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 crystallinephyllosilicate material.[9] In soils, clay is a soil textural class and is defined in a physical sense as any mineral particle less than 2μm (8×10−5in) in effective diameter. Many soil minerals, such as gypsum, calcite, feldspar or quartz particles, 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]
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.[11] The type of clay that is formed is a function of the parent material and the composition of the minerals in solution.[12] Clay minerals continue to be formed as long as the soil exists, whether by inheritance, neoformation, or transformation of pre-existing minerals.[13] 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.[14] Most clays are crystalline, but some clays or some parts of clay minerals are amorphous.[15] The clays of a soil are a mixture of the various types of clay, but one type often predominates according to soil type.[16]
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.[30] The active surface area is reduced due to the potassium ionic 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.[31]
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.[32] It has very high CEC.[33]
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.[34] Chlorite does not swell and it has low CEC.[35]
Kaolinite is a very common, highly weathered clay, and more common than montmorillonite in acid soils.[36] 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.[37] 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.[38] Where rainfall is high, acid soils selectively leach more silica than alumina from the original clays, leaving kaolinite.[39] Even heavier weathering results in sesquioxide clays.[40]
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.[41]
Amorphous clays
Amorphous clays are young, and commonly found in recent volcanic ash deposits such as tephra.[42] They are mixtures of alumina and silica which have not formed the ordered crystal shape of alumino-silica clays which time would provide.[43] 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 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.[43]
Sesquioxide clays
silica-sesquioxide
Sesquioxide clays or sesquioxides 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 hydroxidegibbsite (Al(OH)3), hydrated manganese birnessite (MnO2), as can be observed in most lateriticweathering profiles of tropical soils.[44] It takes hundreds of thousands of years of leaching to create sesquioxide clays.[45]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 (e.g. lateritic soils) behave much like sand and can rapidly pass water.[46] 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.[47] Sesquioxides have low CEC but these variable-charge minerals are able to hold anions as well as cations.[48] Such soils range from yellow to red in colour according to the dominance of various iron oxides.[49] Such clays tend to hold phosphorus so tightly that it is unavailable for absorption by plants, in proportion to their content in goethite.[50]
↑ Hillier, Stephen (1978). "粘土鉱物学" . Middleton, Gerard V.; Church, Michael J.; Coniglio, Mario; Hardie, Lawrence A.; Longstaffe, Frederick J. (編).堆積物と堆積岩の百科事典. 地球科学百科事典. ドルドレヒト、オランダ: Springer Science+Business Media BV pp. 223–8 . doi : 10.1007/3-540-31079-7_47 . ISBN978-0-87933-152-8ISSN 1871-756X。2026年5月18日取得。
↑ Wilson, M. Jeff (1999年3月) 「土壌中の粘土鉱物の起源と形成:過去、現在、未来の展望」 . Clay Minerals . 34 (1): 7–25 . Bibcode : 1999ClMin..34....7W . doi : 10.1180/000985599545957 . S2CID 140587736. 2018年3月29日のオリジナルからアーカイブ(PDF) 。 2026年5月18日取得。
↑ Eberl, Dennis D. (1984年6月14日). 「岩石および土壌における粘土鉱物の形成と変質」 . Philosophical Transactions A. 311 ( 1517): 241–57 . doi : 10.1098/rsta.1984.0026 . 2026年5月18日取得。
↑ Donahue, Roy L.; Miller, Raymond W.; Shickluna, John C. (1977). "化学的性質とコロイド特性" . Donahue, Roy L.; Miller, Raymond W.; Shickluna, John C. (編)『土壌:土壌と植物の生育入門』(第4版). ニュージャージー州エングルウッド・クリフス:プレンティス・ホール. pp. 101–22 . ISBN978-01382191852026年5月18日に取得。
↑ Aylmore, LA Graham; Quirk, James P. (1971年7月~8月) 「粘土系におけるドメインと準結晶領域」 . Soil Science Society of America Journal . 35 (4): 652–4 . Bibcode : 1971SSASJ..35..652Q . doi : 10.2136/sssaj1971.03615995003500040046x . 2026年5月19日取得。
↑ Schoonheydt, Robert A. ; Johnston, Cliff T. (2011). "粘土鉱物の表面特性" . Brigatti, Maria Franca; Mottana, Annibale (eds.). Layered mineral structures and their application in advanced technologies . Twickenham, United Kingdom: Mineralogical Society of Great Britain & Ireland . pp. 337– 73. doi : 10.1180/EMU-notes.11.10 . 2026年5月19日取得.
