin.1970.008.3.02 |citeseerx=10.1.1.624.1439 |bibcode=1970ClMin...8..241W }}</ref> The clays of a soil are a mixture of the various types of clay, but one type predominates.{{sfn|Donahue|Miller|Shickluna|1977|p=102}}


Typically there are four main groups of clay minerals: [[kaolinite]], [[montmorillonite]]-[[smectite]], [[illite]], and [[chlorite]].<ref>{{cite web |title=The clay mineral group |url=http://www.galleries.com/Clays_Group |publisher=Amethyst Galleries, Inc. |accessdate=28 October 2018 |format=[[Portable Document Format|PDF]]}}</ref> Most clays are crystalline and most are made up of three or four planes of oxygen held together by planes of aluminium and silicon by way of ionic bonds that together form a single layer of clay. The spatial arrangement of the oxygen atoms determines clay's structure.<ref>{{cite book |last=Schulze |first=Darrell G. |date=2005 |chapter=Clay minerals |doi=10.1016/b0-12-348530-4/00189-2 |title=Encyclopedia of soils in the environment |editor-last=Hillel |editor-first=Daniel |publisher=Academic Press |location=Amsterdam |pages=246–54 |chapter-url=http://www.geoinfo.amu.edu.pl/geoinf/m/GLEB/1b%20Clay%20minerals_EncSoilEnv_SCHULZE%2005.pdf |accessdate=28 October 2018 |isbn=9780123485304 }}</ref> Half of the weight of clay is oxygen, but on a volume basis oxygen is ninety percent.{{sfn|Russell|1957|p=33}} The layers of clay are sometimes held together through [[hydrogen bonds]], sodium or potassium bridges and as a result will swell less in the presence of water.<ref>{{cite journal |last1=Tambach |first1=Tim J. |last2=Bolhuis |first2=Peter G. |last3=Hensen |first3=Emiel J.M. |last4=Smit |first4=Berend |year=2006 |title=Hysteresis in clay swelling induced by hydrogen bonding: accurate prediction of swelling states |journal=[[Langmuir (journal)|Langmuir]] |volume=22 |issue=3 |pages=1223–34 |url=https://pdfs.semanticscholar.org/8012/819c1e06adc056ea770fae7f68adca09e61f.pdf |doi=10.1021/la051367q |pmid=16430287 |accessdate=3 November 2018 }}</ref> Clays such as [[montmorillonite]] have layers that are loosely attached and will swell greatly when water intervenes between the layers.{{sfn|Donahue|Miller|Shickluna|1977|pp=102–07}}
Typically there are four main groups of clay minerals: [[kaolinite]], [[montmorillonite]]-[[smectite]], [[illite]], and [[chlorite]].<ref>{{cite web |title=The clay mineral group |url=http://www.galleries.com/Clays_Group |publisher=Amethyst Galleries, Inc. |accessdate=28 October 2018 |format=[[Portable Document Format|PDF]]}}</ref> Most clays are crystalline and most are made up of three or four planes of oxygen held together by planes of aluminium and silicon by way of ionic bonds that together form a single layer of clay. The spatial arrangement of the oxygen atoms determines clay's structure.<ref>{{cite book |last=Schulze |first=Darrell G. |date=2005 |chapter=Clay minerals |doi=10.1016/b0-12-348530-4/00189-2 |title=Encyclopedia of soils in the environment |editor-last=Hillel |editor-first=Daniel |publisher=Academic Press |location=Amsterdam |pages=246–54 |chapter-url=http://www.geoinfo.amu.edu.pl/geoinf/m/GLEB/1b%20Clay%20minerals_EncSoilEnv_SCHULZE%2005.pdf |accessdate=28 October 2018 |isbn=9780123485304 }}</ref> Half of the weight of clay is oxygen, but on a volume basis oxygen is ninety percent.{{sfn|Russell|1957|p=33}} The layers of clay are sometimes held together through [[hydrogen bonds]], sodium or potassium bridges and as a result will swell less in the presence of water.<ref>{{cite journal |last1=Tambach |first1=Tim J. |last2=Bolhuis |first2=Peter G. |last3=Hensen |first3=Emiel J.M. |last4=Smit |first4=Berend |year=2006 |title=Hysteresis in clay swelling induced by hydrogen bonding: accurate prediction of swelling states |journal=[[Langmuir (journal)|Langmuir]] |volume=22 |issue=3 |pages=1223–34 |url=https://pdfs.semanticscholar.org/8012/819c1e06adc056ea770fae7f68adca09e61f.pdf |archive-url=https://web.archive.org/web/20181103210124/https://pdfs.semanticscholar.org/8012/819c1e06adc056ea770fae7f68adca09e61f.pdf |url-status=dead |archive-date=3 November 2018 |doi=10.1021/la051367q |pmid=16430287 |accessdate=3 November 2018 }}</ref> Clays such as [[montmorillonite]] have layers that are loosely attached and will swell greatly when water intervenes between the layers.{{sfn|Donahue|Miller|Shickluna|1977|pp=102–07}}


