Ersheh
- AfSIS
- Haplic Phaeozems: 65%
- Haplic Phaeozems: 20%
- Techniques
Soil properties (estimated): Bundibugyo, Yuganda
- Tarie (Terkip)
- pH
- Bulk density
- Organic carbon
- CEC
Korroti,eshara
Challenges
Korroti,eshara
- The ideal pH range for most crops is 6.5 to 7.0, therefore some crops may require slight pH adjustment for optimal growth
- To lower soil pH, add a source of acid, such as shredded leaves, sulfur, sawdust or peat moss
- Add alkaline material such as limestone to decrease soil acidity
- Apply 2.3 kg of lime per 30 square meters to raise the pH by one point
- Applying wood ashes will raise soil pH--Wood ashes contain up to 70 percent calcium carbonate, as well as potassium, phosphorus, and many trace elements. Because it is powdery, wood ash is a fast-acting liming material
- Limit the application of wood ashes to 1 kg per 30 square meters and only apply it every other year in the same area
- Breed aluminum-tolerant crops
Tatoowego(Khalfieh
- Many plant species are adapted to acidic or alkaline soils
- The availability of many plant nutrients (for example, P), non-essential elements (for example, Al, Cd, Pb), and essential trace elements (for example, Mn, Fe, Cu, Zn) is strongly dependent on soil pH (Miller and Gardiner 2001)
- Generally, metal cations (for example, Mn, Fe, Ni, Cu, Zn, Cd, Pb) become more available as pH decreases, while oxyanions (for example, SO4) become more available at alkaline pH levels
- Soil pH is strongly dependent on the chemical weathering environment. Soils in hot, humid areas and even mesic, wetter areas tend to be more acidic than those of much drier areas. Vegetation communities in those areas tend to be adapted to the soil conditions in which they developed
Challenges
Korroti,eshara
- To reduce high bulk density and compaction, minimize soil disturbance and production activities when soils are wet, use designated field roads or rows for equipment traffic, reduce the number of trips across the area, and maintain or increase soil organic matter
- Use grazing systems that minimize livestock traffic and loafing, provide protected heavy use areas, and adhere to recommended minimum grazing heights
- Use conservation crop rotation, cover crop, deep tillage, prescribed grazing residue, and tillage management
- Avoid plowing, timber harvesting, or compaction of the soil
Tatoowego(Khalfieh
- Soil bulk density may indicate soil compaction but is dependent on many soil factors including particle size distribution, soil organic matter content, and coarse fragment content
- Bulk density increases as the sand and rock content increases
- Bulk density decreases as the organic matter content increases
- A mineral soil with “ideal” physical properties has 50 percent solids and 50 percent pore space occupying a given volume of space
- At optimal water content, half the pore space is filled with water (such a soil will have a bulk density of 1.33 g/cm3)
- Roots usually grow well in soils with bulk densities of up to 1.4 g/cm3
- Root penetration begins to decline significantly at bulk densities above 1.7 g/cm3
- Above 1.5 g/cm3, there is an increasing probability of adverse effects from soil compaction or high rock content
- Coarse fragments—Soils with a coarse fragment content of > 50 percent to have a greater probability of adverse effects from infiltration rates that are too high, water storage capacity that is too low, more difficult root penetration, and greater difficulty in seed germination and seedling growth
- A high contents of coarse fragments can limit soil productivity
Challenges
- Difficult to raise organic matter content of well-aerated soils (coarse sands, soils in warm-hot and arid regions) because the added materials decompose rapidly
- Soil organic matter levels can be maintained with less organic residue in fine-textured soils in cold temperate and moist-wet regions with restricted aeration
Korroti,eshara
- Increase the organic matter content by returning organic materials to soils and adding rotations with high-residue crops and deep- or dense-rooting crops
- Ways to increase organic matter contents of soils: compost, cover crops/green manure crops, crop rotation, perennial forage crops, zero or reduced tillage, agroforestry
Tatoowego(Khalfieh
- Organic Carbon is, together with pH, the best simple indicator of the health status of the soil
- Soils with very high amounts of organic carbon are generally nutrient-rich, fertile soils with a good structure
