Building Soil Organic MatterBuilding Soil Organic MatterBuilding Soil Organic MatterBuilding Soil Organic MatterBuilding Soil Organic Matterwith Organic Amendmentswith Organic Amendmentswith Organic Amendmentswith Organic Amendmentswith Organic AmendmentsA resource for urban and rural gardeners, small farmers,turfgrass managers and large-scale producers

Leslie CooperbandLeslie CooperbandLeslie CooperbandLeslie CooperbandLeslie CooperbandUniversity of Wisconsin-MadisonUniversity of Wisconsin-MadisonUniversity of Wisconsin-MadisonUniversity of Wisconsin-MadisonUniversity of Wisconsin-Madison

Center for Integrated Agricultural SystemsSeptember 16, 2002

AcknowledgementsI would like to thank Dr. Julie Meyer for her major contributions to the organization,

writing and editing of this document. I also want to thank Ruth McNair of the Center forIntegrated Agricultural Systems (CIAS) for her help with layout, design and editing. The

creation and printing of this document was funded by a grant from CIAS.

Leslie CooperbandMadison, WisconsinSeptember 16, 2002

This report was published by the Center for Integrated Agricultural Systems (CIAS), Collegeof Agricultural and Life Sciences, University of Wisconsin-Madison.

For more information about CIAS, or for additional copies, contact:Center for Integrated Agricultural Systems1450 Linden Drive, Madison, WI 53706

Phone: (608) 262-5200Fax: (608) 265-3020

Email: cecarusi@facstaff.wisc.eduWeb: http://www.wisc.edu/cias/

The Center for Integrated Agricultural Systems brings together university faculty, farmers,policy makers, and others to study relationships between farming practices, farm

profitability, the environment, and rural vitality. Located at the University of Wisconsin,CIAS fosters multidisciplinary inquiry and supports a range of research, curriculum, and

program development projects.

Table of ContentsBuilding Soil Organic Matter with Organic Amendments

What is soil organic matter? 1

How does soil organic matter improve soil properties and functions? 2

Building soil organic matter 5

Characteristics of specific organic soil amendments, their productionin Wisconsin, and guidelines for use 6

Animal manures 6

Crop residues, spoiled hay and straw 8

Municipal yard waste 8

Biosolids (sewage sludge) 9

Wastes from dairy, vegetable, fish, meat and poultry processing industries 9

Wastes from paper mills, timber and paper products 10

Peat 11

Compost 11

Summary 12

Resources 13

1

Building Soil Organic Matter with Organic AmendmentsBuilding Soil Organic Matter with Organic AmendmentsBuilding Soil Organic Matter with Organic AmendmentsBuilding Soil Organic Matter with Organic AmendmentsBuilding Soil Organic Matter with Organic AmendmentsA resource for urban and rural gardeners, small farmers, turfgrass managers and large-scale producers

“Soil is a living entity: the crucible of life, a seething foundry in which matter and energy are in constant flux andlife is continually created and destroyed.” — Daniel Hillel, Out of Earth, 1991.

The mineral matter is made of sand, silt and clay sizeparticles—the basic texture of the soil. The soil watercontains dissolved minerals and is the main source ofwater and nutrients for plants. The air in the soil isneeded for plant roots and soil microorganisms toobtain oxygen. Organic matter includes plant and animalmaterials in various stages of decomposition. Somesoil scientists think of living plant roots and soilmicroorganisms as part of the soil organic matter.

Dead animal and plant matter begin to decompose assoon as they are added to the soil. Eathworms, beetles,springtails, and collembola, the macro (large) to meso(medium) fauna, begin to break large pieces of debrisinto smaller pieces. At the same time, the microbialpopulation increases rapidly. The microorganismsconsume the animal and plant remains and then die,adding themselves to the organic matter. Some organicmatter is more readily decomposed than others. Theend product of decomposition is humus—darkbrown or black organic matter that is highly resistant tofurther decomposition.

Most soil organic matter is present near the soil surface,rather than deeper in the soil. Plant roots becomeorganic matter as their cells slough off or as they die.Aboveground parts of the plant that are not harvestedare left on the soil surface when it dies. Earthwormsand insects incorporate the surface residues deeper intothe soil, but the greatest concentration of organicmatter still remains in the top six inches of soil.

Small component, big impact!Small component, big impact!Small component, big impact!Small component, big impact!Small component, big impact!Most Wisconsin soils contain about 1 to 6 percentorganic matter. Despite its small percentage, soilorganic matter is the foundation of a healthy andproductive soil. Fertility, water availability, susceptibilityto erosion, soil compaction and even resistance toinsects and disease all depend on soil organic matter!

Soils will have inherent differences in organic mattercontents depending on the vegetation history andmineral parent materials. For example, the CentralSands Plainfield loamy sand typically contains less than1% organic matter, while a bog soil can have close to

My intention with this bulletin is to give you anappreciation for soil organic matter and what it doesfor the health of your soil and crops. Soil organicmatter is a dynamic property of soil, not a static one.Building soil organic matter is something you can dofor your soil, and the benefits to your soil and thehealth of your plants can’t be overstated! If youfollow practices that build and maintain soil organicmatter, especially through the addition of organicamendments, you will improve the quality of yoursoil, reducing compaction and crusting, and increasingdrainage and water-holding capacity. Plants will behealthier, may yield more, and will be more tolerantof drought, insects and diseases. You may also needless fertilizer because soil organic matter serves as areservoir for plant nutrients. Some gardeners andfarmers incorporate organic amendments into the soilas a way to recycle organic materials—thereby turninga “waste” product into a valuable soil resource. In thisbulletin, you will learn what soil organic matter is,how it functions in the soil and how organic amend-ments can be used to build soil organic matter.

What is soil organic matter?What is soil organic matter?What is soil organic matter?What is soil organic matter?What is soil organic matter?Soil is three-dimensional and highly dynamic. Itcontains abundant plant and animal life. There arefour main components of soil: mineral matter,organic matter, air and water (Fig. 1).

Figure 1. There are four main components of soil.Figure 1. There are four main components of soil.Figure 1. There are four main components of soil.Figure 1. There are four main components of soil.Figure 1. There are four main components of soil.

