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El Nino or La Nina – manage nitrogen (N) in the soil to ensure maximum maize yield, maximum profit and minimum risk.

By Nitrogen, Nitrogen Products No Comments

AFRIKAANS: El Nino of La Nina – bestuur stikstof (N) in die grond om maksimum mielieopbrengs, maksimum wins en minimum risiko te verseker The quantity of measurable inorganic N that should be in the soil throughout the growing period for maximum yield does not differ between El Nino (dry) or La Nina (wet) or average rainfall seasons but the actual yield, profitability and risk will differ to a large extent between these conditions. The quantity of N that is taken up and utilized by the crop will also differ largely between dry and wet seasons. For this reason it can be expected that more N will be applied during a wet season to maintain the quantity of N in the soil. It can also be expected that more N will be left over in the soil after a dry season which can effectively be utilized during the next season. The management of a threshold value for N in the soil for every season will effectively result in fertilization according to obtained yield and N removal from the soil over seasons. N-losses and N-toxicity effects will however very strongly be affected by an under or over supply of rain. Apart from soil N-measurements, choice of N-source and N-management practices can effectively be used to reduce these negative effects. El Nino conditions also coincide with high temperatures resulting in volatilization losses from ammonia forming products such as urea. Ammonia losses can result from surface applications as well as soil incorporated applications when the topsoil dries out. Ammonia released in close proximity of plant roots will be toxic under dry conditions. Urease inhibitors such as NBPT will effectively reduce or delay volatilization and toxicity from urea but will not eliminate these effects. Almost no N will volatilize from LAN even at high temperatures. LAN will only be moderately toxic at high concentrations. The band placement of high concentrations ammonia forming N-sources at planting but even before plating should therefore be avoided. La Nina conditions also coincides with heavy downpours over short periods resulting in N-leaching in well drain soils or water logging in poorly drained soils. Urea-N and nitrate-N are equally leachable but due to the fact that nitrate uptake is much quicker it will effectively leach much less than urea. Ammonium-N does not leach significantly and is also taken up much quicker than urea-N. LAN will therefore also leach much less than urea. Due to the possible risk of leaching pre-plant applications should rather be avoided and multiple post-plant topdressings considered. N is not taken up effectively in soils that are waterlogged for prolonged periods. Oxygen is required for N-uptake but also for the nitrification process. Consequently high levels of ammonium-N and nitrite-N, which are toxic, will accumulate. Nitrate-N dissolved in soil water near the soil surface will be converted to atmospheric N through the denitrification process and lost. Vertical or lateral drainage of soils should improve this condition.  

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USING COVER CROPS TO IMPROVE THE SOIL HEALTH ON YOUR FARM

By Conferences and Training No Comments

Book your place for the annual No-Till Conference  to held on from 4 – 6 September 2018 at the ATKV Drakensville Holliday Resort, Drakensville, Kwa Zulu Natal. The theme for this years conference is Managing Adversity with Diversity with Emerging Cover Crop Strategies by Making Cover Crops Pay. Steve Groff from the USA is this years international guest speaker and will conduct an in depth Cover Crop and Soil Fertility workshop discussing “Tips for Making Cover Crops Work in Dryland Areas”,  ” Taking Cover Crops to the Next Level” and “Bringing Animals Back to the Land”. This conference provides a comprehensive program, some of the speakers include soil scientist Guy Thibaud covering “Restoration of previously degraded soils is a key factor in the transition to No-Till”  Simon Hodgson on “using cover crops and plants to advance biological control of insects” and Dr Colin Forbes on “Moving to No-Till on a mixed farming operation” I you have an interest in Conservation Agriculture and improving the productivity of your soil, this conference provides and excellent opportunity to meet research scientists and farmers who will share their experiences and learnings on how to successfully reap the benefits of No-Till farming. Motivational speaker Quinton Coetzee will address the delegates on Wednesday evening on “THRIVING IN TOUGH TIMES – Lessons from the Wild”. Take advantage of the Early Bird Registration which lasts until 24 August 2018 to avoid the late registration fee. For more information on the principles and practice of no-till farming and the No-Till club visit: www.notillclub.com 2018 NO-TILL CONFERENCE PROGRAMME   2018 BEWARINGSLANDBOUKONFERENSIE PROGRAM 2018 Delegates Registration Form 2018 Contact Numbers For Accommodation