- Very high soil organic carbon (SOC) can be an indicator of good crop yields
- Total organic carbon in mineral soils (percent): 1 to 5 = adequate levels,
- > 5 = excellent buildup of organic C with all associated benefits
Challenges
- Having a larger CEC values is an indicator that the soil has a greater capacity to hold cations
- A high CEC soil has a greater capacity to hold cations, so higher rates of fertilizer or lime are often required to change a high CEC soil
- high CEC is an indicator that there is a high reserve of nutrients in the soil
- Soils with low CEC can take a large amount of fertilizer or lime to correct
- A high CEC soil requires a higher soil cation level, or soil test, to provide adequate crop nutrition
Korroti,eshara
- The higher the CEC, the larger the quantity of lime that must be added to increase the soil pH
- Sandy soils need less lime than clay soils to increase the pH to desired levels
- The higher the CEC, the larger the quantities of soil additives the soil will need to change soil pH, either when increasing pH with lime or high bicarbonate irrigation water, or when decreasing pH with nitrogen fertilizers or elemental sulfur.. Acceptable saturation ranges for Soil CEC = 6-10: 3-5% K, 50-70% Ca, 8-20% Mg
Tatoowego(Khalfieh
Awleq (Forsa) | Depth | Tesrif | Texture Reaction - pH | Organic Carbon Conductivity - Electrical | Subsoil Cation Exchange | Clay Cation Exchange | Calcium Carbonate - Lime | Gypsum Sodium - Exchangeable |
---|---|---|---|---|---|---|---|---|
Topsoil | 4 | 6.5 | 1.75 | 22 | 50 | 0.1 | 0 | |
Subsoil | 4 | 6.5 | 0.66 | 21 | 63 | 1 | 0.1 |
Soil Triangle - Haplic Phaeozems
Tareef - Haplic Phaeozems
- Phaeozems accommodate soils of relatively wet grassland and forest regions in warm to cool (e.g. tropical highlands) moderately continental climates, humid enough that there is, in most years, some percolation through the soil, but also with periods in which the soil dries out; flat to undulating land; the natural vegetation is grassland such as tallgrass steppe and/or forest. They have dark, humus-rich surface. Phaeozems may or may not have secondary carbonates but have a high base saturation in the upper metre of the soil. Phaeozems are dark soils rich in organic matter from parent material Aeolian (loess), glacial till and other unconsolidated, predominantly basic materials. Haplic indicates that the major part of the upper 0.5 m of the soil profile is whole coloured. Some 70 million ha of Phaeozems are found in the humid and subhumid Central Lowlands and easternmost parts of the Great Plains of the United States of America. Another 50 million ha of Phaeozems are in the subtropical pampas of Argentina and Uruguay. The third largest area of Phaeozems (18 million ha) is in northeast China, followed by extensive areas in the centre of the Russian Federation. Smaller, mostly discontinuous areas are found in Central Europe, notably the Danube area of Hungary and adjacent countries and in montane areas in the tropics. Phaeozems are porous, fertile soils and make excellent farmland. In the United States of America and Argentina, Phaeozems are in use for the production of soybean and wheat (and other small grains). Phaeozems on the high plains of Texas produce good yields of irrigated cotton. Phaeozems in the temperate belt are planted to wheat, barley and vegetables alongside other crops. Wind and water erosion are serious hazards. Vast areas of Phaeozems are used for cattle rearing and fattening on improved pastures
Description - Clay loam
- A soil carrying 30 to 40 percent of clay is generally classed as a clay loam, and a soil carrying 40 to 50 per cent, of clay as a heavy clay loam. Clay loam compresses because of the microscopic size of its particles, so it has poor drainage and aeration. A clay loam usually has 25 to 35 percent of sand, and a heavy clay loam, 10 to 25 percent, of sand. The fair proportion of sand mixed with the clay in this type of soils makes them easier to handle than clay soils, and more porous. They are apt to be rich, especially in potash, not only because of the store of native plant food, but also because they are very retentive soils. The plant food in fertilizers that may be applied to them is not quickly leached away, as it is on sandy soils, but is held very tenaciously by this more compact soil. Crops upon clay loams are not likely to suffer from drought as badly as on clay soils, because water moves through them more freely. Some clay loams, however, are