In a wider sense clays can be classified as:
In a wider sense clays can be classified as:
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* '''Vermiculite''' is a mica-based clay similar to illite, but the crystals of clay are held together more loosely by hydrated magnesium and it will swell, but not as much as does montmorillonite.<ref>{{cite journal |last1=Norrish |first1=Keith |last2=Rausell-Colom |first2=José Antonio |year=1961 |title=Low-angle X-ray diffraction studies of the swelling of montmorillonite and vermiculite |journal=Clays and Clay Minerals |volume=10 |issue=1 |pages=123–49 |doi=10.1346/CCMN.1961.0100112 |bibcode=1961CCM....10..123N |doi-access=free }}</ref> It has very high CEC.{{sfn|Donahue|Miller|Shickluna|1977|p=110}}{{sfn|Coleman|Mehlich|1957|p=73}}{{sfn|Allison|1957|p=90}}{{sfn|Reitemeier|1957|p=103}}
* '''Vermiculite''' is a mica-based clay similar to illite, but the crystals of clay are held together more loosely by hydrated magnesium and it will swell, but not as much as does montmorillonite.<ref>{{cite journal |last1=Norrish |first1=Keith |last2=Rausell-Colom |first2=José Antonio |year=1961 |title=Low-angle X-ray diffraction studies of the swelling of montmorillonite and vermiculite |journal=Clays and Clay Minerals |volume=10 |issue=1 |pages=123–49 |doi=10.1346/CCMN.1961.0100112 |bibcode=1961CCM....10..123N |doi-access=free }}</ref> It has very high CEC.{{sfn|Donahue|Miller|Shickluna|1977|p=110}}{{sfn|Coleman|Mehlich|1957|p=73}}{{sfn|Allison|1957|p=90}}{{sfn|Reitemeier|1957|p=103}}
* '''Chlorite''' is similar to vermiculite, but the loose bonding by occasional hydrated magnesium, as in vermiculite, is replaced by a hydrated magnesium sheet, that firmly bonds the planes above and below it. It has two planes of silicon, one of aluminium and one of magnesium; hence it is a 2:2 clay.<ref>{{cite book |last1=Moore |first1=Duane M. |last2=Reynolds |first2=Robert C. Jr |date=1997 |title=X-ray diffraction and the identification and analysis of clay minerals |publisher=[[Oxford University Press]] |location=Oxford|url=http://www.labpku.com/UploadFiles/2014-01/admin/2014011016073967283.pdf |accessdate=16 December 2018 }}</ref> Chlorite does not swell and it has low CEC.{{sfn|Donahue|Miller|Shickluna|1977|p=110}}{{sfn|Holmes|Brown|1957|p=112}}
* '''Chlorite''' is similar to vermiculite, but the loose bonding by occasional hydrated magnesium, as in vermiculite, is replaced by a hydrated magnesium sheet, that firmly bonds the planes above and below it. It has two planes of silicon, one of aluminium and one of magnesium; hence it is a 2:2 clay.<ref>{{cite book |last1=Moore |first1=Duane M. |last2=Reynolds |first2=Robert C. Jr |date=1997 |title=X-ray diffraction and the identification and analysis of clay minerals |publisher=[[Oxford University Press]] |location=Oxford|url=http://www.labpku.com/UploadFiles/2014-01/admin/2014011016073967283.pdf |accessdate=16 December 2018 }}</ref> Chlorite does not swell and it has low CEC.{{sfn|Donahue|Miller|Shickluna|1977|p=110}}{{sfn|Holmes|Brown|1957|p=112}}
* '''Kaolinite''' is very common, highly weathered clay, and more common than montmorillonite in acid soils.<ref>{{cite journal |last1=Karathanasis |first1=Anastasios D. |last2=Hajek |first2=Benjamin F. |year=1983 |title=Transformation of smectite to kaolinite in naturally acid soil systems: structural and thermodynamic considerations |journal=[[Soil Science Society of America Journal]] |volume=47 |issue=1 |pages=158–63 |doi=10.2136/sssaj1983.03615995004700010031x|bibcode=1983SSASJ..47..158K }}</ref> It has one silica and one alumina plane per crystal; hence it is a 1:1 type clay. One plane of silica of montmorillonite is dissolved and is replaced with hydroxyls, which produces strong hydrogen bonds to the oxygen in the next crystal of clay.<ref>{{cite journal |last1=Tombácz |first1=Etelka |last2=Szekeres |first2= Márta |year=2006 |title=Surface charge heterogeneity of kaolinite in aqueous suspension in comparison with montmorillonite |journal=Applied Clay Science |volume=34 |issue=1–4 |pages=105–24 |url=https://www.academia.edu/11482380 |doi=10.1016/j.clay.2006.05.009 |accessdate=16 February 2019 |format=[[Portable Document Format|PDF]]}}</ref> As a result, kaolinite does not swell in water and has a low specific surface area, and as almost no isomorphous substitution has occurred it has a low CEC.<ref>{{cite journal |last1=Coles |first1=Cynthia A. |last2=Yong |first2=Raymond N. |year=2002 |title=Aspects of kaolinite characterization and retention of Pb and Cd |journal=Applied Clay Science |volume=22 |issue=1–2 |pages=39–45 |url=https://pdfs.semanticscholar.org/0a67/90d14853df562568cd6ceaa17689cf08a55d.pdf |doi=10.1016/S0169-1317(02)00110-2 |accessdate=24 February 2019 |citeseerx=10.1.1.576.3783 }}</ref> Where rainfall is high, acid soils selectively leach more silica than alumina from the original clays, leaving kaolinite.<ref>{{cite journal |last1=Fisher |first1=G. Burch |last2=Ryan |first2=Peter C. |year=2006 |title=The smectite-to-disordered kaolinite transition in a tropical soil chronosequence, Pacific coast, Costa Rica |journal=Clays and Clay Minerals |volume=54 |issue=5 |pages=571–86 |url=https://www.researchgate.net/publication/240744358 |doi=10.1346/CCMN.2006.0540504 |accessdate=24 February 2019 |format=[[Portable Document Format|PDF]]|bibcode=2006CCM....54..571F }}</ref> Even heavier weathering results in sesquioxide clays.{{sfn|Donahue|Miller|Shickluna|1977|p=111}}{{sfn|Russell|1957|p=33}}{{sfn|Coleman|Mehlich|1957|p=74}}{{sfn|Dean|1957|p=82}}{{sfn|Olsen|Fried|1957|p=96}}{{sfn|Reitemeier|1957|p=101}}
* '''Kaolinite''' is very common, highly weathered clay, and more common than montmorillonite in acid soils.<ref>{{cite journal |last1=Karathanasis |first1=Anastasios D. |last2=Hajek |first2=Benjamin F. |year=1983 |title=Transformation of smectite to kaolinite in naturally acid soil systems: structural and thermodynamic considerations |journal=[[Soil Science Society of America Journal]] |volume=47 |issue=1 |pages=158–63 |doi=10.2136/sssaj1983.03615995004700010031x|bibcode=1983SSASJ..47..158K }}</ref> It has one silica and one alumina plane per crystal; hence it is a 1:1 type clay. One plane of silica of montmorillonite is dissolved and is replaced with hydroxyls, which produces strong hydrogen bonds to the oxygen in the next crystal of clay.<ref>{{cite journal |last1=Tombácz |first1=Etelka |last2=Szekeres |first2= Márta |year=2006 |title=Surface charge heterogeneity of kaolinite in aqueous suspension in comparison with montmorillonite |journal=Applied Clay Science |volume=34 |issue=1–4 |pages=105–24 |url=https://www.academia.edu/11482380 |doi=10.1016/j.clay.2006.05.009 |accessdate=16 February 2019 |format=[[Portable Document Format|PDF]]}}</ref> As a result, kaolinite does not swell in water and has a low specific surface area, and as almost no isomorphous substitution has occurred it has a low CEC.<ref>{{cite journal |last1=Coles |first1=Cynthia A. |last2=Yong |first2=Raymond N. |year=2002 |title=Aspects of kaolinite characterization and retention of Pb and Cd |journal=Applied Clay Science |volume=22 |issue=1–2 |pages=39–45 |url=https://pdfs.semanticscholar.org/0a67/90d14853df562568cd6ceaa17689cf08a55d.pdf |archive-url=https://web.archive.org/web/20190224231236/https://pdfs.semanticscholar.org/0a67/90d14853df562568cd6ceaa17689cf08a55d.pdf |url-status=dead |archive-date=24 February 2019 |doi=10.1016/S0169-1317(02)00110-2 |accessdate=24 February 2019 |citeseerx=10.1.1.576.3783 }}</ref> Where rainfall is high, acid soils selectively leach more silica than alumina from the original clays, leaving kaolinite.<ref>{{cite journal |last1=Fisher |first1=G. Burch |last2=Ryan |first2=Peter C. |year=2006 |title=The smectite-to-disordered kaolinite transition in a tropical soil chronosequence, Pacific coast, Costa Rica |journal=Clays and Clay Minerals |volume=54 |issue=5 |pages=571–86 |url=https://www.researchgate.net/publication/240744358 |doi=10.1346/CCMN.2006.0540504 |accessdate=24 February 2019 |format=[[Portable Document Format|PDF]]|bibcode=2006CCM....54..571F }}</ref> Even heavier weathering results in sesquioxide clays.{{sfn|Donahue|Miller|Shickluna|1977|p=111}}{{sfn|Russell|1957|p=33}}{{sfn|Coleman|Mehlich|1957|p=74}}{{sfn|Dean|1957|p=82}}{{sfn|Olsen|Fried|1957|p=96}}{{sfn|Reitemeier|1957|p=101}}