Organic MatterAirWaterMineral Matter

Active

Recalcitrant

Organic MatterAirWaterMineral Matter

Active

Recalcitrant

10

6

3

Tons

/acr

e O

M

Months after soil incorporation

0 126

Compost

Cover Crop

Figure 2. Composted organic materials decomposeFigure 2. Composted organic materials decomposeFigure 2. Composted organic materials decomposeFigure 2. Composted organic materials decomposeFigure 2. Composted organic materials decomposemore slowly than fresh organic matter because theymore slowly than fresh organic matter because theymore slowly than fresh organic matter because theymore slowly than fresh organic matter because theymore slowly than fresh organic matter because theyhave already undergone a significant amount ofhave already undergone a significant amount ofhave already undergone a significant amount ofhave already undergone a significant amount ofhave already undergone a significant amount ofdecomposition.decomposition.decomposition.decomposition.decomposition.

90% organic matter. The Wisconsin state soil, theAntigo silt loam, contains 1 to 4% organic matter.Crop cultivation, harvesting, erosion, and naturaldecomposition gradually reduce the amount oforganic matter in soils. However, you can maintainand even increase your soil's current organic matterlevel through proper management.

Pools of soil organic matter based onPools of soil organic matter based onPools of soil organic matter based onPools of soil organic matter based onPools of soil organic matter based ondecomposition leveldecomposition leveldecomposition leveldecomposition leveldecomposition levelNot all soil organic matter is created equal. Fruit andvegetable wastes are easily degraded because theycontain mostly simple carbohydrates (sugars andstarches). In contrast, leaves, stems, nutshells, bark andtrees decompose more slowly because they containcellulose, hemicellulose and lignin. The ease withwhich compounds degrade is determined by thecomplexity of the carbon compounds and generallyfollows the order: carbohydrates > hemicellulose >cellulose = chitin > lignin.

In contrast to fresh plant residues, composted organicmaterials decompose slowly when added to soilbecause they have already undergone a significantamount of decomposition during the compostingprocess (Fig. 2).

Thus soil organic matter can be differentiated intopools or fractions based on their availability formicrobial breakdown. The active fraction has thehighest turnover rate: 1 to 2 years. The intermediatepool turns over in two to five years. The recalcitrant orstable pool is well-decomposed organic matter that ischemically or physically resistant to breakdown, takingmore than 10 years (Fig. 3).

Well-decomposed organic matter no longer providesas many nutrients for plants and soil microbes as theactive pool, but it does play important roles in the soil,such as promoting water and nutrient retention, andprevent soil compaction and crusting.

How does soil organic matter improveHow does soil organic matter improveHow does soil organic matter improveHow does soil organic matter improveHow does soil organic matter improvesoil properties and functions?soil properties and functions?soil properties and functions?soil properties and functions?soil properties and functions?Soil organic matter is often viewed as the thread thatlinks the biological, chemical and physical properties ofa soil. It has been associated with numerous soilfunctions like nutrient cycling, water retention anddrainage, erosion control, disease suppression andpollution remediation (Table 1).

2

Figure 3. The different pools of soil organic matterFigure 3. The different pools of soil organic matterFigure 3. The different pools of soil organic matterFigure 3. The different pools of soil organic matterFigure 3. The different pools of soil organic matter(active and recalcitrant) play different roles in soil(active and recalcitrant) play different roles in soil(active and recalcitrant) play different roles in soil(active and recalcitrant) play different roles in soil(active and recalcitrant) play different roles in soilfunction.function.function.function.function.

Recalcitrant orStable SOM

CEC Micro-aggregation

Active SOM Disease suppressionSoil AggregationNutrient supply

Decomposition

Total SOM

TTTTTable 1. How soil organic matter affects soilable 1. How soil organic matter affects soilable 1. How soil organic matter affects soilable 1. How soil organic matter affects soilable 1. How soil organic matter affects soilqualityqualityqualityqualityquality.....

1. Stores and supplies plant nutrients (N P K andmicronutrients; increases cation exchangecapacity.2. Stabilizes and holds soil particles together asaggregates.3. Helps soil to resist compaction, promotes waterinfiltration, and reduces runoff.4. Aids growth of crops by improving the soil'sability to store and transmit air and water, asmeasured by improved porosity; water holdingcapacity, and drought resistance.5. Makes soil more friable and easier to work sothat plant roots can penetrate the soil profile better.6. Provides a source of carbon and energy for soilmicrobes which cycle nutrients and fight plantdiseases.7. Reduces the negative environmental effects ofpesticides, heavy metals and other pollutants bybinding contaminants.

3

Soil fertility and nutrient supplySoil fertility and nutrient supplySoil fertility and nutrient supplySoil fertility and nutrient supplySoil fertility and nutrient supplyPlants obtain essential nutrients from fresh organicresidues as they decompose in soil. The nutrient valueof soil amendments and plant residues can be assessedby analyzing the amount of nitrogen, phosphorus andpotassium (N-P-K) they provide. However, knowingthe total amounts of N, P and K doesn’t tell you howmuch will become available for crop uptake during thegrowing season. Plant available amounts of N, P andK are often estimated as some percentage of the totalN-P-K in the amendment or residue. For example,available N from manure is estimated at 25-40% ofthe total N content (depending on manure type, ageand manure storage practices). Available N fromcompost is estimated at less than 10% of total N,because the composting process stabilizes organic N.

The active fraction of SOM has been most closelyassociated with nutrient supply. However, the stable,recalcitrant soil organic matter pool also improves soilfertility by holding plant nutrients and preventing themfrom leaching into the subsoil out of reach of plantroots. The SOM has a net negative charge and nutrientssuch as calcium, magnesium, potassium and ammo-nium (called cations) have a positive charge. Thecapacity of a soil to hold plant nutrients so that theyare easily released or “exchanged” into the soil solutionis measured by the cation exchange capacity or CEC. SoilCEC is estimated from the sum of exchangeablecations in the soil.

Soil organic matter also binds plant micronutrients likeiron, aluminum, zinc, copper and manganese bychelation—a chemical association of organic matterand micronutrients that keeps the micronutrients in aform available for plant uptake.

Soil pH buffering capacitySoil pH buffering capacitySoil pH buffering capacitySoil pH buffering capacitySoil pH buffering capacityOrganic matter has the ability to moderate majorchanges in the soil pH. Soil pH is a measure of acidityor alkalinity as determined by the amount of positivelycharged hydrogen (H+) ions in the soil solution.Organic matter buffers the soil against major swings inpH by either taking up or releasing H+ into the soilsolution, making the concentration of soil solution H+more constant. The result is a stable pH close to neutralor suitable for the specific crop to be grown.