↑ Johns, William D.; Jonas, Edward C. (1954 年 3 月). 「粘土の同形性と性質の関係に関するいくつかの考察」 . The Journal of Geology . 62 (2): 163–71 . doi : 10.1086/626143 . 2026 年5 月 19 日取得。
↑ Lagaly, Gerhard (1979). "規則的な層間2:1粘土鉱物の「層電荷」" . Clays and Clay Minerals . 27 (1): 1– 10. Bibcode : 1979CCM....27....1L . doi : 10.1346/CCMN.1979.0270101 . S2CID 46978307. 2026年5月19日取得。
↑ Sperry, James M.; Peirce, J. Jeffrey (1999年5月1日). "モンモリロナイト粘土のイオン交換と表面電荷" . Water Environment Research . 71 (3): 316– 22. doi : 10.2175/106143098X121798 . 2026年5月19日取得.
↑Ng, Charles Wang Wai; Owusu, Seth Tawiah; Zhou, Chao; Chiu, Abraham Chung Fai (5 March 2020). "Effects of sesquioxide content on stress-dependent water retention behaviour of weathered soils". Engineering Geology. 266 105455. doi:10.1016/j.enggeo.2019.105455. hdl:10397/89505. Retrieved 20 May 2026.
↑Hunt, James F.; Ohno, Tsutomu; He, Zhongqi; Honeycutt, C. Wayne; Dail, D. Bryan (15 May 2007). "Inhibition of phosphorus sorption to goethite, gibbsite, and kaolin by fresh and decomposed organic matter". Biology and Fertility of Soils. 44 (2): 277–88. Bibcode:2007BioFS..44..277H. doi:10.1007/s00374-007-0202-1. S2CID29681161. Archived from the original on July 9, 2020. Retrieved 20 May 2026.
↑Shamshuddin, Jusop; Anda, Markus (November 2008). "Charge properties of soils in Malaysia dominated by kaolinite, gibbsite, goethite and hematite". Bulletin of the Geological Society of Malaysia. 54: 27–31. doi:10.7186/bgsm54200805.
↑Duchaufour, Philippe (1982). "Sesquioxide-rich soils". In Duchaufour, Philippe (ed.). Pedology, translated by T.R. Paton. Dordrecht, The Netherlands: Springer. pp.373–425. doi:10.1007/978-94-011-6003-2_13. ISBN978-94-011-6003-2. Retrieved 20 May 2026.
↑Bortoluzzi, Edson C.; Pérez, Carlos A. S.; Ardisson, José D.; Tiecher, Tales; Caner, Laurent (February 2015). "Occurrence of iron and aluminum sesquioxides and their implications for the P sorption in subtropical soils". Applied Clay Science. 104: 196–204. doi:10.1016/j.clay.2014.11.032. Retrieved 20 May 2026.
↑ Manning, David AC (2018年7月5日). "土壌炭酸塩沈殿の生物学的促進:大気中のCO2の受動的除去" . Mineralogical Magazine . 72 (2): 639–49 . doi : 10.1180/minmag.2008.072.2.639 . 2026年5月20日取得。
↑ Paul, Eldor A.; Campbell, Colin A.; Rennie, David A.; McCallum, Kenneth J. (1964). "炭素年代測定法を用いた土壌腐植の動態に関する研究" (PDF) . Transactions of the 8th International Congress of Soil Science, Bucharest, Romania, 1964 . Bucharest, Romania: Publishing House of the Academy of the Socialist Republic of Romania. pp. 201–08 . 2026年5月20日取得.
