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Red soil

Red soil is a type of that develops from the of pre-Cambrian crystalline and metamorphic rocks in warm climates with varying rainfall, often moderate to low in contexts, and high temperatures, resulting in a distinctive reddish hue primarily due to the oxidation and accumulation of iron oxides such as . The term "red soil" is commonly used in for soils that align with Alfisols and Ultisols in the USDA system. These soils are typically less leached compared to lateritic soils and exhibit a range of 5.0 to 7.5, with depths varying from 25 to 50 cm, though they can be deeper in some regions. Red soils are widely distributed across tropical and subtropical regions globally, but they are particularly prominent in , where they cover extensive areas in states such as , southern , northeastern , parts of , and , encompassing approximately 350,000 km² (10.6% of India's land area). In these formations, the soils often develop on parent materials like granites, gneisses, and quartzites, leading to highly weathered profiles with, for example, low permeability (10⁻⁵ to 10⁻⁶ cm/s in some regions like Okinawa) and a specific of 2.6–2.8. Their texture ranges from sandy clay to clay , and they are generally porous and friable, though may be absent or minimal. Despite their prevalence, red soils are typically of low fertility, being deficient in essential nutrients like , , and (calcium), which limits their without amendments such as liming or fertilization. They correspond to soil orders like Ultisols in the USDA , which feature clay accumulation in subsurface horizons (argillic or kandic) and acidic conditions, making them suitable for crops such as millets, pulses, groundnuts, and under improved practices. In regions like southern and the Paraná Basin in , similar red soils support specific ecosystems, including grasslands and shrublands, highlighting their role in diverse land uses despite inherent challenges like low organic carbon and high aluminum content.

Characteristics

Physical Characteristics

Red soil exhibits a distinctive brick-red to reddish-brown coloration, primarily resulting from the accumulation of iron oxides, including and , which oxidize under well-aerated conditions. This pigmentation is most prominent in the subsoil horizons and reflects the soil's exposure to processes that concentrate these minerals. The intensity of the red hue can vary based on the relative proportions of , which imparts a stronger red tint, and , contributing more yellowish-brown shades. In terms of texture, red soil generally ranges from sandy clay to clay , characterized by a mix of , , and clay particles that influence its handling and behavior. This composition leads to moderate permeability, allowing reasonable infiltration while preventing excessive runoff in stable conditions. The is typically crumbly or granular, with aggregates that lack strong , particularly in drier states, rendering the soil susceptible to under heavy rainfall or in humid environments. Red soil demonstrates moderate , featuring a combination of macropores similar to sandy soils for and micropores within aggregates for limited retention. Its water-holding capacity supports adequate but is relatively low in drier variants, often resulting in high that can compact under management pressure. The profile usually comprises shallow to moderately deep A horizons overlying B horizons, with the latter distinctly due to enrichment and serving as the primary zone of accumulation.

Chemical Characteristics

Red soils are characterized by acidic conditions, with values typically ranging from 5.0 to 7.5, arising from of basic cations like calcium and magnesium under semi-arid to sub-humid climatic conditions with alternating wet and dry periods. This acidity enhances the of aluminum and iron, potentially leading to for plant roots as exchangeable Al³⁺ levels increase below pH 5.5. The (CEC) of red soils is generally low, ranging from 5 to 15 meq/100 g, which restricts their ability to retain essential nutrients such as , calcium, and magnesium against losses. This low CEC stems from the predominance of low-activity clays like and the accumulation of sesquioxides, limiting overall fertility and requiring frequent amendments for agricultural use. Sesquioxides, primarily Fe₂O₃ and Al₂O₃, constitute a significant portion of red soil profiles, often reaching 20-30% in horizons, contributing to the characteristic red hue from pigmentation. These compounds exhibit high reactivity in acidic environments, binding phosphates and other anions, which further diminishes nutrient availability. Base saturation in red soils is typically below 35%, with exchange sites dominated by hydrogen and aluminum ions rather than nutrient bases, exacerbating infertility and aluminum toxicity risks. This low saturation reflects extensive weathering and eluviation processes typical of these soils.