The blue color in hydrangea flowers is a classic ex-ample of buffering pH with organic matter. The bluecolor results from plants taking up available aluminumfrom the soil under low pH or acid conditions. HighpH or alkaline soils don’t have enough available

aluminum to turn the hydrangea flowers blue, and theirresultant color is either pink or white. When organicmatter is added to alkaline soil, it grabs or chelates thealuminum and pulls it into the soil solution in a formthat hydrangea plants can take it up. And then theirflowers turn blue!

Soil structure and tilthSoil structure and tilthSoil structure and tilthSoil structure and tilthSoil structure and tilthMany people often use soil texture and structureinterchangeably. There is a difference, however. Soiltexture is defined as the proportion of sand, silt andclay size particles. The arrangement of these primary soilparticles into aggregates is the soil structure. Theaggregates are held together chemically and biologicallyby the “glue” of organic matter. (Fig. 4)

When fresh organic matter is added to the soil, soilmicrobes release long-chain sugars or polysaccharidesrelatively quickly. These polysaccharides promoteformation of large or macro-aggregates. As theorganic matter decomposes over the longer term,different sizes of aggregates are formed that areresistant to physical disruption. The number anddiversity of stable soil aggregates are what give a soilan excellent physical structure.

A soil with a good physical structure will have poresand channels of many sizes, from the tiniest channel tolarge spaces that will allow rainfall to penetrate withoutrunning off and taking soil with it. Soil organic matterhelps to form and maintain the air passages andchannels, protecting the soil from compaction.

When a soil has plenty of spaces for air passage, holdswater well without becoming too wet, is not com-pacted, and has a good physical structure for plant

Figure 4. Figure 4. Figure 4. Figure 4. Figure 4. Dairy manure added to a silt loam soilimproves soil structure, especially the formation ofmacro-aggregates.

4

roots to grow and explore, we say it has good soiltilth. Organic matter is one of the key components togood tilth.

Soil organic matter reduces erosionSoil organic matter reduces erosionSoil organic matter reduces erosionSoil organic matter reduces erosionSoil organic matter reduces erosionThe degree of surface soil aggregation will determinehow tightly the soil particles are held during rain orwind storms. Stable soil aggregates resist movementby wind or water because they are larger than primaryparticles of silt or clay. Soil pores created by aggre-gation also promote water infiltration, therebyreducing runoff and the likelihood that soil particleswill be transported with the water.

Crop residues, vegetative cover or mulches on the soilsurface will also slow down water as it impacts thesoil during a rainstorm, giving it a better chance toseep into the soil.

Preventing soil erosion conserves soil fertility becausethe most fertile soil is the top few inches.

SOM supplies carbon and energy to soilSOM supplies carbon and energy to soilSOM supplies carbon and energy to soilSOM supplies carbon and energy to soilSOM supplies carbon and energy to soilmicrobesmicrobesmicrobesmicrobesmicrobesA soil rich in organic matter and regularly suppliedwith different kinds of soil organic matter will supporta rich and varied population of soil organisms. There isa complex food web below ground similar to thefood web above ground.

Organic matter provides a carbon source for primaryproducers like cyanobacteria that can convert atmo-spheric nitrogen to plant available N forms. Organicmatter is the principle food source for secondaryconsumers. The most predominant functional groupof secondary consumers are the decomposers: bacte-ria, fungi and actinomycetes. Decomposers quicklycolonize newly-added organic materials and begin thedecomposition process. It is during this decompositionprocess that nutrients become available to plants,humus is created, and soil-building aggregation andchannels are formed.

A soil populated by a diverse, active microbial popula-tion is less likely to support uncontrolled spread ofplant pathogens (Cook and Baker, 1983). Interactionsbetween beneficial soil organisms and plant pathogenscreate situations in which pathogens are suppressed orinhibited, especially soil-borne pathogens. Some soilmicroorganisms are antagonistic to plant pathogens,creating an unfavorable environment for them to grow.Others compete against pathogens, effectively keepingthe pathogen population in check. There is also

evidence that soil microorganisms can induce the plantitself to fight disease. This phenomenon is calledsystemic acquired resistance (SAR) (Fig. 5).

We are only beginning to appreciate the numerousroles soil organic matter and the associated microor-ganisms play in the productivity and health of soils. Forexample, research studies show that moderate applica-tion rates (5-10 tons/acre) of organic amendments(both raw and composted) can reduce the incidenceand severity of root rot diseases like Pythium.

SOM buffers environmental pollutantsSOM buffers environmental pollutantsSOM buffers environmental pollutantsSOM buffers environmental pollutantsSOM buffers environmental pollutantsJust as soil organic matter buffers the soil from rapidchanges in soil pH, it also binds organic pollutants,keeping them out of the soil solution where theywould be taken up by plants or leached into groundwater. Organic matter also provides sites for microbesto colonize and decompose organic pollutants.

Soil organic matter has been shown to protect plantroots from potentially harmful levels of aluminum,which occur in some acid soils, and also from certainherbicides that are potentially toxic to plants.

SOM sequesters carbon and can mitigateSOM sequesters carbon and can mitigateSOM sequesters carbon and can mitigateSOM sequesters carbon and can mitigateSOM sequesters carbon and can mitigategreenhouse gas emissionsgreenhouse gas emissionsgreenhouse gas emissionsgreenhouse gas emissionsgreenhouse gas emissionsThere is an emerging awareness of global warmingand its connection to human activities that promotegreenhouse gas emissions (carbon dioxide or CO2,methane or CH4, nitrous oxide or N2O). Carbonsequestration or storage in soil is considered a meansto reduce greenhouse gas (CO2 or CH4) emissions.Building and maintain higher soil organic matter levels

Figure 5. How soil microorganisms help prevent plantFigure 5. How soil microorganisms help prevent plantFigure 5. How soil microorganisms help prevent plantFigure 5. How soil microorganisms help prevent plantFigure 5. How soil microorganisms help prevent plantdisease. disease. disease. disease. disease. (Figure courtesy of Dr(Figure courtesy of Dr(Figure courtesy of Dr(Figure courtesy of Dr(Figure courtesy of Dr. . . . . Alex Stone, Alex Stone, Alex Stone, Alex Stone, Alex Stone, Assistant ProfessorAssistant ProfessorAssistant ProfessorAssistant ProfessorAssistant Professor,,,,,Horticulture, Oregon State UniversityHorticulture, Oregon State UniversityHorticulture, Oregon State UniversityHorticulture, Oregon State UniversityHorticulture, Oregon State University, Corvallis, OR), Corvallis, OR), Corvallis, OR), Corvallis, OR), Corvallis, OR)

Effects on the pathogen:ï destruction of the pathogen ï prevention of infection (competition)

How SOM Affects Crop Diseasesï induced resistance to root and foliar diseases

should translate to lower levels of CO2 being givenoff to the atmosphere. Research is underway toquantify the effects of different cropping systems andtillage practices on carbon sequestration.