↑ Lehmann, Johannes; Kleber, Markus (2015年11月23日) 「土壌有機物の論争的な性質」 Nature . 528 ( 7580): 60–8 . doi : 10.1038/nature16069 . 2026年5月20日取得。
↑ Bin, Gao; Cao, Xinde; Dong, Yan; Luo, Yongming; Ma, Lena Q. (2011年2月2日). 「土壌中のコロイド沈着と放出、および重金属との関連性」 . Critical Reviews in Environmental Science and Technology . 41 (4): 336–72 . Bibcode : 2011CREST..41..336B . doi : 10.1080/10643380902871464 . S2CID 32879709. 2026年5月21日取得.
↑ Six, Johan; Frey, Serita D. ; Thiet, Rachel K.; Batten, Katherine M. (2006 年 3 月). "農業生態系における炭素隔離への細菌および真菌の寄与" . Soil Science Society of America Journal . 70 (2): 555– 69. Bibcode : 2006SSASJ..70..555S . doi : 10.2136/sssaj2004.0347 . S2CID 39575537 . 2020 年 7 月 22 日のオリジナルからアーカイブ(PDF) . 2026 年5 月 21 日取得.
↑ Parfitt, Roger L.; Giltrap, Donna J.; Whitton, JS (1995). "土壌の陽イオン交換容量に対する有機物と粘土鉱物の寄与" . Communications in Soil Science and Plant Analysis . 26 ( 9– 10): 1343– 55. doi : 10.1080/00103629509369376 . 2026年5月21日取得.
↑ Thornton, Peter E.; Doney, Scott C.; Lindsay, Konkel; Moore, J. Keith; Mahowald, Natalie; Randerson, James T.; Fung, Inez; Lamarque, Jean-François; Feddema, Johannes J.; Lee, Y. Hanna (2009年10月8日). "炭素-窒素相互作用が気候-炭素循環フィードバックを調節する:大気-海洋大循環モデルの結果" . Biogeosciences . 6 (10): 2099– 120. Bibcode : 2009BGeo....6.2099T . doi : 10.5194/bg-6-2099-2009 . hdl : 1808/9294 .
↑ Morgan, Jack A.; Follett, Ronald F.; Allen Jr, Leon Hartwell; Del Grosso, Stephen; Derner, Justin D.; Dijkstra, Feike; Franzluebbers, Alan; Fry, Robert; Paustian, Keith; Schoeneberger, Michele M. (2010年1月1日). 「米国の農地における炭素隔離」 . Journal of Soil and Water Conservation . 65 (1): 6A– 13A. doi : 10.2489/jswc.65.1.6A . 2026年5月21日取得。
↑ Parton, Willam J.; Scurlock, Jonathan MO; Ojima, Dennis S.; Schimel, David; Hall, David O.; The SCOPEGRAM Group (1995年2月)。「気候変動が世界の草原生産と土壌炭素に与える影響」。Global Change Biology。1 ( 1 ): 13– 22。Bibcode : 1995GCBio...1...13P。doi : 10.1111 /j.1365-2486.1995.tb00002.x。2026年5月21日取得。
↑ Schuur, Edward AG; Vogel, Jason G.; Crummer, Kathryn G.; Lee, Hanna; Sickman, James O.; Osterkamp, Tom E. (2009年5月28日). "永久凍土の融解がツンドラからの古い炭素放出と正味炭素交換に及ぼす影響" . Nature . 459 ( 7246): 556–9 . Bibcode : 2009Natur.459..556S . doi : 10.1038/nature08031 . PMID 19478781. S2CID 4396638. 2026年5月21日取得。
↑ Nortcliff, Stephen (2010). "熱帯の土壌" . Dion, Patrice (編) 『熱帯の土壌生物学と農業』 . 土壌生物学. ベルリン、ドイツ: Springer. pp. 1–15 . doi : 10.1007/978-3-642-05076-3_1 . ISBN978-3-642-05076-3ISSN 2196-4831。2026年5月21日取得。
↑ Wieder, William R.; Cleveland, Cory C.; Townsend, Alan R. (2009 年 12 月). "熱帯湿潤林における落葉分解の制御" . Ecology . 90 (12): 3333– 41. Bibcode : 2009Ecol...90.3333W . doi : 10.1890/08-2294.1 . PMID 20120803 . 2026 年5 月 21 日取得.