cold and wet. These soils more than any other type, are benefited by under-drainage. The clay loams are suitable for a larger range of cropping than any other soils, except the loams themselves. They are especially valuable for grass, wheat and corn. In handling clay loams attention should be given to the details of management that are beneficial to clay soils, and especially to under-drainage, judicious plowing and the incorporation of humus. Rice is one grain that thrives in clay loam and will happily grow in it as long as the soil is wet or flooded. Because clay drains poorly, a clay loam provides the wet conditions rice needs. Wheat grows best in silt loam or clay loam but needs good drainage and nutrient-rich soil. Barley also does best with good drainage but it grows well in clay or sandy loam. And oats need a very fine sandy loam but will grow in clay if it drains well. Corn can handle sandy to clay loam but will only yield an abundant crop if the soil is well-fertilized
Metrics/Discussion
Topic | Temen (Qimieh) | Sesila (tafaseel) |
---|---|---|
Tesrif | 4 | Tatoowego(Khalfieh
Tareef
|
Soil reference depth | 100 mm | ChallengesTareef
|
Base saturation | 89Fi meya alama | Challenges
Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Calcium carbonate CaCO3 - Lime | 0.1% weight | Tatoowego(KhalfiehTareef
|
Organic carbon | 1.75% weight | Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Cation exchange capacity - clay | 50 cmol/kg | Challenges
Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Cation exchange capacity - Ersheh | 22 cmol/kg | Challenges
Korroti,eshara
Tareef
|
Clay - percent - weight | 31% weight | Challenges
Korroti,eshara
Tatoowego(KhalfiehTareef
|
Gravel - percent - volume | 1% weight | ChallengesKorroti,esharaTareef
|
Sand - percent - weight | 34% weight | Challenges
Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Silt - percent - weight | 35% weight | Challenges
Korroti,esharaTatoowego(Khalfieh
Tareef
|
Electrical conductivity | 0 dS/m | ChallengesKorroti,esharaTatoowego(Khalfieh
Tareef
|
Gypsum content CaSO4 | 0% volume | Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Soil reaction - pH | 6.5 -log H+ | ChallengesKorroti,eshara
Tatoowego(Khalfieh
Tareef
|
Exchangeable sodium | 1Fi meya alama | Tareef
|
Reference bulk density | 1.29 kg/dm3 | Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Nitrogen (N) | ChallengesKorroti,eshara
Tatoowego(Khalfieh
| |
Phosphorus (P) | Challenges
Korroti,esharaTatoowego(Khalfieh
| |
Potassium (K) | Korroti,eshara
Tatoowego(Khalfieh
|
Awleq (Forsa) | Depth | Tesrif | Texture Reaction - pH | Organic Carbon Conductivity - Electrical | Subsoil Cation Exchange | Clay Cation Exchange | Calcium Carbonate - Lime | Gypsum Sodium - Exchangeable |
---|---|---|---|---|---|---|---|---|
Topsoil | 4 | 6.5 | 1.75 | 22 | 50 | 0.1 | 0 | |
Subsoil | 4 | 6.5 | 0.66 | 21 | 63 | 1 | 0.1 |
Soil Triangle - Haplic Phaeozems
Tareef - Haplic Phaeozems
- Phaeozems accommodate soils of relatively wet grassland and forest regions in warm to cool (e.g. tropical highlands) moderately continental climates, humid enough that there is, in most years, some percolation through the soil, but also with periods in which the soil dries out; flat to undulating land; the natural vegetation is grassland such as tallgrass steppe and/or forest. They have dark, humus-rich surface. Phaeozems may or may not have secondary carbonates but have a high base saturation in the upper metre of the soil. Phaeozems are dark soils rich in organic matter from parent material Aeolian (loess), glacial till and other unconsolidated, predominantly basic materials. Haplic indicates that the major part of the upper 0.5 m of the soil profile is whole coloured. Some 70 million ha of Phaeozems are found in the humid and subhumid Central Lowlands and easternmost parts of the Great Plains of the United States of America. Another 50 million ha of Phaeozems are in the subtropical pampas of Argentina and Uruguay. The third largest area of Phaeozems (18 million ha) is in northeast China, followed by extensive areas in the centre of the Russian Federation. Smaller, mostly discontinuous areas are found in Central Europe, notably the Danube area of Hungary and adjacent countries and in montane areas in the tropics. Phaeozems are porous, fertile soils and make excellent farmland. In the United States of America and Argentina, Phaeozems are in use for the production of soybean and wheat (and other small grains). Phaeozems on the high plains of Texas produce good yields of irrigated cotton. Phaeozems in the temperate belt are planted to wheat, barley and vegetables alongside other crops. Wind and water erosion are serious hazards. Vast areas of Phaeozems are used for cattle rearing and fattening on improved pastures