Building soil organic matterBuilding soil organic matterBuilding soil organic matterBuilding soil organic matterBuilding soil organic matterThe first step in effective management of soil organicmatter is to determine your management goals (Figure6). Do you want to build the amount of soil organicmatter quickly? Do you want to supply nutrients in thefirst year of amendment application? Or is your maingoal to improve the structure of the soil, graduallyover time?

Choose those practices that are most effective inpromoting the goal(s) you have in mind for your soil.Building and maintaining soil organic matter requires asustained effort. But it can be done.

Building soil organic matter with coverBuilding soil organic matter with coverBuilding soil organic matter with coverBuilding soil organic matter with coverBuilding soil organic matter with covercrops and green manurescrops and green manurescrops and green manurescrops and green manurescrops and green manuresCover crops are those crops planted after the main(cash) crop is harvested. Some cover crops are seededover the standing cash crop so they can get a head

start on growth while the cash crop is still in the field.Cover crops are usually killed the following spring,prior to planting the next season’s cash crop.

Planting cover crops or green manures build soilorganic matter in several ways. Both protect the topsoilcompletely and greatly decrease soil erosion by reduc-ing raindrop impact. Cover crops reduce leachinglosses by utilizing excess nutrients, especially nitrogen,after the main crops are harvested (Table 2). Greenmanures are cover crops that are managed to provide

TTTTTable 2. able 2. able 2. able 2. able 2. Ability of cover crops to scavengeAbility of cover crops to scavengeAbility of cover crops to scavengeAbility of cover crops to scavengeAbility of cover crops to scavengenitrogen (N) in the fall.nitrogen (N) in the fall.nitrogen (N) in the fall.nitrogen (N) in the fall.nitrogen (N) in the fall.(Staver and Brinsfield, 1997)

Cover cropCover cropCover cropCover cropCover crop N uptake by DecemberN uptake by DecemberN uptake by DecemberN uptake by DecemberN uptake by December(lb/acre) following corn(lb/acre) following corn(lb/acre) following corn(lb/acre) following corn(lb/acre) following corn

Cereal rye 71Wheat 40Ryegrass 38Brassica (mustard) 35Oats 28Barley 32Legumes (various) 10

5

Figure 6. What is your management goal?Figure 6. What is your management goal?Figure 6. What is your management goal?Figure 6. What is your management goal?Figure 6. What is your management goal?

Goal

Appropriatematerials and

methods

Build SOMquickly

Supply nutrients Improve soilstructure quickly

Use stableorganic

amendmentslike

compost

Apply raw orminimally pro-cessed organicwastes high in

nutrients

ManuresProcessed

wastesBat

guano

Leaves

Plant alegume

cover crop(green

manure)

Add highcarbon,“raw”

wastes

Incorporatecrop residues

Resto-ration

ofgrass-land

Grazeforageratherthan

harvest

Rotationwith highresidue

crop (grassor legume)

Cottonseedmeal

Vegetablewastes

Soybeanmeal

Biological actvity and nutrient supply continua

Biological activity

Nutrient supply

Low High

Low High

compost cover cropsraw wastes

finished compostleaves

manurelegumes

Heavily bed-ded manures

Plant acovercrop

Inter-cropping

Livingmulches

��

��

grass, cover crops

6

nutrients to the next season’s cash crop by killing themwhile they are still green. Usually legumes and othernitrogen-fixing plants such as clover and vetch are usedas green manures for their nitrogen supply (Table 3).Decomposition is rapid and nitrogen is released.Grasses can also make good green manure crops ifthey are killed early.

The extensive root systems of cover crops contributeto the soil organic matter while the crop is still alive.Some cover crops won’t survive a hard frost anddon’t overwinter, such as oats and vetch in Wisconsin.If the cover crop survives the winter, most farmers killthe crop several weeks before the next crop is plantedand till the residues into the soil. As the residuesdecompose, they build SOM.

Building soil organic matter with organicBuilding soil organic matter with organicBuilding soil organic matter with organicBuilding soil organic matter with organicBuilding soil organic matter with organicamendmentsamendmentsamendmentsamendmentsamendmentsThere is no end to the number of possible organicamendments available for your soil. Many are currentlyconsidered “waste” products or by-products fromfarm enterprises, food processors, municipalities orindustry. They can be applied raw or following somekind of processing like anaerobic digestion,composting or drying/pelletizing. Common organicamendments available in Wisconsin include:

1. On-farm wastes: manure, crop residues, spoiledstraw, hay and silage.2. Municipal wastes: yard debris and biosolids (sewagesludge).3. Organic wastes from food processors: vegetable,meat, fish, dairy.4. Organic wastes from paper mills and the timberindustry.5. Post consumer food wastes (restaurants, institutionalcafeterias).

6. Pre-consumer food wastes from grocery stores andsupermarkets7. Composts

Amendment or fertilizer?Amendment or fertilizer?Amendment or fertilizer?Amendment or fertilizer?Amendment or fertilizer?Whether an organic soil amendment can be considereda “fertilizer” or general soil conditioner depends on itseffect on plant nutrition.

Fertilizers are a source of readily available nutrients andhave a direct, short-term effect on plant growth. Soilconditioners affect plant growth indirectly by improv-ing the physical and biological properties of the soil,such as water retention, aeration and microbial activityand diversity.

Animal manures and biosolids (sewage sludge) aregood examples of organic amendments with fertilizervalue. Both can supply N, P and K needs of manycrops because greater than 25% of their total N, P andK contents are in forms readily available for cropuptake. Amendments like municipal yard waste, barkand composts are examples of soil conditioners. Theyare not considered fertilizer substitutes, but mainly theyimprove soil properties by building soil organic matter.