===Crystalline chain clays===
===Crystalline chain clays===
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==Organic colloids==
==Organic colloids==
[[Humus]] is one of the two final stages of [[decomposition]] of organic matter. It remains in the soil as the organic component of the soil matrix while the other stage, [[carbon dioxide]], is freely liberated in the [[atmosphere]] or reacts with [[calcium]] to form the soluble [[calcium bicarbonate]]. While humus may linger for a thousand years,<ref>{{cite book |last1=Paul |first1=Eldor A. |last2=Campbell |first2=Colin A. |last3=Rennie |first3=David A. |last4=McCallum |first4=Kenneth J. |name-list-style=amp |date=1964 |chapter=Investigations of the dynamics of soil humus utilizing carbon dating techniques |title=Transactions of the 8th International Congress of Soil Science, Bucharest, Romania, 1964 |publisher=Publishing House of the Academy of the Socialist Republic of Romania |location=Bucharest, Romania |pages=201–08 |chapter-url=http://www.nrel.colostate.edu/assets/nrel_files/labs/paul-lab/docs/NREL_Paul_Paul_8th_ICSS.pdf |accessdate=16 March 2019 }}</ref> on the larger scale of the age of the mineral soil components, it is temporary, being finally released as CO<sub>2</sub>. It is composed of the very stable [[lignin]]s (30%) and complex [[sugars]] (polyuronides, 30%), [[proteins]] (30%), [[waxes]], and [[fat]]s that are resistant to breakdown by microbes and can form [[metal complexes|complexes with metals]], facilitating their downward migration ([[podzolization]]).<ref>{{cite journal |last1=Bin |first1=Gao |last2=Cao |first2=Xinde |last3=Dong |first3=Yan |last4=Luo |first4=Yongming |last5=Ma |first5=Lena Q. |name-list-style=amp |year=2011 |title=Colloid deposition and release in soils and their association with heavy metals |journal=Critical Reviews in Environmental Science and Technology |volume=41 |issue=4 |pages=336–72 |url=https://pdfs.semanticscholar.org/337c/26d44a43150e9d5eca46e4ba80a4849aff1b.pdf?_ga=2.265737423.1754694067.1553360310-127282468.1551019891 |doi=10.1080/10643380902871464 |accessdate=24 March 2019 |format=[[Portable Document Format|PDF]]}}</ref> However, although originating for its main part from dead plant organs (wood, bark, foliage, roots), a large part of humus comes from organic compounds excreted by soil organisms (roots, microbes, animals) and from their decomposition upon death.<ref>{{cite journal |last1=Six |first1=Johan |last2=Frey |first2=Serita D. |last3=Thiet |first3=Rachel K. |last4=Batten |first4=Katherine M. |name-list-style=amp |year=2006 |title=Bacterial and fungal contributions to carbon sequestration in agroecosystems |journal=[[Soil Science Society of America Journal]] |volume=70 |issue=2 |pages=555–69 |url=https://pdfs.semanticscholar.org/65a5/f3923273bab7658b7b4a0775163c767595d4.pdf |doi=10.2136/sssaj2004.0347 |accessdate=16 March 2019 |bibcode=2006SSASJ..70..555S |citeseerx=10.1.1.461.9539 }}</ref> Its chemical assay is 60% carbon, 5% nitrogen, some oxygen and the remainder hydrogen, sulfur, and phosphorus. On a dry weight basis, the [[Cation-exchange capacity|CEC]] of humus is many times greater than that of clay.{{sfn|Donahue|Miller|Shickluna|1977|p=112}}{{sfn|Russell|1957|p=35}}{{sfn|Allaway|1957|p=69}}
[[Humus]] is one of the two final stages of [[decomposition]] of organic matter. It remains in the soil as the organic component of the soil matrix while the other stage, [[carbon dioxide]], is freely liberated in the [[atmosphere]] or reacts with [[calcium]] to form the soluble [[calcium bicarbonate]]. While humus may linger for a thousand years,<ref>{{cite book |last1=Paul |first1=Eldor A. |last2=Campbell |first2=Colin A. |last3=Rennie |first3=David A. |last4=McCallum |first4=Kenneth J. |name-list-style=amp |date=1964 |chapter=Investigations of the dynamics of soil humus utilizing carbon dating techniques |title=Transactions of the 8th International Congress of Soil Science, Bucharest, Romania, 1964 |publisher=Publishing House of the Academy of the Socialist Republic of Romania |location=Bucharest, Romania |pages=201–08 |chapter-url=http://www.nrel.colostate.edu/assets/nrel_files/labs/paul-lab/docs/NREL_Paul_Paul_8th_ICSS.pdf |accessdate=16 March 2019 }}</ref> on the larger scale of the age of the mineral soil components, it is temporary, being finally released as CO<sub>2</sub>. It is composed of the very stable [[lignin]]s (30%) and complex [[sugars]] (polyuronides, 30%), [[proteins]] (30%), [[waxes]], and [[fat]]s that are resistant to breakdown by microbes and can form [[metal complexes|complexes with metals]], facilitating their downward migration ([[podzolization]]).<ref>{{cite journal |last1=Bin |first1=Gao |last2=Cao |first2=Xinde |last3=Dong |first3=Yan |last4=Luo |first4=Yongming |last5=Ma |first5=Lena Q. |name-list-style=amp |year=2011 |title=Colloid deposition and release in soils and their association with heavy metals |journal=Critical Reviews in Environmental Science and Technology |volume=41 |issue=4 |pages=336–72 |url=https://pdfs.semanticscholar.org/337c/26d44a43150e9d5eca46e4ba80a4849aff1b.pdf |doi=10.1080/10643380902871464 |accessdate=24 March 2019 |format=[[Portable Document Format|PDF]]}}</ref> However, although originating for its main part from dead plant organs (wood, bark, foliage, roots), a large part of humus comes from organic compounds excreted by soil organisms (roots, microbes, animals) and from their decomposition upon death.<ref>{{cite journal |last1=Six |first1=Johan |last2=Frey |first2=Serita D. |last3=Thiet |first3=Rachel K. |last4=Batten |first4=Katherine M. |name-list-style=amp |year=2006 |title=Bacterial and fungal contributions to carbon sequestration in agroecosystems |journal=[[Soil Science Society of America Journal]] |volume=70 |issue=2 |pages=555–69 |url=https://pdfs.semanticscholar.org/65a5/f3923273bab7658b7b4a0775163c767595d4.pdf |archive-url=https://web.archive.org/web/20200722042852/https://pdfs.semanticscholar.org/65a5/f3923273bab7658b7b4a0775163c767595d4.pdf |url-status=dead |archive-date=22 July 2020 |doi=10.2136/sssaj2004.0347 |accessdate=16 March 2019 |bibcode=2006SSASJ..70..555S |citeseerx=10.1.1.461.9539 }}</ref> Its chemical assay is 60% carbon, 5% nitrogen, some oxygen and the remainder hydrogen, sulfur, and phosphorus. On a dry weight basis, the [[Cation-exchange capacity|CEC]] of humus is many times greater than that of clay.{{sfn|Donahue|Miller|Shickluna|1977|p=112}}{{sfn|Russell|1957|p=35}}{{sfn|Allaway|1957|p=69}}