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FACTORS DETERMINING THE EFFICACY OF AGRICULTURAL LIME

By LIME & LIMING PRODUCTS One Comment

South Africa has an abundance of agricultural lime sources distributed throughout the country which should enable farmers to source lime as economically as possible. Lime is classified as a Group 2 fertilizer and regulated by The Fertilizer, Farm Feeds and Agricultural Remedies Act of 1947 (Act 36 of 1947). Dolomitic and calcitic lime sources are used to ameliorate soil acidity, Al3+ and Mn2+ toxicities, raise soil pH and manage calcium and magnesium levels in the soil. The sources of lime may be of both natural and industrial origin and vary significantly in their chemical and physical properties which in turn will determine the efficacy the product being used. Factors affecting efficacy of lime In the article, Soil Acidity and its Management in Crop and Pasture Production; Miles and Farina indicate that the effectiveness of various liming materials varies widely, with the following factors being of particular importance: Chemical purity ─ the presence or otherwise of non-reactive materials such as sand and clay greatly affects the neutralizing value of the lime (importantly, the colour of the liming material is not a reliable indicator of its quality!). Chemical composition ─ the nature of the calcium and magnesium compounds present. Fineness ─ the finer the lime particles, the faster will be their reaction in the soil. Lime particles larger than 0.84 mm in diameter (about the size of a match head) are of little value. Very coarse liming materials are completely ineffective. Hardness ─ the solubility, and hence neutralizing value, of lime depends on whether it is derived from hard crystalline material or from softer relatively unconsolidated material. Where uncertainty exists as to the quality of a particular liming material, they advise that a sample should be submitted for analysis. The rate of chemical reaction When lime is applied to the soil it reacts with the acidic components of the soil, H+, Al3+ and Mn2+ , the rate of chemical reaction is determined by temperature, surface area for reaction, relative concentration of the reactants and the presence of soil moisture. Four factors determine the efficiency of lime: Rate of application Purity (CCE) Particle size distribution Degree of incorporation into soil Chemical purity – Calcium Carbonate Equivalent (CCE) The chemical composition of lime varies according to its geological or industrial origin. The term calcium carbonate equivalent (CCE) is a measure used to distinguish the neutralizing capacity of a lime source relative to the mass of pure calcium carbonate required to neutralize hydrochloric acid (HCl). The CCE of pure calcium carbonate is rated as 100%, pure magnesium carbonate has a lower molecular mass and as such less magnesium carbonate is required to neutralize the equivalent amount of HCl, the CCE of magnesium carbonate is 119%. The CCE of lime will vary according to the calcium (Ca) and magnesium (Mg) content as well as other impurities such as sand and clay; large variances in CCE may exist between different sources of lime. The minimum CCE of lime in terms of Act 36 is 70%. Fineness –…

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Dr Neil Miles consulting soil scientist

Dr Neil Miles, consulting soil scientist

Neil Miles is a consulting soil scientist based in Mount Edgecombe. Prior to entering into consultancy, he spent 28 years with the KZN Department of Agriculture, as a research scientist and research manager, followed by 10 years in research and advisory work with the South African Sugarcane Research Institute (SASRI).

Neil played a leading role in the development of both the Cedara Fertilizer Advisory Service and SASRI’s Fertiliser Advisory Service (FAS). His PhD, through the University of Natal, focused on the nutrition of intensive pastures.  Neil’s particular interests are soil health and the nutrition of crops and pastures.

Contact Neil: milesofsoil@gmail.com