↑ Liang, Biqing; Lehmann, Johannes; Solomon, Dawit; Kinyangi, James; Grossman, Julie; O'Neill, Brendan; Skjemstad, Jan O.; Thies, Janice; Luizaõ, Flávio J.; Petersen, Julie; Neves, Eduardo G. (2006 年 9 月). "ブラックカーボンは土壌の陽イオン交換容量を増加させる" . Soil Science Society of America Journal . 70 (5): 1719– 30. Bibcode : 2006SSASJ..70.1719L . doi : 10.2136/sssaj2005.0383 . 2026 年5 月 21 日取得.
↑ Neves, Eduardo G.; Petersen, James B.; Bartone, Robert N.; da Silva, Carlos Augusto (2003). "アマゾンの黒土の歴史的および社会文化的起源" . Lehmann, Johannes; Kern, Dirse C.; Glaser, Bruno; Woods, William I. (eds.). Amazonian Dark Earths: origin, properties, management . Berlin, Germany: Springer Science & Business Media . pp. 29– 50 . 2026年5月21日取得.
↑ 「Terra Preta de Indio」。コーネル大学、作物・土壌科学科。2013年4月24日のオリジナルからアーカイブ。 2026年5月21日取得。
↑ Lehmann, Johannes; Rondon, Marco (2006). "湿潤熱帯の高度に風化した土壌におけるバイオ炭土壌管理" . Uphoff, Norman; Ball, Andrew S.; Fernandes, Erick; Herren, Hans; Husson, Olivier; Laing, Mark; Palm, Cheryl; Pretty, Jules; Sánchez, Pedro; Sanginga, Nteranya; Thies, Janice (eds.). Biological approaches to sustainable soil systems . Boca Raton, Florida: CRC Press . pp. 517–30 . 2026年5月21日取得.
↑Yu, Xiangyang; Pan, Ligang; Ying, Guangguo; Kookana, Rai S. (2010). "Enhanced and irreversible sorption of pesticide pyrimethanil by soil amended with biochars". Journal of Environmental Sciences. 22 (4): 615–20. Bibcode:2010JEnvS..22..615Y. doi:10.1016/S1001-0742(09)60153-4. PMID20617740. Archived from the original on 22 July 2020. Retrieved 21 May 2026.
↑Whitman, Thea; Lehmann, Johannes (November 2009). "Biochar: one way forward for soil carbon in offset mechanisms in Africa?"(PDF). Environmental Science and Policy. 12 (7): 1024–7. Bibcode:2009ESPol..12.1024W. doi:10.1016/j.envsci.2009.07.013. S2CID14697278. Archived(PDF) from the original on 4 March 2019. Retrieved 21 May 2026.
↑Mwampamba, Tuyeni Heita (August 2007). "Has the woodfuel crisis returned? Urban charcoal consumption in Tanzania and its implications to present and future forest availability". Energy Policy. 35 (8): 4221–34. Bibcode:2007EnPol..35.4221M. doi:10.1016/j.enpol.2007.02.010. Retrieved 21 May 2026.
Bibliography
Donahue, Roy Luther; Miller, Raymond W.; Shickluna, John C. (1977). Soils: an introduction to soils and plant growth (4thed.). Englewood Cliffs, New Jersey: Prentice-Hall. ISBN978-0138219185. Retrieved 21 May 2026.
"Arizona Master Gardener Manual". Arizona Cooperative Extension, College of Agriculture, University of Arizona. Retrieved 21 May 2026.