Description - Clay loam
- A soil carrying 30 to 40 percent of clay is generally classed as a clay loam, and a soil carrying 40 to 50 per cent, of clay as a heavy clay loam. Clay loam compresses because of the microscopic size of its particles, so it has poor drainage and aeration. A clay loam usually has 25 to 35 percent of sand, and a heavy clay loam, 10 to 25 percent, of sand. The fair proportion of sand mixed with the clay in this type of soils makes them easier to handle than clay soils, and more porous. They are apt to be rich, especially in potash, not only because of the store of native plant food, but also because they are very retentive soils. The plant food in fertilizers that may be applied to them is not quickly leached away, as it is on sandy soils, but is held very tenaciously by this more compact soil. Crops upon clay loams are not likely to suffer from drought as badly as on clay soils, because water moves through them more freely. Some clay loams, however, are cold and wet. These soils more than any other type, are benefited by under-drainage. The clay loams are suitable for a larger range of cropping than any other soils, except the loams themselves. They are especially valuable for grass, wheat and corn. In handling clay loams attention should be given to the details of management that are beneficial to clay soils, and especially to under-drainage, judicious plowing and the incorporation of humus. Rice is one grain that thrives in clay loam and will happily grow in it as long as the soil is wet or flooded. Because clay drains poorly, a clay loam provides the wet conditions rice needs. Wheat grows best in silt loam or clay loam but needs good drainage and nutrient-rich soil. Barley also does best with good drainage but it grows well in clay or sandy loam. And oats need a very fine sandy loam but will grow in clay if it drains well. Corn can handle sandy to clay loam but will only yield an abundant crop if the soil is well-fertilized
Metrics/Discussion
Topic | Temen (Qimieh) | Sesila (tafaseel) |
---|---|---|
Tesrif | 4 | Tatoowego(Khalfieh
Tareef
|
Soil reference depth | 100 mm | ChallengesTareef
|
Base saturation | 89Fi meya alama | Challenges
Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Calcium carbonate CaCO3 - Lime | 0.1% weight | Tatoowego(KhalfiehTareef
|
Organic carbon | 1.75% weight | Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Cation exchange capacity - clay | 50 cmol/kg | Challenges
Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Cation exchange capacity - Ersheh | 22 cmol/kg | Challenges
Korroti,eshara
Tareef
|
Clay - percent - weight | 31% weight | Challenges
Korroti,eshara
Tatoowego(KhalfiehTareef
|
Gravel - percent - volume | 1% weight | ChallengesKorroti,esharaTareef
|
Sand - percent - weight | 34% weight | Challenges
Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Silt - percent - weight | 35% weight | Challenges
Korroti,esharaTatoowego(Khalfieh
Tareef
|
Electrical conductivity | 0 dS/m | ChallengesKorroti,esharaTatoowego(Khalfieh
Tareef
|
Gypsum content CaSO4 | 0% volume | Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Soil reaction - pH | 6.5 -log H+ | ChallengesKorroti,eshara
Tatoowego(Khalfieh
Tareef
|
Exchangeable sodium | 1Fi meya alama | Tareef
|
Reference bulk density | 1.29 kg/dm3 | Korroti,eshara
Tatoowego(Khalfieh
Tareef
|
Nitrogen (N) | ChallengesKorroti,eshara
Tatoowego(Khalfieh
| |
Phosphorus (P) | Challenges
Korroti,esharaTatoowego(Khalfieh
| |
Potassium (K) | Korroti,eshara
Tatoowego(Khalfieh
|
Zero Tillage
Conservation tillage systems such as zero tillage cause minimum disturbance to the soil after the previous crop has been harvested. In zero tillage, the ideal is to plant direct into the soil, without hoeing or plowing. Tillage is reduced to ripping planting lines or making holes for planting with a hoe. Crop residues are left in the field to reduce soil erosion, conserve moisture, inhibit weed growth, and act as green manure. Zero tillage is not recommended when disease is present. To manage disease, crop residues must be either removed from the field and destroyed or deeply ploughed to reduce sources of disease infection and spread.