Humus plays a major role in the regulation of [[Carbon dioxide in Earth's atmosphere|atmospheric carbon]], through [[carbon sequestration]] in the soil profile, more especially in deeper horizons with reduced [[biological activity]].<ref>{{cite journal |last1=Thornton |first1=Peter E. |last2=Doney |first2=Scott C. |last3=Lindsay |first3=Konkel |last4=Moore |first4=J. Keith |last5=Mahowald |first5=Natalie |last6=Randerson |first6=James T. |last7=Fung |first7=Inez |last8=Lamarque |first8=Jean-François |last9=Feddema |first9=Johannes J. |last10=Lee |first10=Y. Hanna |name-list-style=amp |year=2009 |title=Carbon-nitrogen interactions regulate climate-carbon cycle feedbacks: results from an atmosphere-ocean general circulation model |journal=[[Biogeosciences]] |volume=6 |issue=10 |pages=2099–120 |doi=10.5194/bg-6-2099-2009 |bibcode=2009BGeo....6.2099T |doi-access=free }}</ref> Stocking and destocking of soil carbon are under strong climate influence.<ref>{{cite journal |last1=Morgan |first1=Jack A. |last2=Follett |first2=Ronald F. |last3=Allen Jr |first3=Leon Hartwell |last4=Del Grosso |first4= Stephen |last5=Derner |first5=Justin D. |last6=Dijkstra |first6=Feike |last7=Franzluebbers |first7=Alan |last8=Fry |first8=Robert |last9=Paustian |first9=Keith |last10=Schoeneberger |first10=Michele M. |name-list-style=amp |year=2010 |title=Carbon sequestration in agricultural lands of the United States |journal=[[Journal of Soil and Water Conservation]] |volume=65 |issue=1 |pages=6A–13A |url=https://www.srs.fs.fed.us/pubs/ja/2010/ja_2010_morgan_001.pdf |doi=10.2489/jswc.65.1.6A |accessdate=24 March 2019 }}</ref> They are normally balanced through an equilibrium between [[Primary production|production]] and [[Mineralization (soil science)|mineralization]] of organic matter, but the balance is in favour of destocking under present-day [[climate warming]],<ref>{{cite journal |last1=Parton |first1=Willam J. |last2=Scurlock |first2=Jonathan M. O. |last3=Ojima |first3=Dennis S. |last4=Schimel |first4=David |last5=Hall |first5=David O. |last6=The SCOPEGRAM Group |name-list-style=amp |year=1995 |title=Impact of climate change on grassland production and soil carbon worldwide |journal=[[Global Change Biology]] |volume=1 |issue=1 |pages=13–22 |url=https://www.researchgate.net/publication/233714480 |doi=10.1111/j.1365-2486.1995.tb00002.x |accessdate=24 March 2019 |format=[[Portable Document Format|PDF]]|bibcode=1995GCBio...1...13P }}</ref> and more especially in [[permafrost]].<ref>{{cite journal |last1=Schuur |first1=Edward A. G. |last2=Vogel |first2=Jason G. |last3=Crummer |first3=Kathryn G. |last4=Lee |first4=Hanna |last5=Sickman |first5=James O. |last6=Osterkamp |first6=T. E. |name-list-style=amp |year=2009 |title=The effect of permafrost thaw on old carbon release and net carbon exchange from tundra |journal=[[Nature (journal)|Nature]] |volume=459 |issue=7246 |pages=556–59 |url=https://www.academia.edu/18296573 |doi=10.1038/nature08031 |pmid=19478781 |accessdate=24 March 2019 |format=[[Portable Document Format|PDF]]|bibcode=2009Natur.459..556S }}</ref>
Humus plays a major role in the regulation of [[Carbon dioxide in Earth's atmosphere|atmospheric carbon]], through [[carbon sequestration]] in the soil profile, more especially in deeper horizons with reduced [[biological activity]].<ref>{{cite journal |last1=Thornton |first1=Peter E. |last2=Doney |first2=Scott C. |last3=Lindsay |first3=Konkel |last4=Moore |first4=J. Keith |last5=Mahowald |first5=Natalie |last6=Randerson |first6=James T. |last7=Fung |first7=Inez |last8=Lamarque |first8=Jean-François |last9=Feddema |first9=Johannes J. |last10=Lee |first10=Y. Hanna |name-list-style=amp |year=2009 |title=Carbon-nitrogen interactions regulate climate-carbon cycle feedbacks: results from an atmosphere-ocean general circulation model |journal=[[Biogeosciences]] |volume=6 |issue=10 |pages=2099–120 |doi=10.5194/bg-6-2099-2009 |bibcode=2009BGeo....6.2099T |doi-access=free }}</ref> Stocking and destocking of soil carbon are under strong climate influence.<ref>{{cite journal |last1=Morgan |first1=Jack A. |last2=Follett |first2=Ronald F. |last3=Allen Jr |first3=Leon Hartwell |last4=Del Grosso |first4= Stephen |last5=Derner |first5=Justin D. |last6=Dijkstra |first6=Feike |last7=Franzluebbers |first7=Alan |last8=Fry |first8=Robert |last9=Paustian |first9=Keith |last10=Schoeneberger |first10=Michele M. |name-list-style=amp |year=2010 |title=Carbon sequestration in agricultural lands of the United States |journal=[[Journal of Soil and Water Conservation]] |volume=65 |issue=1 |pages=6A–13A |url=https://www.srs.fs.fed.us/pubs/ja/2010/ja_2010_morgan_001.pdf |doi=10.2489/jswc.65.1.6A |accessdate=24 March 2019 }}</ref> They are normally balanced through an equilibrium between [[Primary production|production]] and [[Mineralization (soil science)|mineralization]] of organic matter, but the balance is in favour of destocking under present-day [[climate warming]],<ref>{{cite journal |last1=Parton |first1=Willam J. |last2=Scurlock |first2=Jonathan M. O. |last3=Ojima |first3=Dennis S. |last4=Schimel |first4=David |last5=Hall |first5=David O. |last6=The SCOPEGRAM Group |name-list-style=amp |year=1995 |title=Impact of climate change on grassland production and soil carbon worldwide |journal=[[Global Change Biology]] |volume=1 |issue=1 |pages=13–22 |url=https://www.researchgate.net/publication/233714480 |doi=10.1111/j.1365-2486.1995.tb00002.x |accessdate=24 March 2019 |format=[[Portable Document Format|PDF]]|bibcode=1995GCBio...1...13P }}</ref> and more especially in [[permafrost]].<ref>{{cite journal |last1=Schuur |first1=Edward A. G. |last2=Vogel |first2=Jason G. |last3=Crummer |first3=Kathryn G. |last4=Lee |first4=Hanna |last5=Sickman |first5=James O. |last6=Osterkamp |first6=T. E. |name-list-style=amp |year=2009 |title=The effect of permafrost thaw on old carbon release and net carbon exchange from tundra |journal=[[Nature (journal)|Nature]] |volume=459 |issue=7246 |pages=556–59 |url=https://www.academia.edu/18296573 |doi=10.1038/nature08031 |pmid=19478781 |accessdate=24 March 2019 |format=[[Portable Document Format|PDF]]|bibcode=2009Natur.459..556S }}</ref>