C:N ratioC:N ratioC:N ratioC:N ratioC:N ratioAll organic matter contains some carbon and somenitrogen. The relative amount of each present (thecarbon to nitrogen ratio) will determine whethernitrogen, and sometimes other nutrients, will be tied upin the decomposition process. Decomposition ofmaterials with a low C:N ratio like animal manures(less than about 20:1) will release nitrogen, while thedecomposition of high C:N materials such as straw orsawdust, will require that soil microbes use the amend-ment N for their own metabolic needs.

Table 4 lists some average ratios for common organicby-products. Green materials usually have lower C:Nratios than woody materials or dead leaves. Animalwastes are more N rich than plant wastes.

Characteristics of specific organic soilCharacteristics of specific organic soilCharacteristics of specific organic soilCharacteristics of specific organic soilCharacteristics of specific organic soilamendments, their production inamendments, their production inamendments, their production inamendments, their production inamendments, their production inWisconsin, and guidelines for useWisconsin, and guidelines for useWisconsin, and guidelines for useWisconsin, and guidelines for useWisconsin, and guidelines for use

Animal ManuresAnimal ManuresAnimal ManuresAnimal ManuresAnimal ManuresIn general, raw manures are a good source of N, Pand K as well as organic matter. There are majordifferences in nutrient contents among livestock species

TTTTTable 3. Relative N value of certain cover cropsable 3. Relative N value of certain cover cropsable 3. Relative N value of certain cover cropsable 3. Relative N value of certain cover cropsable 3. Relative N value of certain cover crops(Source: Sarrantonio, 1994.)

LegumeLegumeLegumeLegumeLegume N-fixation capacityN-fixation capacityN-fixation capacityN-fixation capacityN-fixation capacity

Alfalfa HighHairy vetch HighCrimson clover ModerateField peas ModerateWhite or red clover ModerateCommon bean Low

High = greater than 150 lbs. N/acre Moderate = 50 to 150 lbs. N/acre Low = less than 50 lbs. N/acre

7

(Table 5). For example, poultry litter typically hashigher concentrations of N and P compared to dairymanure. Wisconsin is home to close to 2 million dairy

cows. Each full-grown dairy cow produces approxi-mately 80 lbs manure/day; statewide this translates toover 30 million tons of manure produced annually.Most of this manure is spread directly on croplandsassociated with the dairy operations.

Guidelines for useSince manures are most commonly applied to soilsbased on their N contents, application rates can varyfrom 3-5 tons/acre for poultry litter to 25-40 tons/acre for dairy manure. Till fresh manure into the soil inthe late fall or early spring.

Manure can be applied raw or composted.Composting changes the qualities of the manure. Forexample, nutrient availability will be lower aftercomposting. But the composted manure is much morebiologically stable. This means that the effects of theorganic matter will be longer lasting. Compostedmanure is odor, weed and pathogen-free and can bestored for a longer time (Table 6). See The Art andScience of Composting in Resources for details on how tocompost manure.

Precautions in using manureSalts, especially sodium, in raw animal manures can behigh enough to cause problems for plant growth. Ifraw manure is land-applied, it is important to incorpo-rate the manure into the soil to dilute salt concentra-tions. Also, it is best to allow rain or precipitation toleach out some of the salts before you plant. Potassium(K) can build up in surface soils from long-termapplications of manure. This can lead to increasedconcentrations of K in livestock feed, which has beenassociated with some cattle health problems.

Raw manures often contain weed seeds and pathogens.Pathogens found in the animal digestive system willusually not survive in soils, especially if the manure isapplied several months prior to crop planting or

TTTTTable 4. Common organic amendments andable 4. Common organic amendments andable 4. Common organic amendments andable 4. Common organic amendments andable 4. Common organic amendments andtheir C:N ratiostheir C:N ratiostheir C:N ratiostheir C:N ratiostheir C:N ratios(Adapted from various sources, including Rynk, 1992,to illustrate representative values.)

Organic amendmentOrganic amendmentOrganic amendmentOrganic amendmentOrganic amendment C:NC:NC:NC:NC:NHigh in carbonHigh in carbonHigh in carbonHigh in carbonHigh in carbonCorn stalks 60-70Straw 40-150Corn silage 40Fall leaves 30-80Sawdust 200-700Brush, wood chips 100-500Bark (paper mill waste) 100-130Newspaper 400-800Cardboard 500Mixed paper 150-200

High in NitrogenHigh in NitrogenHigh in NitrogenHigh in NitrogenHigh in NitrogenHay 15-30Dairy manure 5-25Poultry manure 5-15Hog manure 10-20Cull potatoes 18Vegetable wastes 10-20Coffee grounds 20Grass clippings 15-25Municipal biosolids 9-25

TTTTTable 6. Qualities of raw and composted manureable 6. Qualities of raw and composted manureable 6. Qualities of raw and composted manureable 6. Qualities of raw and composted manureable 6. Qualities of raw and composted manure

Raw manureRaw manureRaw manureRaw manureRaw manure Composted manureComposted manureComposted manureComposted manureComposted manure

High available nutrients: N,P, K Low available nutrients, esp. N

Heterogeneousóhigh volume Homogeneousólow volume

Very biologically active Biologically stableStrong odor Non-offensive odorWet Moist-dryMay contain weed seeds and Weed seeds andpathogens pathogens killed

TTTTTable 5. Rule of thumb average nutrient contentable 5. Rule of thumb average nutrient contentable 5. Rule of thumb average nutrient contentable 5. Rule of thumb average nutrient contentable 5. Rule of thumb average nutrient contentfrom various solid and liquid manures (notfrom various solid and liquid manures (notfrom various solid and liquid manures (notfrom various solid and liquid manures (notfrom various solid and liquid manures (notcomposted)composted)composted)composted)composted)

TTTTType of Manureype of Manureype of Manureype of Manureype of Manure lbs. per ton (solid)lbs. per ton (solid)lbs. per ton (solid)lbs. per ton (solid)lbs. per ton (solid)lbs. per 1000 gallons (liquid)lbs. per 1000 gallons (liquid)lbs. per 1000 gallons (liquid)lbs. per 1000 gallons (liquid)lbs. per 1000 gallons (liquid)

NNNNN PPPPP222220000055555 KKKKK2222200000

Dairy, solid 10 5 9Beef, solid 14 9 11Swine, solid 14 10 9Duck, solid 17 21 30Chicken, solid 40 50 30Turkey, solid 40 40 30Sheep, solid 26 18 40Horse, solid 10 6 10Dairy, liquid 24 9 20Veal calf, liquid 15 10 25Beef, liquid 20 9 20Swine, liquid indoor pit 50 42 30Swine, liquid outdoor pit 34 16 20Swine, liquid, farrow-nursery indoor pit 25 23 22Poultry, liquid 16 10 12

These data are taken from a combination of Midwest PlanService (2000), manure analysis from Wisconsin certifiedsoil testing laboratories (2002), and University of Wiscon-sin-Extension publications.