Composition

Mineral Composition

Red soil is characterized by a mineral composition dominated by secondary minerals formed through intense weathering, particularly in tropical and subtropical environments. The primary clay mineral is kaolinite, which typically constitutes 50-70% of the clay fraction in Ultisols and Oxisols, reflecting its low cation exchange capacity and stability in highly leached conditions. This dominance underscores the soil's advanced stage of mineral alteration, where kaolinite serves as a structural framework for the fine particle matrix. Iron-bearing minerals, primarily (Fe₂O₃) and (FeOOH), are key components that impart the characteristic red coloration through the oxidation of iron under well-aerated, humid conditions. predominates in redder variants, while is more common in slightly less oxidized profiles, together comprising significant portions of the fraction in these soils. These minerals contribute to the soil's and color stability, with often exceeding in abundance in highly weathered red horizons. In the coarser fractions, and feldspars are prevalent in the sand and components, derived from resistant primary minerals in parent rocks and enhancing the soil's granular structure. , in particular, forms the bulk of these fractions, resisting further breakdown and maintaining a relatively coarse . Accessory minerals include (Al(OH)₃), which appears in highly weathered profiles as a product of aluminum accumulation, and remnants of , present in trace amounts from incomplete of primary silicates. is especially notable in , where it stabilizes the mineral assemblage in iron- and aluminum-rich environments. Overall, the mineralogy indicates an advanced stage, with red soils classified primarily as Ultisols or in the USDA system, featuring low contents of weatherable minerals like feldspars and . Aluminum-rich minerals such as and contribute to the soil's variable charge characteristics.

Organic and Elemental Composition

Red soils typically exhibit low content, ranging from 0.5% to 2%, which decreases with soil depth owing to rapid microbial in warm, humid climates characteristic of their formation environments. This limited organic fraction contributes to reduced stability and retention, with surface horizons often containing the highest concentrations before a sharp decline in subsurface layers. In terms of elemental composition, red soils are enriched with iron () at 2-5% and aluminum () at 5-10%, primarily occurring as oxides and hydroxides that impart the characteristic reddish hue and influence soil reactivity. Conversely, base cations such as calcium (), magnesium (), and potassium (K) remain low, typically below 1% total content, reflecting intense leaching in these acidic profiles with base saturation under 35%. Nitrogen levels are also generally low, around 0.05-0.1%, limiting microbial activity and without external inputs. Phosphorus availability in red soils is severely constrained, often below 10 , due to fixation by iron and aluminum oxides that bind into insoluble forms, reducing its uptake by . Trace elements like () and () show variability across regions but are frequently deficient, with Zn particularly prone to shortages in these highly weathered, acidic conditions. formation in red soils is limited, featuring a thin A horizon with poorly developed that fail to accumulate substantially due to accelerated and eluviation. This results in an ochric epipedon that is light-colored and low in organic complexes, further emphasizing the soil's inherent poverty.

Formation and Development

Pedogenic Processes

Red soils typically develop from parent materials such as , , or through prolonged pedogenic processes spanning over 10,000 years. These igneous and metamorphic rocks undergo transformation under conditions favoring intense chemical , where primary minerals are destroyed at rates up to 90-100%. Unlike the more intense laterization seen in higher rainfall areas leading to lateritic soils, red soil formation involves moderate and sesquioxide enrichment. A key process is desilication, involving the loss of silica (SiO₂) through dissolution and removal, with significant reductions occurring in highly weathered profiles. Concurrently, leaching by percolating water removes bases such as calcium (Ca), magnesium (Mg), sodium (Na), and potassium (K), at substantial levels, which contributes to soil acidity. This leaching enhances further weathering and promotes the translocation of solutes downward. Sesquioxide enrichment follows, characterized by the illuviation and accumulation of iron () and aluminum () oxides in the B horizon, forming enriched layers. Iron accumulates preferentially over aluminum during this phase. Additionally, the oxidation of ferrous iron (Fe²⁺) to ferric iron (Fe³⁺) imparts the characteristic to the over millennia, as ferric oxides produce reddish hues upon hydration. Kaolinite emerges as the dominant end-product of this extensive .

Environmental Influences

Red soils develop under tropical to subtropical climates characterized by mean annual temperatures exceeding 20°C and ranging from 500 to 1000 mm, conditions that facilitate intense and the of bases while concentrating iron oxides. These warm environments with seasonal variations in rainfall promote alternating wet and dry periods, which enhance the oxidation of iron minerals, imparting the distinctive red hue to the soil through the formation of . Such climatic regimes are essential for the chemical that defines red soil profiles, distinguishing them from soils in more arid or perennially wet settings. Topography plays a critical role in red soil genesis by influencing and , with formation favored on undulating uplands or plateaus that prevent waterlogging and support oxidative processes. Well-drained slopes in these landscapes allow oxygen to penetrate the , enabling the aerobic oxidation of iron necessary for the red pigmentation, whereas poorly drained lowlands lead to reduced conditions and different soil types. Biotic factors, particularly vegetation cover, further shape red soil development; savanna grasslands or forests predominate, releasing organic acids from decomposing litter that accelerate mineral weathering and contribute to soil acidity. These communities enhance the breakdown of by supplying that chelate metals, promoting the translocation of elements within the profile over time. The time factor is vital for complete red soil maturation, typically requiring 5,000 to 50,000 years for horizon and iron accumulation to stabilize. Human influences, including , primarily accelerate surface on existing red soils but do not fundamentally drive their pedogenic formation.