==Carbon and terra preta==
==Carbon and terra preta==
In the extreme environment of high temperatures and the leaching caused by the heavy rain of [[tropical rain forests]], the clay and organic colloids are largely destroyed. The heavy rains wash the [[alumino-silicate]] clays from the soil leaving only [[sesquioxide]] clays of low [[Cation-exchange capacity|CEC]]. The high temperatures and humidity allow bacteria and fungi to virtually decay any organic matter on the rain-forest [[Forest floor|floor]] overnight and much of the nutrients are volatilized or leached from the soil and lost,<ref>{{cite journal |last1=Wieder |first1=William R. |last2=Cleveland |first2=Cory C. |last3=Townsend |first3=Alan R. |name-list-style=amp |year=2009 |title=Controls over leaf litter decomposition in wet tropical forests |journal=[[Ecology (journal)|Ecology]] |volume=90 |issue=12 |pages=3333–41 |url=https://scholarworks.umt.edu/cgi/viewcontent.cgi?article=1009&context=decs_pubs |doi=10.1890/08-2294.1 |pmid=20120803 |accessdate=31 March 2019 |format=[[Portable Document Format|PDF]]}}</ref> leaving only a thin root mat lying directly on the mineral soil.<ref>{{cite journal |last1=Stark |first1=Nellie M. |last2=Lordan |first2=Carl F. |name-list-style=amp |year=1978 |title=Nutrient retention by the root mat of an Amazonian rain forest |journal=[[Ecology (journal)|Ecology]] |volume=59 |issue=3 |pages=434–37 |url=http://w3.marietta.edu/~biol/102online/tropicalrainforest.pdf |doi=10.2307/1936571 |accessdate=31 March 2019 |jstor=1936571 |archive-url=https://web.archive.org/web/20190331102112/http://w3.marietta.edu/~biol/102online/tropicalrainforest.pdf |archive-date=31 March 2019 |url-status=dead }}</ref> However, carbon in the form of finely divided [[charcoal]], also known as [[black carbon]], is far more stable than soil colloids and is capable of performing many of the functions of the soil colloids of sub-tropical soils.<ref>{{cite journal |last1=Liang |first1=Biqing |last2=Lehmann |first2=Johannes |last3=Solomon |first3=Dawit |last4=Kinyangi |first4=James |last5=Grossman |first5=Julie |last6=O'Neill |first6=Brendan |last7=Skjemstad |first7=Jan O. |last8=Thies |first8=Janice |last9=Luizaõ |first9=Flávio J. |last10=Petersen |first10=Julie |last11=Neves |first11=Eduardo G. |name-list-style=amp |year=2006 |title=Black carbon increases cation exchange capacity in soils |journal=[[Soil Science Society of America Journal]] |volume=70 |issue=5 |pages=1719–30 |url=http://xrm.phys.northwestern.edu/research/pdf_papers/2006/liang_sssaj_2006.pdf |doi=10.2136/sssaj2005.0383 |accessdate=30 March 2019 |bibcode=2006SSASJ..70.1719L }}</ref> Soil containing substantial quantities of charcoal, of an anthropogenic origin, is called [[terra preta]]. In [[Amazonia]] it testifies for the agronomic knowledge of past [[Amerindian]] civilizations.<ref>{{cite book |last1=Neves |first1=Eduardo G. |last2=Petersen |first2=James B. |last3=Bartone |first3=Robert N. |last4=da Silva |first4=Carlos Augusto |date=2003 |chapter=Historical and socio-cultural origins of Amazonian Dark Earth |title=Amazonian Dark Earths: origin, properties, management |editor-last1=Lehmann |editor-first1=Johannes |editor-last2=Kern |editor-first2=Dirse C. |editor-last3=Glaser |editor-first3=Bruno |editor-last4=Woods |editor-first4=William I. |publisher=[[Springer Science & Business Media]] |location=Berlin, Germany |pages=29–50 |chapter-url=https://www.researchgate.net/publication/226546157 |accessdate=7 April 2019 |chapter-format=[[Portable Document Format|PDF]]}}</ref> The [[pantropical]] peregrine earthworm ''Pontoscolex corethrurus'' has been suspected to contribute to the fine division of charcoal and its mixing to the mineral soil in the frame of present-day [[slash-and-burn]] or [[shifting cultivation]] still practiced by Amerindian tribes.<ref>{{cite journal |last1=Ponge |first1=Jean-François |last2=Topoliantz |first2=Stéphanie |last3=Ballof |first3=Sylvain |last4=Rossi |first4=Jean-Pierre |last5=Lavelle |first5=Patrick |last6=Betsch |first6=Jean-Marie |last7=Gaucher |first7=Philippe |name-list-style=amp |year=2006 |title=Ingestion of charcoal by the Amazonian earthworm Pontoscolex corethrurus: a potential for tropical soil fertility |journal=Soil Biology and Biochemistry |volume=38 |issue=7 |pages=2008–09 |url=https://www.researchgate.net/publication/44735820 |doi=10.1016/j.soilbio.2005.12.024 |accessdate=7 April 2019 |format=[[Portable Document Format|PDF]]}}</ref> Research into terra preta is still young but is promising. [[Fallow]] periods "on the Amazonian Dark Earths can be as short as 6 months, whereas fallow periods on [[oxisol]]s are usually 8 to 10 years long"<ref>{{cite web|last=Lehmann |first=Johannes|title=Terra Preta de Indio |url=http://www.css.cornell.edu/faculty/lehmann/research/terra%20preta/terrapretamain.html |publisher=University of Cornell, Department of Crop and Soil Sciences |accessdate=7 April 2019 |url-status=live |archiveurl=https://web.archive.org/web/20130424061552/http://www.css.cornell.edu/faculty/lehmann/research/terra%20preta/terrapretamain.html |archivedate=24 April 2013 }}</ref> The incorporation of charcoal to agricultural soil for improving water and nutrient retention has been called [[biochar]], being extended to other charred or carbon-rich by-products, and is now increasingly used in [[Sustainable agriculture|sustainable]] [[tropical agriculture]].<ref>{{cite book |last1=Lehmann |first1=Johannes |last2=Rondon |first2=Marco |date=2006 |chapter=Bio-char soil management on highly weathered soils in the humid tropics |title=Biological approaches to sustainable soil systems |editor-last1=Uphoff |editor-first1=Norman |editor-last2=Ball |editor-first2=Andrew S. |editor-last3=Fernandes |editor-first3=Erick |editor-last4=Herren |editor-first4=Hans |editor-last5=Husson |editor-first5=Olivier |editor-last6=Laing |editor-first6=Mark |editor-last7=Palm |editor-first7=Cheryl |editor-last8=Pretty |editor-first8=Jules |editor-last9=Sánchez |editor-first9=Pedro |editor-last10=Sanginga |editor-first10=Nteranya |editor-last11=Thies |editor-first11=Janice |publisher=[[CRC Press]] |location=Boca Raton, Florid |pages=517–30 |chapter-url=https://www.researchgate.net/publication/201998979 |accessdate=14 April 2019 |chapter-format=[[Portable Document Format|PDF]]}}</ref> Biochar also allows the irreversible sorption of pesticides and other pollutants, a mechanism by which their mobility, and thus their environmental risk, decreases.<ref>{{cite journal |last1=Yu |first1=Xiangyang |last2=Pan |first2=Ligang |last3=Ying |first3=Guangguo |last4=Kookana |first4=Rai S. |name-list-style=amp |year=2010 |title=Enhanced and irreversible sorption of pesticide pyrimethanil by soil amended with biochars |journal=Journal of Environmental Sciences |volume=22 |issue=4 |pages=615–20 |url=http://www.jesc.ac.cn/jesc_En/ch/reader/create_pdf.aspx?file_no=2010220420&year_id=2010&quarter_id=4&falg=1 |doi=10.1016/S1001-0742(09)60153-4 |pmid=20617740 |accessdate=14 April 2019 |format=[[Portable Document Format|PDF]] }}{{Dead link|date=June 2020 |bot=InternetArchiveBot |fix-attempted=yes }}</ref> It has also been argued as a mean of [[Carbon sequestration|sequestering]] more carbon in the soil, thereby mitigating the so-called [[greenhouse effect]].<ref>{{cite journal |last1=Whitman |first1=Thea |last2=Lehmann |first2=Johannes |name-list-style=amp |year=2009 |title=Biochar: one way forward for soil carbon in offset mechanisms in Africa? |journal=Environmental Science and Policy |volume=12 |issue=7 |pages=1024–27 |url=https://pdfs.semanticscholar.org/c196/57fc5fd4d88c9f5acf51fdb3e31dc6f8ae04.pdf |doi=10.1016/j.envsci.2009.07.013 |accessdate=14 April 2019 }}</ref> However, the use of biochar is limited by the availability of wood or other products of [[pyrolysis]] and by risks caused by concomitent [[deforestation]].<ref>{{cite journal |last=Mwampamba |first=Tuyeni Heita |year=2007 |title=Has the woodfuel crisis returned? Urban charcoal consumption in Tanzania and its implications to present and future forest availability |journal=Energy Policy |volume=35 |issue=8 |pages=4221–34 |url=https://www.academia.edu/3076522 |doi= 10.1016/j.enpol.2007.02.010|accessdate=14 April 2019 |format=[[Portable Document Format|PDF]]}}</ref>
In the extreme environment of high temperatures and the leaching caused by the heavy rain of [[tropical rain forests]], the clay and organic colloids are largely destroyed. The heavy rains wash the [[alumino-silicate]] clays from the soil leaving only [[sesquioxide]] clays of low [[Cation-exchange capacity|CEC]]. The high temperatures and humidity allow bacteria and fungi to virtually decay any organic matter on the rain-forest [[Forest floor|floor]] overnight and much of the nutrients are volatilized or leached from the soil and lost,<ref>{{cite journal |last1=Wieder |first1=William R. |last2=Cleveland |first2=Cory C. |last3=Townsend |first3=Alan R. |name-list-style=amp |year=2009 |title=Controls over leaf litter decomposition in wet tropical forests |journal=[[Ecology (journal)|Ecology]] |volume=90 |issue=12 |pages=3333–41 |url=https://scholarworks.umt.edu/cgi/viewcontent.cgi?article=1009&context=decs_pubs |doi=10.1890/08-2294.1 |pmid=20120803 |accessdate=31 March 2019 |format=[[Portable Document Format|PDF]]}}</ref> leaving only a thin root mat lying directly on the mineral soil.<ref>{{cite journal |last1=Stark |first1=Nellie M. |last2=Lordan |first2=Carl F. |name-list-style=amp |year=1978 |title=Nutrient retention by the root mat of an Amazonian rain forest |journal=[[Ecology (journal)|Ecology]] |volume=59 |issue=3 |pages=434–37 |url=http://w3.marietta.edu/~biol/102online/tropicalrainforest.pdf |doi=10.2307/1936571 |accessdate=31 March 2019 |jstor=1936571 |archive-url=https://web.archive.org/web/20190331102112/http://w3.marietta.edu/~biol/102online/tropicalrainforest.pdf |archive-date=31 March 2019 |url-status=dead }}</ref> However, carbon in the form of finely divided [[charcoal]], also known as [[black carbon]], is far more stable than soil colloids and is capable of performing many of the functions of the soil colloids of sub-tropical soils.<ref>{{cite journal |last1=Liang |first1=Biqing |last2=Lehmann |first2=Johannes |last3=Solomon |first3=Dawit |last4=Kinyangi |first4=James |last5=Grossman |first5=Julie |last6=O'Neill |first6=Brendan |last7=Skjemstad |first7=Jan O. |last8=Thies |first8=Janice |last9=Luizaõ |first9=Flávio J. |last10=Petersen |first10=Julie |last11=Neves |first11=Eduardo G. |name-list-style=amp |year=2006 |title=Black carbon increases cation exchange capacity in soils |journal=[[Soil Science Society of America Journal]] |volume=70 |issue=5 |pages=1719–30 |url=http://xrm.phys.northwestern.edu/research/pdf_papers/2006/liang_sssaj_2006.pdf |doi=10.2136/sssaj2005.0383 |accessdate=30 March 2019 |bibcode=2006SSASJ..70.1719L }}</ref> Soil containing substantial quantities of charcoal, of an anthropogenic origin, is called [[terra preta]]. In [[Amazonia]] it testifies for the agronomic knowledge of past [[Amerindian]] civilizations.<ref>{{cite book |last1=Neves |first1=Eduardo G. |last2=Petersen |first2=James B. |last3=Bartone |first3=Robert N. |last4=da Silva |first4=Carlos Augusto |date=2003 |chapter=Historical and socio-cultural origins of Amazonian Dark Earth |title=Amazonian Dark Earths: origin, properties, management |editor-last1=Lehmann |editor-first1=Johannes |editor-last2=Kern |editor-first2=Dirse C. |editor-last3=Glaser |editor-first3=Bruno |editor-last4=Woods |editor-first4=William I. |publisher=[[Springer Science & Business Media]] |location=Berlin, Germany |pages=29–50 |chapter-url=https://www.researchgate.net/publication/226546157 |accessdate=7 April 2019 |chapter-format=[[Portable Document Format|PDF]]}}</ref> The [[pantropical]] peregrine earthworm ''Pontoscolex corethrurus'' has been suspected to contribute to the fine division of charcoal and its mixing to the mineral soil in the frame of present-day [[slash-and-burn]] or [[shifting cultivation]] still practiced by Amerindian tribes.<ref>{{cite journal |last1=Ponge |first1=Jean-François |last2=Topoliantz |first2=Stéphanie |last3=Ballof |first3=Sylvain |last4=Rossi |first4=Jean-Pierre |last5=Lavelle |first5=Patrick |last6=Betsch |first6=Jean-Marie |last7=Gaucher |first7=Philippe |name-list-style=amp |year=2006 |title=Ingestion of charcoal by the Amazonian earthworm Pontoscolex corethrurus: a potential for tropical soil fertility |journal=Soil Biology and Biochemistry |volume=38 |issue=7 |pages=2008–09 |url=https://www.researchgate.net/publication/44735820 |doi=10.1016/j.soilbio.2005.12.024 |accessdate=7 April 2019 |format=[[Portable Document Format|PDF]]}}</ref> Research into terra preta is still young but is promising. [[Fallow]] periods "on the Amazonian Dark Earths can be as short as 6 months, whereas fallow periods on [[oxisol]]s are usually 8 to 10 years long"<ref>{{cite web|last=Lehmann |first=Johannes|title=Terra Preta de Indio |url=http://www.css.cornell.edu/faculty/lehmann/research/terra%20preta/terrapretamain.html |publisher=University of Cornell, Department of Crop and Soil Sciences |accessdate=7 April 2019 |url-status=live |archiveurl=https://web.archive.org/web/20130424061552/http://www.css.cornell.edu/faculty/lehmann/research/terra%20preta/terrapretamain.html |archivedate=24 April 2013 }}</ref> The incorporation of charcoal to agricultural soil for improving water and nutrient retention has been called [[biochar]], being extended to other charred or carbon-rich by-products, and is now increasingly used in [[Sustainable agriculture|sustainable]] [[tropical agriculture]].<ref>{{cite book |last1=Lehmann |first1=Johannes |last2=Rondon |first2=Marco |date=2006 |chapter=Bio-char soil management on highly weathered soils in the humid tropics |title=Biological approaches to sustainable soil systems |editor-last1=Uphoff |editor-first1=Norman |editor-last2=Ball |editor-first2=Andrew S. |editor-last3=Fernandes |editor-first3=Erick |editor-last4=Herren |editor-first4=Hans |editor-last5=Husson |editor-first5=Olivier |editor-last6=Laing |editor-first6=Mark |editor-last7=Palm |editor-first7=Cheryl |editor-last8=Pretty |editor-first8=Jules |editor-last9=Sánchez |editor-first9=Pedro |editor-last10=Sanginga |editor-first10=Nteranya |editor-last11=Thies |editor-first11=Janice |publisher=[[CRC Press]] |location=Boca Raton, Florid |pages=517–30 |chapter-url=https://www.researchgate.net/publication/201998979 |accessdate=14 April 2019 |chapter-format=[[Portable Document Format|PDF]]}}</ref> Biochar also allows the irreversible sorption of pesticides and other pollutants, a mechanism by which their mobility, and thus their environmental risk, decreases.<ref>{{cite journal |last1=Yu |first1=Xiangyang |last2=Pan |first2=Ligang |last3=Ying |first3=Guangguo |last4=Kookana |first4=Rai S. |name-list-style=amp |year=2010 |title=Enhanced and irreversible sorption of pesticide pyrimethanil by soil amended with biochars |journal=Journal of Environmental Sciences |volume=22 |issue=4 |pages=615–20 |url=http://www.jesc.ac.cn/jesc_En/ch/reader/create_pdf.aspx?file_no=2010220420&year_id=2010&quarter_id=4&falg=1 |archive-url=https://web.archive.org/web/20200722185918/http://www.jesc.ac.cn/jesc_En/ch/reader/create_pdf.aspx?file_no=2010220420&year_id=2010&quarter_id=4&falg=1 |url-status=dead |archive-date=22 July 2020 |doi=10.1016/S1001-0742(09)60153-4 |pmid=20617740 |accessdate=14 April 2019 |format=[[Portable Document Format|PDF]] }}</ref> It has also been argued as a mean of [[Carbon sequestration|sequestering]] more carbon in the soil, thereby mitigating the so-called [[greenhouse effect]].<ref>{{cite journal |last1=Whitman |first1=Thea |last2=Lehmann |first2=Johannes |name-list-style=amp |year=2009 |title=Biochar: one way forward for soil carbon in offset mechanisms in Africa? |journal=Environmental Science and Policy |volume=12 |issue=7 |pages=1024–27 |url=http://pdfs.semanticscholar.org/c196/57fc5fd4d88c9f5acf51fdb3e31dc6f8ae04.pdf |archive-url=https://web.archive.org/web/20190304184712/http://pdfs.semanticscholar.org/c196/57fc5fd4d88c9f5acf51fdb3e31dc6f8ae04.pdf |url-status=dead |archive-date=4 March 2019 |doi=10.1016/j.envsci.2009.07.013 |accessdate=14 April 2019 }}</ref> However, the use of biochar is limited by the availability of wood or other products of [[pyrolysis]] and by risks caused by concomitent [[deforestation]].<ref>{{cite journal |last=Mwampamba |first=Tuyeni Heita |year=2007 |title=Has the woodfuel crisis returned? Urban charcoal consumption in Tanzania and its implications to present and future forest availability |journal=Energy Policy |volume=35 |issue=8 |pages=4221–34 |url=https://www.academia.edu/3076522 |doi= 10.1016/j.enpol.2007.02.010|accessdate=14 April 2019 |format=[[Portable Document Format|PDF]]}}</ref>