Advantages of conservation tillage include less machinery, labour and fuel, as well as reduced soil erosion and compaction. Disadvantages of conservation tillage include lower soil temperatures, slower germination and emergence when direct sowing is used, slower early growth, delayed competition with weeds, higher incidence of root diseases, heavier crop residue, the possibility of more difficult planter operation, weed spectrum changes, and potential increase of soil insect pests or insects that spend part of their life cycle in the soil (e.g. cutworms, thrips, leafmining flies, grubs). Cultivation exposes these pests to desiccation by the sun heat and to predation by natural enemies.
Green Manuring
Green manure legumes create nitrogen in the soil by fixing it from the atmosphere.
Benefits of Green Manure Cover Crops
- Easy to grow
- Increases soil organic matter
- Reduce soil losses from wind and water erosion
- If it is a legume, it can fix nitrogen. When the legume is mature, chopped up and added to the soil, it will add nitrogen to the soil which will be used by later crops on the land.
- The roots of the green manure crops extract nutrients from deep in the soil.
- The deep roots work to break up and aerate the soil
- When the green manure is added to the soil, it works to lighten and loosen the soil to aerate and improve drainage, making the soil healthier for later crops. After tilling in a green manure crop, we see the soil level in the farm beds raise several inches. The soil is loose and no longer compacted.
- Green manure crops include jack beans, perennial peanut, and Mucuna.
- These plants help the main crop by increasing soil fertility by adding nitrogen to the soil by nitrogen fixation.
- They add biomass (organic matter) to the soil.
- As cover crops, they reduce soil loss.
Planting Green Manure Crops
Green manure crops can be planting using intercropping with the main crop or by using crop rotation in which the green manure crop is planted in-between plantings of the main crop. For intercropping, plant the legume seeds in rows between rows of the main crop. Plow the legumes into the soil at the start of the rainy season.
In crop rotation, plant legumes after the main crop has been harvested. The legumes will benefit the field as a cover crop and as green manure. At full biomass maturity, plow the legumes into the soil as green manure for the next crop.
For a source of green manure to the field, cut the legumes at full maturity, shred, and spread over the field.
Preventing Soil Erosion while Adding Nutrients to the Soil
The first step in soil management is preventing the loss, or erosion, of soil. Topsoil is particularly vulnerable to erosion if not protected by plants or mulch or by other measures. The soil that remains after the loss of topsoil is usually less productive, which can result in lower yields. The challenge is to protect soil while using the land for food production and other non-food activities.
Soil erosion is caused mainly by wind and water but also by incorrect cultivation practices. Rain and wind dislodge and then carry away soil particles. Where the soil is bare or the vegetation poor, rainwater does not seep into the soil; instead it runs off and carries with it loose topsoil. Sloping land and light soils with low organic matter content are both prone to erosion. Once eroded, the soil is lost forever.