Geographic Distribution

In , red soils are extensively distributed across subtropical and tropical regions, particularly in and , where they form under conditions of high intensity and seasonal rainfall. These soils derive their characteristic reddish hue from iron oxides and are prominent in areas with granitic, gneissic, or ic parent materials. hosts one of the largest extents of red soils in , covering approximately 350,000 km² or 10.6% of the country's total land area, primarily across the in states such as , , , and . These soils result from intensive of and other crystalline rocks in semi-arid to sub-humid climates with low rainfall. In , red soils span a vast area of about 1.02 million km² in the southern provinces, including , , , and , representing a significant portion of the subtropical zone influenced by climates. This aligns with the red soil hilly , which encompasses roughly 10% of China's land and is shaped by tropical to subtropical processes on and other acidic rocks. Red soils also occur in parts of , notably in , , and , where they are often classified as lateritic red soils associated with tropical of ferruginous rocks under high and alternating wet-dry cycles. In these regions, the soils contribute to diverse landscapes from highlands to coastal plains. Local variations distinguish Asian red soils; for instance, variants tend to be sandier and more porous, facilitating but limiting water retention, while red soils are generally clayier with elevated aluminum content, enhancing their stickiness and susceptibility to in hilly terrains. These soils typically exhibit acidic levels below 5.5, influencing their agricultural potential. Economically, red soils in support key crops such as and millets, including and , which thrive in their well-drained, iron-rich profiles across rainfed uplands. In , these soils underpin plantations in acidic, humid southern areas and double-cropping systems of , leveraging their capacity for wet-season cultivation despite nutrient limitations.

Europe

In Europe, red soils are predominantly represented by terra rossa, a type of reddish, clayey to silty-clay soil that is limited to the and differs from the more acidic, tropical red soils found elsewhere due to its nature and neutral pH. These soils develop as thin, discontinuous layers on hard and parent materials, often in karstic landscapes with high internal drainage, and their red color arises from iron oxides such as formed through rubification processes. Unlike broader global distributions, European terra rossa is shaped by the semi-arid featuring wet winters and dry summers that facilitate decalcification, clay illuviation, and iron oxidation during alternating wet and dry periods. In , terra rossa is widespread but most prominent in southern regions such as and the , where it forms thin, calcareous soils on limestone karsts and basic igneous rocks, serving as a key agricultural resource. These variants exhibit higher calcium content derived from residues, with a pH typically ranging from 6.5 to 7.5 and high base saturation exceeding 90%, making them more neutral and less acidic than tropical counterparts. Formation occurs under the influence of Pleistocene geomorphological changes and the Mediterranean climate's wet winters, which promote and pedogenic processes like bisiallitization on sloping terrains. Similar terra rossa occurrences extend to other Mediterranean European areas, including southern Italy's region, Spain's , and Croatia's and , where soils derive from , , or occasionally volcanic parent rocks, maintaining the characteristic reddish hue and profile. In these locales, the soils support traditional crops like and grapes, thriving in the well-drained, nutrient-retentive conditions suitable for Mediterranean and olive groves, as seen in northern Italy's Haplic Luvisols used for wine production. However, their occurrence on steep slopes renders them highly prone to , exacerbated by the region's seasonal rainfall patterns and historical , necessitating careful to prevent .

North America

In , red soils are primarily classified as Ultisols in the United States, occurring extensively in the southeastern states such as and . These soils develop from the weathering of mountain materials under humid subtropical climates, resulting in reddish clay-rich subsoils due to accumulation. Ultisols cover approximately 9.2% of the U.S. land area, equivalent to about 840,000 km², and are dominant in regions like the Piedmont Plateau. In , red soils are more restricted, appearing as podzolic-red intergrades and Brunisolic soils in and the interior of , formed on glacial till deposits. These occur in limited areas, influenced by temperate humid conditions and forested vegetation. Brunisols, which include reddish variants, occupy over 1.2 million km² across but are concentrated in southern zones for red expressions. North American red soils exhibit variations that enhance fertility compared to tropical counterparts, owing to cooler climates that reduce intense and weathering. They typically have low content, contributing to moderate natural productivity. However, the region's sloping terrain leads to high vulnerability, historically exacerbated by . Overall, red soils span about 1 million km² in and have been historically linked to the , where they supported extensive cotton cultivation from the late onward. In modern contexts, management emphasizes conservation tillage to mitigate slope-induced and sustain productivity.