==See also==
==See also==
Line 56: Line 56:
* {{cite book |title=Soils: An Introduction to Soils and Plant Growth |last1=Donahue |first1=Roy Luther |last2=Miller |first2=Raymond W. |last3=Shickluna |first3=John C. |year=1977 |publisher=Prentice-Hall |isbn=978-0-13-821918-5 |url=https://archive.org/details/soilsintroductio00dona }}
* {{cite book |title=Soils: An Introduction to Soils and Plant Growth |last1=Donahue |first1=Roy Luther |last2=Miller |first2=Raymond W. |last3=Shickluna |first3=John C. |year=1977 |publisher=Prentice-Hall |isbn=978-0-13-821918-5 |url=https://archive.org/details/soilsintroductio00dona }}
* {{cite web|title=Arizona Master Gardener|url=http://ag.arizona.edu/pubs/garden/mg/soils/soils.html|publisher=Cooperative Extension, College of Agriculture, University of Arizona|accessdate=27 May 2013}}
* {{cite web|title=Arizona Master Gardener|url=http://ag.arizona.edu/pubs/garden/mg/soils/soils.html|publisher=Cooperative Extension, College of Agriculture, University of Arizona|accessdate=27 May 2013}}
* {{cite book |title=Soil: The Yearbook of Agriculture 1957 |editor-last=Stefferud |editor-first=Alfred |year=1957 |publisher=United States Department of Agriculture |url=//archive.org/stream/yoa1957#page/n18/mode/1up |oclc=704186906 }}
* {{cite book |title=Soil: The Yearbook of Agriculture 1957 |editor-last=Stefferud |editor-first=Alfred |year=1957 |publisher=United States Department of Agriculture |url=http://archive.org/stream/yoa1957#page/n18/mode/1up |oclc=704186906 }}
** {{harvc |name-list-style=harv |last=Kellogg |first=Charles E. |chapter=We Seek; We Learn |in=Stefferud |year=1957 |url=//archive.org/stream/yoa1957#page/n17/mode/1up }}
** {{harvc |name-list-style=harv |last=Kellogg |first=Charles E. |chapter=We Seek; We Learn |in=Stefferud |year=1957 |url=//archive.org/stream/yoa1957#page/n17/mode/1up }}
** {{harvc |name-list-style=harv |last=Simonson |first=Roy W. |chapter=What Soils Are |in=Stefferud |year=1957 |url=//archive.org/stream/yoa1957#page/n34/mode/1up }}
** {{harvc |name-list-style=harv |last=Simonson |first=Roy W. |chapter=What Soils Are |in=Stefferud |year=1957 |url=//archive.org/stream/yoa1957#page/n34/mode/1up }}