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harvesting. If fresh manure is applied to vegetables,apply at least three months before crops are harvested.Weed seeds can survive in manure-amended soils longafter the manure is applied. The types and amount ofweed seeds will depend partly on animal feed sourcesand where manure is stored prior to land spreading.

Farmers applying manures to supply nitrogen (N) areoften applying too much phosphorus (P), becausemanures contain similar amounts of N and P, yet cropsneed about six times more N than P. A long-termconsequence of fertilizing soils with manure is that Pbuilds up in the soil and may be lost in runoff. Oneway to minimize P loss in runoff is to reduce manureapplication rates to supply only the P needs of thecrop. The tradeoff in this approach is the need forsupplemental N from other sources and reducedadditions of organic matter.

Crop residues, spoiled hay and strawCrop residues, spoiled hay and strawCrop residues, spoiled hay and strawCrop residues, spoiled hay and strawCrop residues, spoiled hay and strawThe parts of the plants remaining after you haveharvested the usable portion are called crop residues.They are an important source of organic matter. Itrequires no extra time or labor to grow the material orto leave it in place. Beneath the soil surface, decayingroots are also adding to the soil organic matter.Although crop residues add organic matter, diseasedplant parts left in the field can serve as inoculum thatcould infect the next year’s crops. So it is important toremove diseased plant residues and compost thembefore you return this organic matter to the field.Rotating crops also reduces the transmission of manysoil-borne diseases.

Leave crop residues on the surface to increase soilaggregation and protect the soil surface from crusting.Soil crusts are caused by raindrop impact and freeze-thaw processes that break soil aggregates into fineparticles, creating a seal over the soil surface.

Spoiled hay, straw and silage can be applied to soils asorganic amendments. However, these materials arehigh in carbon and very biologically active. As such,they should be applied in the fall or at least twomonths prior to crop planting to avoid nutrient tie upduring the active phase of their decomposition.

Municipal yard wasteMunicipal yard wasteMunicipal yard wasteMunicipal yard wasteMunicipal yard wasteMunicipal yard waste includes leaves, brush and grassclippings that are collected curbside in most municipali-ties. Fresh yard trimmings can contain 1.2-2.3 % N,0.2-0.3% P, 0.5-1.0 % K, 50-60% organic matter and

pH values between 5-6 (Cogger et al., 2002). Nutrientcontents increase in relation to the proportion of grassclippings in the mix. Wisconsin, like most states in theU.S., has a ban on sending these materials to the landfill.In 2000, Wisconsin recovered and recycled approxi-mately 225,000 tons of yard waste (Goldstein andMadtes, 2001).

Yard wastes are either composted or applied directlyto farmland. Composting municipal yard waste variesfrom intensive, well-managed operations that sell thefinished compost to facilities that occasionally turn pilesand give away the finished product. Low-intensitymanagement of yard waste composts frequently leadsto variable, low quality finished products that oftencontain woody debris, trash and weed seeds (“buyer”beware!).

Guidelines for UseComposted municipal yard waste can used in homegardens, landscape plantings, establishment of turfgrasses and green spaces and for erosion control onsteep hillsides. For most of these applications, it isimportant to use biologically stable, screened finishedcompost. Application rates vary from 1/2 to 3 inchesapplied to the surface of the soil. In most cases, itshould be incorporated into the top 6 inches of thesoil. It can also be used as a mulch for trees and shrubs.

Fresh yard trimmings can be applied to agriculturalfields to build soil organic matter. However, it is bestto apply leaves in the fall to give them ample opportu-nity to break down before the next year’s crop isplanted. In one study (Peterson, 1991) 20-40 tons/acreof leaves were applied to a corn field each fall. Theleaves decomposed in fall and early the next spring,increasing soil organic matter. The high application rateof leaves received supplemental N to lower the C:Nratio of the leaves. All leaf-amended plots and controls( no leaves) produced similar corn yields the followingyear, demonstrating that fall leaf applications minimizethe chances of decomposing leaves robbing N fromthe corn crop.

Experiences with on-farm “leaf mulching” in NewJersey showed that a 3-inch layer of leaves chisel-plowed into the soil surface improved soil aggregationand increased soil water holding capacity (Kluchinski etal., 2002). Crops grown the spring following leafapplication showed reduced drought stress. However,increased soil moisture in the spring prolonged germi-nation of some broadleaf and grass weeds. A 6- inch

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layer of leaves proved to hold too much moisture andtie up too much N, reducing crop yields.

PrecautionsIn general, fresh yard trimmings are more difficult toland spread than composted yard trimmings. Leavesand chipped brush can be difficult to till into the soil.Yard trimmings need to be spread as soon as they aredelivered to minimize odor generation.

Biosolids (sewage sludge)Biosolids (sewage sludge)Biosolids (sewage sludge)Biosolids (sewage sludge)Biosolids (sewage sludge)Biosolids are by-products of municipal wastewaterand sewage treatment. There are several technologiesin use that separate and de-water solids followingaerobic (with oxygen) or anaerobic (in the absence ofoxygen) digestion of municipal sewage. Some waste-water treatment facilities use lime or organic polymersto precipitate and coagulate the solids. Some usewood or coal ashes to chemically stabilize and separatethe solids. Others use belts and presses to squeezeexcess water out of the solids. Digested, dewateredbiosolids commonly contain 3-6%N, 1-4%P, 0.2-1%Kand 50-60% organic matter. Biosolids also contain Ca,Mg and trace metals. Water contents can range from70-95% by weight, depending on the process.

Guidelines for useAt present, there are two classes of biosolids that canbe used in agriculture: class A and class B. The majordifference between the two classes is the acceptablepathogen load. Class A biosolids have lower patho-gen loads than class B; as such, class A are considered“exceptional quality” and can be distributed to thegeneral public for higher value crops like turf, homegardens and vegetable crops.