Soil erosion is a problem in regions with little vegetation, particularly in the semi-arid and arid zones. In the humid tropics, erosion was not considered a problem when the land was in its natural state, because the variety of native plants kept the soils covered at all times. Now, people are clearing more land for agricultural purposes, and the situation has changed. Heavy rains coupled with poor soil management of cultivated areas are now common causes of soil erosion in the humid areas.
Water Erosion
Some common forms of water erosion include:
- Sheet erosion: a thin top layer of soil is removed from the soil by the impact of rain. With sheet erosion, small heaps of loose material (e.g. grass) amass between fine lines of sand after a rainstorm. This erosion takes place across a whole garden or field.
- Rill erosion: water flows over minor depressions on the land's surface and cuts small channels into the soil. The erosion takes place along the length of these channels.
- Gully erosion: a gully forms along natural depressions on the soil's surface or on slopes. The head of a gully moves up the slope in the opposite direction of the flow of water. Gullies are symptoms of severe erosion.
Wind Erosion
This occurs mostly on light soils and bare land. High winds cause severe damage. Wind erosion is a common problem in dry and semi-arid areas, as well as in areas that get seasonal rains.
Unlike water which only erodes on slopes, wind can remove soil from flat land as well as from sloping land; it can also transport the soil particles through the air and deposit them far away. Soils vulnerable to wind erosion are dry, loose, light soils with little or no vegetative cover.
Plowing up and down a slope causes soil erosion. To prevent the loss of soils, certain measures must be taken.
These include:
- clearing only the land to be cultivated;
- planting along a contour and using grassed channels;
- establishing windbreaks and bench terraces;
- plowing along a contour;
- planting cover crops and mulching.
When clearing land for cultivation, the beneficial effects of certain trees and plants should be considered. Some trees should be left, since they may supply food, medicine, shade or, when they shed their leaves, organic matter.
Feeding the Soil
One of the main goals in growing crops is to make the soil fertile and well structured, so a wide range of useful crops can grow and produce well. In order to grow, plants require nutrients that are present in organic matter, such as nitrogen, calcium and phosphorus, as well as minerals and trace elements.
If the natural fertility or structure of the soil is poor, it must be continuously "fed" with organic matter, such as leaves and manure, in order to improve its productivity and water-holding capacity. As organic matter decomposes, it becomes food for plants. It also improves soil structure by loosening heavy clay and binding sandy soil.
Feeding the soil with organic matter is especially important in the early years of cultivating the land. Organic matter (i.e. waste from plants and livestock) can be collected and buried in the soil, where it will decompose. The organic matter also can be used to make compost, which can be applied to the soil to enrich its fertility.
The roots of legumes contain nitrogen-fixing bacteria. Therefore, intercropping or rotating legumes with other crops helps maintain or improve the nitrogen content of the soil, and this enhances the growth of other plants.
Healthy plants yield more and are better protected from insects and disease. The application of organic matter, such as compost, animal manure, green manure and soil from anthills, improves soil structure and adds nutrients to the soil.
Long-Term Soil Management
The ideal way to protect and feed the soil is to apply organic matter or compost regularly and to keep the soil covered with plants. A multilayer cropping system in which a mixture of trees and other plants with different maturity times are grown together will protect the soil and recycle nutrients. Leguminous plants such as cowpeas, groundnuts and beans are particularly useful in providing continuous nutrients for crops.
Apply Organic Matter to Soil to Improve the Crop
Plants can contain up to 90 percent water. The water is absorbed mainly through the root system of the plant. With the water, plant nutrients are absorbed. Healthy roots need air (aeration) for development. Excess water in the soil prevents air from penetrating and damages a plant's roots. Water management is therefore extremely important in regions with good water resources as well as in those where water is scarce.
The water-holding capacity of soil varies according to soil type. Soil with a high content of organic matter has better aeration, better structure and better water-holding capacity. Heavy, sticky soils are too dense to allow air in and water out, so roots cannot breathe and plants can have growth problems. When this kind of soil dries out, it sets like cement, and water takes a long time to soak into it. On the other hand, sandy, coarse-grained soils are too loose to hold water before it drains away. In this kind of soil, without a regular external water supply, a plant's roots cannot find enough water for growth. Regular application of organic matter will improve the ability of both these kinds of soil to hold and release enough water and air. During land preparation for planting, organic materials such as animal manure or compost should be applied to the land such that they are well incorporated into the soil.