Other Regions

Red soils are widespread in , particularly on landscapes in countries such as and , derived from highly leached granitic parent materials under seasonal rainfall regimes. These soils exhibit deep and accumulation, contributing to their characteristic red hue, and are often associated with nutrient-poor conditions in tropical and subtropical climates. In , red earth soils dominate the arid interiors, including regions like , spanning vast expanses, particularly in low-rainfall zones receiving less than 500 mm annually. These variants feature moderate with notable silica retention due to limited in semi-arid environments, supporting sparse vegetation such as spinifex grasslands. South American red soils occur prominently on the Brazilian Plateau and in portions of , such as the northeastern , where they form under cerrado ecosystems characterized by well-drained, acidic profiles. In the cerrado, red latosols (equivalent to ) predominate, reflecting intense tropical and association with nutrient-deficient, iron-rich substrates that sustain diverse woody-grass mosaics. Regional variations highlight differences in soil chemistry; African red soils often display higher aluminum toxicity linked to low pH levels below 5.5, exacerbating limitations for crop growth in acidic profiles, whereas counterparts retain more silica owing to drier conditions that reduce dissolution. soils are estimated to cover a significant portion of the world's land area, underscoring their critical role in tropical and subtropical despite inherent fertility challenges.

Soil Fertility

Fertility Assessment

Red soils exhibit low inherent fertility primarily due to extensive nutrient facilitated by high rainfall and acidic conditions in their typical tropical and subtropical environments. This leaching depletes essential cations and anions, resulting in lower productivity potential compared to more fertile soils under comparable management. Their overall rating places them in the low to moderate fertility category, limiting agricultural yields without interventions, though they support drought-tolerant crops owing to their coarser texture. Key metrics underscoring this low fertility include soil organic carbon levels typically below 1% (often around 0.94% in unamended profiles), available typically below 250 kg/ha in surface layers, and phosphorus fixation rates exceeding 80% attributable to iron and aluminum oxides. These values reflect the soil's limited capacity to retain and supply , with organic carbon serving as a critical indicator of overall and microbial activity. The acidic , often below 5.5, further exacerbates nutrient availability issues by enhancing aluminum and reducing base saturation. Fertility assessment in red soils employs standardized extraction methods to quantify available nutrients accurately. Mehlich-3 extraction is commonly used for and , providing a reliable measure of plant-available forms in acidic conditions, while ammonium acetate extraction determines exchangeable bases such as calcium, magnesium, and . These techniques allow for site-specific evaluations, revealing spatial and depth-related variations in nutrient status. Fertility varies significantly across profiles, with younger, less weathered red soils displaying higher inherent levels due to reduced over time compared to mature profiles. However, even in these cases, poor water retention—stemming from low and sandy-loamy textures—constrains overall productivity, making essential for sustained cropping. Historically, red soils were classified as problem soils in 20th-century , particularly in regions like southern , where their low fertility and proneness posed challenges to and led to early recognition in surveys as requiring specialized . This influenced post-independence agricultural policies aimed at reclaiming such lands through on tropical soil dynamics.

Nutrient Deficiencies

Red soils frequently suffer from nitrogen deficiencies due to low organic matter content, which results in reduced mineralization rates and limited supply for uptake. These soils also experience significant annual losses primarily through in permeable profiles and under warm, moist conditions prevalent in tropical environments. availability in red soils is severely restricted by strong and fixation onto iron and aluminum oxides, which bind applied and make less than 5% accessible to crops; available levels below 15 are considered critically low for growth. Micronutrient deficiencies are widespread in red soils, with and shortages commonly observed in alkaline variants due to reduced solubility and low , while deficiency predominates in acidic types because low enhances adsorption of ions by iron and aluminum oxides. status in red soils is generally moderate but prone to depletion under intensive cultivation, such as with , where high potassium-demanding crops rapidly exhaust supplies; exchangeable concentrations below 0.2 meq/100g indicate deficiency risks. Sulfur levels are notably low in high-rainfall regions of red soils, where removes ions from the upper horizons, compounded by inherently low sulfur reserves. The low in red soils, stemming from their kaolinitic clay minerals and dominance, further contributes to inefficient retention of these nutrients.