Direct land application of class B biosolids is regu-lated by the federal government. All municipalitieswith land spreading programs follow strict guidelinesabout which crop fields can receive biosolids andwhat application rates can be used. Typically, biosolidsare applied to meet the nitrogen requirements of thecrops grown (application rates can range from 10-25wet tons/acre). They are most commonly applied tofield crops like corn and soybeans. Municipalities applybiosolids either in the fall (after crop harvest) or inspring (prior to crop planting). In Wisconsin, they arenot allowed to winter spread. Biosolids are eitherinjected below the soil surface as a semisolid orsurface applied and tilled into the top 6” of soil.

There are a growing number of municipalities that areseeking to diversify their land spreading programs to

produce class A biosolids. Heat drying and pelletizingand composting are two accepted technologies used toproduce class A biosolids products.

For example, the city of Milwaukee has been market-ing a fertilizer product called Milorganite for severaldecades. Milorganite is 100% organic activated sewagesludge in a fine granular form. It is heat-treated forsterilization and is inoffensive and easy to handle.Milorganite is high in nitrogen (6-2-0) and a goodsource of iron and trace elements that are slowlyreleased. Milorganite is easy to apply to lawns, plantingbeds or as a soil mix. The turf industry (golf courses,city green spaces) has long recognized the fertilizervalue of this product. Cities in other states have beenproducing biosolids composts for use in potting mixes.

PrecautionsMost of the concerns about biosolids are with class Bmaterials. Potential concerns include the presence ofpathogenic organisms such as bacteria, protozoa andviruses, excess salts, the presence of heavy metals suchas copper, lead, cadmium and the presence of organiccontaminants such as polychlorinated biphenyls (PCBsor dioxins) and “endocrine disrupter” type com-pounds. It is important to note that the concentrationsof heavy metal and organic toxins in biosolids havebeen declining over the past 20 years because thedischarge of sewage contaminated with metals ororganic toxins from industrial sources is no longerallowed.

Alkaline (high) soil pH conditions can result frombiosolids treated with lime, especially in soils with lowpH buffering capacity. As with livestock manures,applications of biosolids to meet N crop needs haveled to buildup of soil P over time. Accordingly,biosolids and manures share similar concerns related tonon-point source pollution of water bodies.

WWWWWastes from dairyastes from dairyastes from dairyastes from dairyastes from dairy, vegetable, fish, meat and, vegetable, fish, meat and, vegetable, fish, meat and, vegetable, fish, meat and, vegetable, fish, meat andpoultry processing industriespoultry processing industriespoultry processing industriespoultry processing industriespoultry processing industriesThe state of Wisconsin is a leading cheese producer inthe U.S. For every one pound of cheese produced,approximately 9 pounds of liquid whey result. TheFood and Drug Administration defines whey as “theliquid substance obtained by separating the coagulumfrom milk, cream, or skim milk in cheese making.”

Wisconsin dairy facilities deal with approximately 19billion pounds of liquid whey by-product every year.Whey by-products are either reused to make otherfood products or spread on land as wastes. In the past,

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raw whey (containing approx. 93% water and 12 lbs.N per 1000 gallons) was separated from waste waterand land-applied to crops as a fertilizer. Today, mostof the material that is land spread is whey permeate(the by-product left after the protein has been re-moved). Whey permeate contains 0.4% solids, 6.5%sodium, 25% potassium and 21% chloride.

Wisconsin is also home to a large fruit and vegetableprocessing industry. All food processing facilities havewaste water discharge permits, and land spreading oftheir solid wastes is part of their strategy to minimizepoint-source pollution of surface waters. Both solidwastes and liquid effluent from canneries and fruitprocessors (e.g. cranberry processors) can be appliedto cropland. Most fruit and vegetable wastes have alow C:N value and will decompose rapidly. This willresult in intense microbial activity and short-termimprovement in soil structure and nutrient levels.However, these wastes have high water contents, andcomposting the vegetable wastes simplifies handlingand spreading of the organic material Compostingwill also produce an amendment that will releasenutrients more slowly and provide organic matter thatis more stable and longer-lasting.

Meat packers and processors, also numerous inWisconsin, produce wastewater treatment residuals(sludges), paunch manure (manure left in the animal gutafter slaughter) and manure collected from the barnsused to house the livestock before storage. Poultryprocessors produce offal (intestines, unwanted animalparts), feathers, wastewater sludge and some manure.Fish processors produce similar waste products likewastewater treatment residuals and unwanted fishparts. Most of these wastes are direct land-spreadunder strict state permit guidelines.

PrecautionsWhey contains milk sugars that are easily degraded,resulting in a very high biological oxygen demand(BOD) when applied to the soil. This can be toxic tocrops if applied shortly before crop planting. If wheyruns off crop fields into streams, the high BOD candeprive oxygen to fish and kill them. Salt accumulationfrom land spreading is a major concern in addition tothe high BOD.

The greatest concern about organic amendments fromthe fish, meat and poultry industries are with odors,excess nutrients and high BOD. Some meat processorssell their wastes to other processors who convert thesematerials into fertilizer products or organic soil amend-

ments such as feather meal and fish emulsion. Therehas been some composting of these types of wastes inWisconsin.

WWWWWastes from paper mills, timber and paperastes from paper mills, timber and paperastes from paper mills, timber and paperastes from paper mills, timber and paperastes from paper mills, timber and paperproductsproductsproductsproductsproductsPaper mill sludge is one of the largest under-utilizedorganic by-products in Wisconsin. Paper mill residualsare either land filled or land spread, but over 60%(740,000 dry tons) are still land filled.

Historically, paper mill wastes contained high levels oforganic contaminants (PCBs, dioxins) and heavy metals.The presence of these contaminants prevented landspreading. However, most paper companies havechanged the way they make paper so that less contami-nated residuals are produced. As land fill optionsdecline for both economic and environmental reasons,the paper industry is shifting focus to beneficial reuse.There are a growing number of paper companies inWisconsin with permitted land spreading programs.

Paper mills that combine primary residuals from thepaper making process itself with the secondarywastewater treatment sludges create sludges with aC:N ratio less than 20:1. This makes them quite suitablefor crop production. The residuals are mostly organicmatter, but also contain calcium carbonate (lime) orclay used as binders and fillers in paper making.Farmers can contact local mills to see if they have aprogram.