Kegoo kasoreh ( masadir)
2. World reference base for soil resources 2006. 2nd edition. World Soil Resources Reports No. 103. FAO, Rome (http://www.fao.org/ag/agl/agll/wrb/doc/wrb2006final.pdf)
3. Lecture Notes on the Major Soils of the World, FAO, Rome, 2001 (http://www.itc.nl/~rossiter/Docs/WRB/wsrr94e.pdf).
4. Grameen Foundation (www.grameenfoundation.org)
5. Mississippi State University (http://msucares.com/lawn/garden/vegetables/soil/index.html)
6. How to Improve Soils (http://www.howtoimprovesoils.info/kinds-of-soils/clay-soils-clay-loams-loam-soils.html)
7. University of Arizona (http://ag.arizona.edu/pubs/garden/mg/soils/principal.html)
8. Wikipedia.org, "Soil pH" (http://en.wikipedia.org/wiki/Soil_pH)
9. PlanTea (http://www.plantea.com/pH.htm)
10. Wikipedia.org, "Tropical Agriculture" (http://en.wikipedia.org/wiki/Tropical_agriculture#Acidic_soils)
11. Wikipedia.org, "Alkali soils" (http://en.wikipedia.org/wiki/Alkali_soils)
12. Spectrum Analytic (http://www.spectrumanalytic.com/support/library/ff/CEC_BpH_and_percent_sat.htm)
13. FAO/IIASA/ISRIC/ISS-CAS/JRC, 2009. Harmonized World Soil Database (version 1.1). FAO, Rome, Italy and IIASA, Laxenburg, Austria (http://www.iiasa.ac.at/Research/LUC/External-World-soil-database/HWSD_Documentation.pdf)
14. Pennsylvania State University (http://pubs.cas.psu.edu/FreePubs/pdfs/uc038.pdf)
15. Clemson University (hubcap.clemson.edu/~blpprt/IL64.html)
16. Soil Quality for Environmental Health (http://soilquality.org/indicators/bulk_density.html)
17. Amacher, Michael C.
18. O’Neil, Katherine P.
19. Perry, Charles H. 2007. Soil vital signs: A new Soil Quality Index (SQI) for assessing forest soil health. Res. Pap. RMRS-RP-65WWW. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 12 p. (http://www.fs.fed.us/rm/pubs/rmrs_rp065.pdf)
20. Andre Bationo, Job Kihara, Bernard Vanlauwe, Boaz Waswa, Joseph Kimetu, "Soil organic carbon dynamics, functions and management in West African agro-ecosystems", Received 8 February 2005
21. accepted 18 August 2005 (http://www.zef.de/module/register/media/18ea_sdarticle.pdf)
22. Department of Primary Industries, Victoria, Australia (http://www.dpi.vic.gov.au/dpi/vro/vrosite.nsf/pages/gloss_HR#l).
23. World reference base for soil resources 2006. 2nd edition. World Soil Resources Reports No. 103. FAO, Rome, page 88 (http://www.fao.org/ag/agl/agll/wrb/doc/wrb2006final.pdf)
24. Lecture Notes on the Major Soils of the World, FAO, Rome, 2001, page 238 (http://www.itc.nl/~rossiter/Docs/WRB/wsrr94e.pdf).
25. CT ECO (http://www.cteco.uconn.edu/guides/Soils_Drainage.htm)
26. McDonald, A.J., Cornell University, "Soil Drainage Classification and Hydric Soil Indicators" (http://www.css.cornell.edu/courses/260/Lab%20Hydric%20Soils.pdf), last modified on August 8, 2002.
27. FAO (http://www.fao.org/nr/land/soils/harmonized-world-soil-database/soil-quality-for-crop-production/en/).
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