Revision as of 15:40, 30 April 2021

The soil matrix is the solid phase of soils, and comprise the solid particles that make up soils. Soil particles can be classified by their chemical composition (mineralogy) as well as their size. The particle size distribution of a soil, its texture, determines many of the properties of that soil, in particular hydraulic conductivity and water potential,[1] but the mineralogy of those particles can strongly modify those properties. The mineralogy of the finest soil particles, clay, is especially important.[2]

Gravel, sand and silt

Gravel, sand and silt are the larger soil particles, and their mineralogy is often inherited from the parent material of the soil, but may include products of weathering (such as concretions of calcium carbonate or iron oxide), or residues of plant and animal life (such as silica phytoliths).[3][4] Quartz is the most common mineral in the sand or silt fraction as it is resistant to chemical weathering, except under hot climate;[5] other common minerals are feldspars, micas and ferromagnesian minerals such as pyroxenes, amphiboles and olivines, which are dissolved or transformed in clay under the combined influence of physico-chemical and biological processes.[3][6]

Mineral colloids; soil clays

Due to its high specific surface area and its unbalanced negative electric charges, clay is the most active mineral component of soil.[7][8] It is a colloidal and most often a crystalline material.[9] In soils, clay is a soil textural class and is defined in a physical sense as any mineral particle less than 2 μm (8×10−5 in) in effective diameter. Many soil minerals, such as gypsum, carbonates, or quartz, are small enough to be classified as clay based on their physical size, but chemically they do not afford the same utility as do mineralogically-defined clay minerals.[10] Chemically, clay minerals are a range of phyllosilicate minerals with certain reactive properties.[11]

Before the advent of X-ray diffraction clay was thought to be very small particles of quartz, feldspar, mica, hornblende or augite, but it is now known to be (with the exception of mica-based clays) a precipitate with a mineralogical composition that is dependent on but different from its parent materials and is classed as a secondary mineral.[12] The type of clay that is formed is a function of the parent material and the composition of the minerals in solution.[13] Clay minerals continue to be formed as long as the soil exists.[14] Mica-based clays result from a modification of the primary mica mineral in such a way that it behaves and is classed as a clay.[15] Most clays are crystalline, but some clays or some parts of clay minerals are amorphous.[16] The clays of a soil are a mixture of the various types of clay, but one type predominates.[17]

Typically there are four main groups of clay minerals: kaolinite, montmorillonite-smectite, illite, and chlorite.[18] Most clays are crystalline and most are made up of three or four planes of oxygen held together by planes of aluminium and silicon by way of ionic bonds that together form a single layer of clay. The spatial arrangement of the oxygen atoms determines clay's structure.[19] Half of the weight of clay is oxygen, but on a volume basis oxygen is ninety percent.[20] The layers of clay are sometimes held together through hydrogen bonds, sodium or potassium bridges and as a result will swell less in the presence of water.[21] Clays such as montmorillonite have layers that are loosely attached and will swell greatly when water intervenes between the layers.[22]

In a wider sense clays can be classified as:

  1. Layer Crystalline alumino-silica clays: montmorillonite, illite, vermiculite, chlorite, kaolinite.
  2. Crystalline Chain carbonate and sulfate minerals: calcite (CaCO3), dolomite (CaMg(CO3)2) and gypsum (CaSO4·2H2O).
  3. Amorphous clays: young mixtures of silica (SiO2-OH) and alumina (Al(OH)3) which have not had time to form regular crystals.
  4. Sesquioxide clays: old, highly leached clays which result in oxides of iron, aluminium and titanium.[23]

Alumino-silica clays

Alumino-silica clays or aluminosilicate clays are characterized by their regular crystalline or quasi-crystalline structure.[24] Oxygen in ionic bonds with silicon forms a tetrahedral coordination (silicon at the center) which in turn forms sheets of silica. Two sheets of silica are bonded together by a plane of aluminium which forms an octahedral coordination, called alumina, with the oxygens of the silica sheet above and that below it.[25] Hydroxyl ions (OH) sometimes substitute for oxygen. During the clay formation process, Al3+ may substitute for Si4+ in the silica layer, and as much as one fourth of the aluminium Al3+ may be substituted by Zn2+, Mg2+ or Fe2+ in the alumina layer. The substitution of lower-valence cations for higher-valence cations (isomorphous substitution) gives clay a local negative charge on an oxygen atom[25] that attracts and holds water and positively charged soil cations, some of which are of value for plant growth.[26] Isomorphous substitution occurs during the clay's formation and does not change with time.[27][28]

  • Montmorillonite clay is made of four planes of oxygen with two silicon and one central aluminium plane intervening. The alumino-silicate montmorillonite clay is thus said to have a 2:1 ratio of silicon to aluminium, in short it is called a 2:1 clay mineral.[29] The seven planes together form a single crystal of montmorillonite. The crystals are weakly held together and water may intervene, causing the clay to swell up to ten times its dry volume.[30] It occurs in soils which have had little leaching, hence it is found in arid regions, although it may also occur in humid climates, depending on its mineralogical origin.[31] As the crystals are not bonded face to face, the entire surface is exposed and available for surface reactions, hence it has a high cation exchange capacity (CEC).[32][33][34]
  • Illite is a 2:1 clay similar in structure to montmorillonite but has potassium bridges between the faces of the clay crystals and the degree of swelling depends on the degree of weathering of potassium-feldspar.[35] The active surface area is reduced due to the potassium bonds. Illite originates from the modification of mica, a primary mineral. It is often found together with montmorillonite and its primary minerals. It has moderate CEC.[36][33][37][38][39]
  • Vermiculite is a mica-based clay similar to illite, but the crystals of clay are held together more loosely by hydrated magnesium and it will swell, but not as much as does montmorillonite.[40] It has very high CEC.[41][42][38][39]
  • Chlorite is similar to vermiculite, but the loose bonding by occasional hydrated magnesium, as in vermiculite, is replaced by a hydrated magnesium sheet, that firmly bonds the planes above and below it. It has two planes of silicon, one of aluminium and one of magnesium; hence it is a 2:2 clay.[43] Chlorite does not swell and it has low CEC.[41][44]
  • Kaolinite is very common, highly weathered clay, and more common than montmorillonite in acid soils.[45] It has one silica and one alumina plane per crystal; hence it is a 1:1 type clay. One plane of silica of montmorillonite is dissolved and is replaced with hydroxyls, which produces strong hydrogen bonds to the oxygen in the next crystal of clay.[46] As a result, kaolinite does not swell in water and has a low specific surface area, and as almost no isomorphous substitution has occurred it has a low CEC.[47] Where rainfall is high, acid soils selectively leach more silica than alumina from the original clays, leaving kaolinite.[48] Even heavier weathering results in sesquioxide clays.[49][20][34][37][50][51]

Crystalline chain clays

The carbonate and sulfate clay minerals are much more soluble and hence are found primarily in desert soils where leaching is less active.[52]

Amorphous clays

Amorphous clays are young, and commonly found in recent volcanic ash deposits such as tephra.[53] They are mixtures of alumina and silica which have not formed the ordered crystal shape of alumino-silica clays which time would provide. The majority of their negative charges originates from hydroxyl ions, which can gain or lose a hydrogen ion (H+) in response to soil pH, in such way was as to buffer the soil pH. They may have either a negative charge provided by the attached hydroxyl ion (OH), which can attract a cation, or lose the hydrogen of the hydroxyl to solution and display a positive charge which can attract anions. As a result, they may display either high CEC in an acid soil solution, or high anion exchange capacity in a basic soil solution.[49]

Sesquioxide clays

silica-sesquioxide

Sesquioxide clays are a product of heavy rainfall that has leached most of the silica from alumino-silica clay, leaving the less soluble oxides iron hematite (Fe2O3), iron hydroxide (Fe(OH)3), aluminium hydroxide gibbsite (Al(OH)3), hydrated manganese birnessite (MnO2), as can be observed in most lateritic weathering profiles of tropical soils.[54] It takes hundreds of thousands of years of leaching to create sesquioxide clays.[55] Sesqui is Latin for "one and one-half": there are three parts oxygen to two parts iron or aluminium; hence the ratio is one and one-half (not true for all). They are hydrated and act as either amorphous or crystalline. They are not sticky and do not swell, and soils high in them behave much like sand and can rapidly pass water. They are able to hold large quantities of phosphates, a sorptive process which can at least partly be inhibited in the presence of decomposed (humified) organic matter.[56] Sesquioxides have low CEC but these variable-charge minerals are able to hold anions as well as cations.[57] Such soils range from yellow to red in colour. Such clays tend to hold phosphorus so tightly that it is unavailable for absorption by plants.[58][59][60]

