32MANAGING SOIL ORGANIC MATTER: A PRACTICAL GUIDEOrganic <strong>matter</strong> and cation exchangeThe ability of a <strong>soil</strong> to hold positively charged cationssuch as calcium, magnesium, potassium, sodium,hydrogen and aluminium at a given pH determinesits cation exchange capacity. Cation exchangemeasures the ability of a <strong>soil</strong> to hold on to and supplynutrients to plants. The cation exchange capacity ofa <strong>soil</strong> provides information on its structural stability,resilience, nutrient status and pH buffering capacity.Sodium and aluminium are negatively correlatedwith plant growth. Soil test results are expressedeither in milliequivalents per 100 grams <strong>soil</strong>(meq/100 g) or centimoles of charge per kilogram(cmol/kg).Soils have variable cation exchange capacityranging from sands, with a very low cation exchangecapacity often less than 3 meq/100 g, to vermiculite,which may hold up to 200 meq/100 g. Kaoliniticclays have a moderate cation exchange capacityof about 10 meq/100 g, while other clays such asillite and smectite have a higher exchange capacity(Purdie 1998).Table 4.1 contains information on the cationexchange of clay minerals.Table 4.1 Indicative cation exchange capacity ofdifferent clay minerals in <strong>soil</strong> (Moore et al. 1998).Clay mineralCation exchange capacity (meq/100g)Kaolinite 3-15Illite 10-40Montmorillonite 70-100Smectite 80-150Vermiculite 100-150Humified <strong>organic</strong> <strong>matter</strong> has a very high cationexchange capacity from 250-400 meq/100g. Therefore, in <strong>soil</strong>s with low clay content theamount of humus and resistant <strong>soil</strong> <strong>organic</strong> <strong>matter</strong>is increasingly important to nutrient exchangebecause its large surface area gathers (adsorbs)cations from the <strong>soil</strong> solution, holding nutrientsthat would otherwise leach. Williams and Donald(1957) estimate that each percentage increase in<strong>soil</strong> <strong>organic</strong> carbon is the equivalent of 2.2 meq/100g cation exchange and in some <strong>soil</strong>s contributesas much as 85 per cent of the cation exchangecapacity (Helling et al. 1964; Turpault et al. 2005;Hoyle et al. 2011).The contribution of <strong>organic</strong> <strong>matter</strong> to <strong>soil</strong> cationexchange capacity declines with <strong>soil</strong> depth, decreasing<strong>soil</strong> pH (i.e. increasing <strong>soil</strong> acidity) and with increasingclay content (see Table 4.2).Table 4.2 Indicative cation exchange capacity fordifferent <strong>soil</strong> textures and <strong>organic</strong> <strong>matter</strong>.Soil textureCation exchange capacity (meq/100g)Sand 1-5Sandy loam 2-15Silt loam 10-25Clay loam/silty clay loam 15-35Clay 25-150Organic <strong>matter</strong> 40-200Humified <strong>organic</strong> <strong>matter</strong> 250-400NITROGEN, PHOSPHORUS, SULPHURAND ORGANIC MATTEROrganic <strong>matter</strong> contains a large store of nutrients— the majority of which are unavailable for plantuptake. It estimated that 2-4 per cent of <strong>soil</strong> <strong>organic</strong><strong>matter</strong> is decomposed each year (Rice 2002). Usingan average three per cent turnover and based on acarbon to nutrient ratio of 1000 (C):100 (N):15 (P):15(S), this suggests for a <strong>soil</strong> which has 1400 tonnesof <strong>soil</strong> per hectare and a <strong>soil</strong> <strong>organic</strong> carbon contentof 2.1 per cent, there would be a release of about 88kg nitrogen, 13 kg phosphorous and 13 kg sulphureach year from <strong>organic</strong> <strong>matter</strong>.Nitrogen supplyIn most <strong>soil</strong>s, while nearly all nitrogen is presentin <strong>organic</strong> form, plants are generally better able totake up in<strong>organic</strong> (mineral) nitrogen forms such asammonium (NH 4+) and nitrate (NO 3-). Nitrate is thedominant form of nitrogen taken up by agriculturalplants.The conversion of <strong>organic</strong> nitrogen to in<strong>organic</strong>nitrogen is a biological process associated withthe mineralisation (decomposition) of <strong>organic</strong><strong>matter</strong>. Mineralisation results in the productionof ammonium, which is predominantly takenupby and immobilised within <strong>soil</strong> microbes andthen transformed via nitrification to nitrate. Theseprocesses can be limited by <strong>soil</strong> pH Caless than 5.5,poor <strong>soil</strong> permeability resulting in water-logged <strong>soil</strong>s,carbon availability, drying <strong>soil</strong>s and temperaturesbelow 20°C (Mengel and Kirkby 1987).Soil biological processes are also integral to the
33MANAGING SOIL ORGANIC MATTER: A PRACTICAL GUIDEavailability of the majority of in<strong>organic</strong> fertilisersapplied to <strong>soil</strong>, which are transformed into nitrateby <strong>soil</strong> microbes before being taken up by plants.This includes urea which is either decomposedby enzymes or chemically hydrolyzed to produceammonia and carbon dioxide. The ammonia isthen converted by microbes into ammonium andsubsequently converted into nitrate by specialistmicroorganisms through a process known asnitrification.In Australia, in<strong>organic</strong> mineral fertilisers oftenmake up as little as 20 per cent of crop uptakedue to relatively low fertiliser applications and poornitrogen use efficiency. Biological processes supplythe remainder and in some cases contribute up to80 per cent of crop nitrogen uptake (Angus 2001).Although direct uptake of ammonium fertilisersby plants can occur most nitrogen fertilisersapplied in an ammonium (NH 4 +) form areconverted to nitrate (NO 3 -) by the <strong>soil</strong> microbesand are then taken-up by plants in this form.In<strong>organic</strong> nitrogen moves readily in <strong>soil</strong> and isrequired in relatively large amounts at critical stages incrop growth such as terminal spikelet, which occursabout eight weeks after sowing, and during grain fill.In wheat, nitrogen deficiency early in the season limitstiller formation and spikelet and floret number, whichin turn reduces yield potential. Later in the seasonnitrogen deficiency can result in smaller or fewer grainand where sufficient moisture during grain filling inlower grain protein.Nitrogen cyclingSoil nitrogen is primarily determined via biologicalprocesses, which are influenced by rate limitingfactors such as <strong>soil</strong> pH, tillage, <strong>soil</strong> moisture andtemperature. Ammonium released from <strong>organic</strong><strong>matter</strong> mineralised by <strong>soil</strong> microbes determinesthe supply (rate and amount) of in<strong>organic</strong> nitrogen.The rate at which nitrogen is immobilised within<strong>soil</strong> microbes and converted to nitrate is directlyproportional to microbial demands for nitrogen(Murphy et al. 2003) and determines the net amount(or surplus) of <strong>soil</strong> nitrogen that becomes available forplant uptake. While both plants and microorganismscan use ammonium a large proportion of it isconverted into nitrate. Once dissolved in solution,nitrate is more readily taken-up by plants, but is alsoeasily leached (see Figure 4.1).Plant-available nitrogen originates from fertiliserinput, nitrogen fixation and mineralisation of <strong>organic</strong><strong>matter</strong>. The fate of mineral nitrogen within the profileis the result of immobilisation, plant uptake, leachingand gaseous losses.