Management Practices

pH and Liming

Red soils are often acidic due to intensive of bases under high rainfall and conditions. The primary goal of management in red soils is to raise the to a target range of 6.0-6.5, which minimizes aluminum () toxicity that inhibits growth and uptake in most crops. This range ensures optimal conditions for crop performance while avoiding excessive alkalinity. Liming serves as the main technique for pH adjustment, utilizing materials such as calcitic (CaCO₃) for calcium supplementation or dolomitic (CaMg(CO₃)₂) to also address magnesium deficiencies common in these soils. Application rates typically range from 1 to 5 tons per , determined by soil index, initial , and to achieve the desired elevation without over-application. The liming process involves incorporating the material into the top 15-20 of soil to ensure even distribution and reaction with soil acids, with noticeable pH changes occurring within 3-6 months depending on and . Benefits include elevating base saturation above 50%, which enhances , and improving (P) availability by reducing fixation with Al and iron oxides prevalent in red soils. However, over-liming can induce (Mn) deficiency by raising too high, limiting Mn and affecting crop nutrition. Regional variations exist; for instance, red soils in , such as terra rossa developed on , often require minimal or no liming due to their inherently higher and lower acidity.

Nutrient Application

Red soils, characterized by high iron and aluminum content, often require targeted nutrient supplementation to address common deficiencies, particularly in , which is prevalent due to strong fixation mechanisms. application in red soils typically involves or at rates of 50-150 kg/ha, depending on type and testing results, with split applications recommended to minimize volatilization and losses—commonly 60% at planting or early growth and 40% during peak demand periods. For , or rock phosphate is applied at 20-60 kg/ha P₂O₅, preferably banded near the root zone to reduce fixation by iron and aluminum oxides and enhance availability to crops. Potassium is supplied via muriate of , with application rates guided by testing to maintain adequate levels, while micronutrients like are provided as chelated Zn formulations to improve uptake in these low-fertility soils. In irrigated red soil systems, such as those supporting or horticultural crops, fertigation delivers soluble nutrients directly to the root zone for precise timing and reduced losses, while foliar sprays offer quick correction for deficiencies during critical growth stages. Nutrient recovery efficiency in red soils ranges from 30-50% for and lower for due to fixation and , underscoring the need for integration with to sustain long-term fertility.

Organic Matter and Crop Rotation

Red soils, characterized by their low baseline content typically ranging from 0.5% to 1%, benefit significantly from the incorporation of amendments to enhance . Green manures, particularly such as sunn hemp (Crotalaria juncea) and dhaincha (Sesbania aculeata), are commonly grown and plowed under after 40-60 days to add and residues, with studies showing N accumulation rates of 80-100 kg/ha in suitable conditions. application at rates of 5-10 t/ha/year is recommended to gradually build levels to 1-2%, as demonstrated in long-term trials on red soils in southern where consistent additions improved overall indices. These inputs provide a slow-release source of and help counteract the inherent in these iron-rich, acidic soils. The addition of organic matter through these amendments improves by promoting aggregate formation and stability, which enhances water infiltration and root penetration. It also increases (CEC) by 20-50% in low-CEC red soils, allowing better retention of essential cations like calcium and magnesium. Furthermore, organic matter boosts microbial activity, with populations of beneficial and fungi rising by up to 2-3 times, facilitating nutrient cycling and suppressing pathogens. is another key benefit, as elevating organic matter from 1% to 3% can reduce soil loss by 20-33% through improved surface cover and reduced runoff velocity, according to models like the Universal Soil Loss Equation applied to similar tropical soils. Crop rotation incorporating legume-cereal cycles, such as -wheat or blackgram-maize, is a vital practice for red soil management, leveraging biological to supply 20-50 kg N/ha from legumes like , thereby reducing dependency on external inputs. These rotations disrupt and cycles, with legume phases breaking cereal pathogens and cereal phases limiting legume-specific nematodes, leading to 10-20% yield stability improvements in subsequent crops. In Indian contexts, -wheat rotations on red soils have shown consistent nitrogen contributions from soybean fixation, averaging 30-40 kg/ha net gain to the soil. Complementary practices include combined with cover crops like or pigeonpea to maintain ground cover and minimize disturbance, preserving decomposition in place. In tropical red soil regions, mulching with crop residues or biomass at 2-5 t/ha post-harvest further protects against heavy rainfall and maintains moisture, with studies in southern reporting up to 40% reduction in . Over the long term, sustained inputs and rotations can increase overall by 20-30% within 5 years, as evidenced by enhanced availability and crop yields in experiments on red soils. For instance, in long-term trials involving blackgram rotations with cereals, amendments led to a 25% rise in available and , alongside 15-20% higher blackgram yields compared to continuous , underscoring the role of these practices in restoring degraded red soil productivity.

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