Organic colloids

Humus is one of the two final stages of decomposition of organic matter. It remains in the soil as the organic component of the soil matrix while the other stage, carbon dioxide, is freely liberated in the atmosphere or reacts with calcium to form the soluble calcium bicarbonate. While humus may linger for a thousand years,[61] on the larger scale of the age of the mineral soil components, it is temporary, being finally released as CO2. It is composed of the very stable lignins (30%) and complex sugars (polyuronides, 30%), proteins (30%), waxes, and fats that are resistant to breakdown by microbes and can form complexes with metals, facilitating their downward migration (podzolization).[62] However, although originating for its main part from dead plant organs (wood, bark, foliage, roots), a large part of humus comes from organic compounds excreted by soil organisms (roots, microbes, animals) and from their decomposition upon death.[63] Its chemical assay is 60% carbon, 5% nitrogen, some oxygen and the remainder hydrogen, sulfur, and phosphorus. On a dry weight basis, the CEC of humus is many times greater than that of clay.[64][65][66]

Humus plays a major role in the regulation of atmospheric carbon, through carbon sequestration in the soil profile, more especially in deeper horizons with reduced biological activity.[67] Stocking and destocking of soil carbon are under strong climate influence.[68] They are normally balanced through an equilibrium between production and mineralization of organic matter, but the balance is in favour of destocking under present-day climate warming,[69] and more especially in permafrost.[70]

Carbon and terra preta

In the extreme environment of high temperatures and the leaching caused by the heavy rain of tropical rain forests, the clay and organic colloids are largely destroyed. The heavy rains wash the alumino-silicate clays from the soil leaving only sesquioxide clays of low CEC. The high temperatures and humidity allow bacteria and fungi to virtually decay any organic matter on the rain-forest floor overnight and much of the nutrients are volatilized or leached from the soil and lost,[71] leaving only a thin root mat lying directly on the mineral soil.[72] However, carbon in the form of finely divided charcoal, also known as black carbon, is far more stable than soil colloids and is capable of performing many of the functions of the soil colloids of sub-tropical soils.[73] Soil containing substantial quantities of charcoal, of an anthropogenic origin, is called terra preta. In Amazonia it testifies for the agronomic knowledge of past Amerindian civilizations.[74] The pantropical peregrine earthworm Pontoscolex corethrurus has been suspected to contribute to the fine division of charcoal and its mixing to the mineral soil in the frame of present-day slash-and-burn or shifting cultivation still practiced by Amerindian tribes.[75] Research into terra preta is still young but is promising. Fallow periods "on the Amazonian Dark Earths can be as short as 6 months, whereas fallow periods on oxisols are usually 8 to 10 years long"[76] The incorporation of charcoal to agricultural soil for improving water and nutrient retention has been called biochar, being extended to other charred or carbon-rich by-products, and is now increasingly used in sustainable tropical agriculture.[77] Biochar also allows the irreversible sorption of pesticides and other pollutants, a mechanism by which their mobility, and thus their environmental risk, decreases.[78] It has also been argued as a mean of sequestering more carbon in the soil, thereby mitigating the so-called greenhouse effect.[79] However, the use of biochar is limited by the availability of wood or other products of pyrolysis and by risks caused by concomitent deforestation.[80]

See also

References

  1. ^ Saxton, Keith E. & Rawls, Walter J. (2006). "Soil water characteristic estimates by texture and organic matter for hydrologic solutions" (PDF). Soil Science Society of America Journal. 70 (5): 1569–78. Bibcode:2006SSASJ..70.1569S. CiteSeerX 10.1.1.452.9733. doi:10.2136/sssaj2005.0117. Archived from the original (PDF) on 2 September 2018. Retrieved 2 September 2018.
  2. ^ College of Tropical Agriculture and Human Resources. "Soil Mineralogy". cms.ctahr.hawaii.edu/. University of Hawai‘i at Mānoa. Retrieved 2 September 2018.
  3. ^ a b Russell, E. Walter (1973). Soil conditions and plant growth (10th ed.). London: Longman. pp. 67–70. ISBN 978-0-582-44048-7.
  4. ^ Mercader, Julio; Bennett, Tim; Esselmont, Chris; Simpson, Steven & Walde, Dale (2011). "Soil phytoliths from miombo woodlands in Mozambique" (PDF). Quaternary Research. 75 (1): 138–50. Bibcode:2011QuRes..75..138M. doi:10.1016/j.yqres.2010.09.008. Retrieved 9 September 2018.
  5. ^ Sleep, Norman H. & Hessler, Angela M. (2006). "Weathering of quartz as an Archean climatic indicator" (PDF). Earth and Planetary Science Letters. 241 (3–4): 594–602. Bibcode:2006E&PSL.241..594S. doi:10.1016/j.epsl.2005.11.020. Retrieved 9 September 2018.
  6. ^ Banfield, Jillian F.; Barker, William W.; Welch, Susan A. & Taunton, Anne (1999). "Biological impact on mineral dissolution: application of the lichen model to understanding mineral weathering in the rhizosphere" (PDF). Proceedings of the National Academy of Sciences of the United States of America. 96 (7): 3404–11. Bibcode:1999PNAS...96.3404B. doi:10.1073/pnas.96.7.3404. PMC 34281. PMID 10097050. Retrieved 9 September 2018.
  7. ^ Santamarina, J. Carlos; Klein, Katherine A.; Wang, Yu-Hsing & Prencke, E. (2002). "Specific surface: determination and relevance" (PDF). Canadian Geotechnical Journal. 39 (1): 233–41. doi:10.1139/t01-077. Archived from the original (PDF) on 30 September 2018. Retrieved 30 September 2018.
  8. ^ Tombácz, Etelka & Szekeres, Márta (2006). "Surface charge heterogeneity of kaolinite in aqueous suspension in comparison with montmorillonite" (PDF). Applied Clay Science. 34 (1–4): 105–24. doi:10.1016/j.clay.2006.05.009. Retrieved 30 September 2018.
  9. ^ Brown, George (1984). "Crystal structures of clay minerals and related phyllosilicates" (PDF). Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences. 311 (1517): 221–40. Bibcode:1984RSPTA.311..221B. doi:10.1098/rsta.1984.0025. Retrieved 30 September 2018.
  10. ^ Hillier, Stephen (1978). "Clay mineralogy" (PDF). In Middleton, Gerard V.; Church, Michael J.; Coniglio, Mario; Hardie, Lawrence A.; Longstaffe, Frederick J. (eds.). Encyclopedia of sediments and Sedimentary rocks. Encyclopedia of Earth Science. Dordrecht, The Netherlands: Springer Science+Business Media B.V. pp. 139–42. doi:10.1007/3-540-31079-7_47. ISBN 978-0-87933-152-8. Retrieved 30 September 2018.
  11. ^ Donahue, Miller & Shickluna 1977, pp. 101–02.
  12. ^ Bergaya, Faïza; Beneke, Klaus; Lagaly, Gerhard. "History and perspectives of clay science" (PDF). University of Kiel. Retrieved 20 October 2018.
  13. ^ Wilson, M. Jeff (1999). "The origin and formation of clay minerals in soils: past, present and future perspectives" (PDF). Clay Minerals. 34 (1): 7–25. Bibcode:1999ClMin..34....7W. doi:10.1180/000985599545957. Archived from the original (PDF) on 29 March 2018. Retrieved 20 October 2018.
  14. ^ Simonson 1957, p. 19.
  15. ^ Churchman, G. Jock (1980). "Clay minerals formed from micas and chlorites in some New Zealand soils" (PDF). Clay Minerals. 15 (1): 59–76. Bibcode:1980ClMin..15...59C. doi:10.1180/claymin.1980.015.1.05. Retrieved 20 October 2018.
  16. ^ Wada, Koji; Greenland, Dennis J. (1970). "Selective dissolution and differential infrared spectroscopy for characterization of 'amorphous' constituents in soil clays". Clay Minerals. 8 (3): 241–54. Bibcode:1970ClMin...8..241W. CiteSeerX 10.1.1.624.1439. doi:10.1180/claymin.1970.008.3.02.
  17. ^ Donahue, Miller & Shickluna 1977, p. 102.
  18. ^ "The clay mineral group" (PDF). Amethyst Galleries, Inc. Retrieved 28 October 2018.
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