Guidelines for useTypical application rates are based on N supply andrange from 5-20 dry tons/acre. Residuals fromdeinking (recycling) mills have much higher C:N ratios(>50:1) and their use for crop production is limited.Paper mill residuals with high C:N ratios should beapplied in fall to allow time for decomposition.

A mill in Northwest Wisconsin has conducted farmtrials using high C:N residuals to control weeds inalfalfa stands. Since alfalfa makes its own nitrogen, itcan grow and out-compete grass and broad-leavedweeds that are deprived of N from the high C:Nresiduals.

Paper mill residuals contain approximately 30% solidsand can be composted with bark, a by-product frompulping, to make a high value soil amendment.Use of paper mill sludge, either raw or composted,holds promise from a soil quality perspective. Incoarse-textured sandy soils, increases in organic matter

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content can quickly improve soil chemical, biologicaland physical properties. Our research has shown thatthat paper mill residuals applied to vegetable fields inthe Central Sands region of Wisconsin increased thewater holding capacity and plant-available water by33%-80% (Foley and Cooperband, 2002). Paper millresiduals also reduced incidence of root rot diseases insnap bean.

Wisconsin supports a strong timber industry, whichgenerates a substantial amount of sawdust throughoutthe state. A survey by the USDA Forest Servicereported sawdust production in Wisconsin of morethan 409,000 and 46,000 fresh tons for hardwood andsoftwood species, respectively. Presently, many of theby-products of the timber industry are used toproduce animal bedding, mulches or biofuels.

Wood ash is another by-product of the timberindustry. Many mills landfill ash generated fromburning wood as a biofuel. However many ashespossess liming value and some fertilizer (P, K, Ca, Mg)value. Application rates from 5-20 dry tons per acrewere shown to increase alfalfa yields (Meyers andKopecky, 1998).

PrecautionsConcerns about use of paper mill residuals in cropproduction relate mostly to the C:N ratio of thematerial and potential presence of organic toxins.There are also concerns about increasing soil pH withlime-containing residuals, especially if fields receiverepeated applications of paper mill residuals. High soilpH has been related to potato scab disease in potatoesgrown on sandy soils.

The greatest concern about direct land spreading ofwood by-products like sawdust and wood chips andincorporation with soil is their very high C:N ratio(often greater than 100:1). This property can result insevere and long-lasting N tie-up in the soil. However,the physical properties and high carbon contents makewood by-products ideally suited to be compostedwith other organic wastes generated in Wisconsin.These include livestock manures and food processingwastes.

PeatPeatPeatPeatPeatPeat is a partly-decomposed plant material that slowlyaccumulates in pond and lake bottoms and swampareas. Sphagnum peat moss is younger and coarserthan muck or sedge peat, which is a fine-textured,more decomposed type of peat.

Peat mosses can hold water and nutrients ten to fifteentimes their own weight when fully saturated, yet still canhold 40% air. They have little nutrient value themselves,but are excellent at holding nutrients to prevent themfrom leaching from the soil or container mix. Peatmoss is the predominant component of commercialpotting mixes.

Issues of concern include the low pH (3.7-4.5) and thefact that peat is a non-renewable resource. Commercialnurseries that depend on peat as a growing medium arefinding that high-quality sources are harder to obtain.Fortunately, composts are being developed to serve aspeat substitutes.

CompostCompostCompostCompostCompostComposting transforms raw organic waste materialsinto biologically stable, humic substances that makeexcellent soil amendments. Compost is easier to handlethan manure and other raw organic materials, storeswell and is odor-free.

Compost has a unique ability to improve the chemical,physical, and biological characteristics of soils. Itimproves water retention in sandy soils and promotessoil structure by increasing the stability of soil aggre-gates. Soil becomes microbially active and moresuppressive to root pathogens. Enhanced microbialactivity also accelerates the breakdown of pesticides.

Compost can be purchased or made at home or on-farm. Common composting materials (called feedstocks)are poultry, hog and cattle manures; food processingwastes; biosolids; leaves, brush and grass clippingscollected by municipalities; and sawdust, wood chipsand bark from wood processing.

Ideally, at least two raw materials should be mixedtogether. Highly biodegradable ingredients such asbiosolids, manure, and yard waste should be incorpo-rated into blends at rates under 15-20%. Blended mixesshould have a C:N ratio between 25-40:1 and moisturecontent around 50%.

See The Art and Science of Composting (Resources) for adetailed discussion about how to compost.

Spent mushroom compostSpent mushroom compost is the organic material thatremains after the mushrooms have been harvested. It isusually a composted mixture of manures and straw.The concerns about use of spent mushroom composteither as a soil amendment or as a component in

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container mixes are quality inconsistency and highsoluble salts.

Guidelines for using compostsCompost makes an excellent medium for growingplants, provided it is a mature compost with character-istics that promote plant growth (Table 7). Nutrientcontent, water holding capacity, bulk density andorganic matter content should all be measured.

• Turf establishment and renovation. Soils low inorganic matter, nutrients and water holding capacitywill benefit greatly from compost addition. Recentresearch has shown that use of high quality compostcan degrade some turf pesticides over time reducingrisks of water contamination. Fine particle size isusually recommended to ensure good seed-to-soilcontact.

• Flower and vegetable beds. Successful recipes forannual and perennial beds include 20-40% compostby volume incorporated into native soil or includedin commercial topsoil mixes. Compost qualityparallels that for container media, soluble salts shouldbe 2.5 dS or less.

• Field nursery production. Growing nursery plantscan result in a tremendous mining of topsoil in just afew years. The conventional practice for buildingorganic matter is planting cover crops. However, thispractice does not build enough organic matter overthe short-term and should be supplemented withannual compost applications. Characteristics ofcompost for field nursery production are similar tothose described for container media, except thatparticle size can be larger (up to 1 inch) and thecompost can be less mature or stable if applied the

fall before planting. Recommended application ratesare 1-3 inches tilled into the top 6 inches of soil.

• Backfill mix. Amending backfill with compostencourages plant establishment and survivability. Itmay also reduce damage from soil-borne diseases.Highly stable composts rich in nitrogen are best.

Precautions for compost useLow application rates are recommended for saltsensitive crops including dogwoods, narrow-leafevergreens and ericaceous crops. Salt damage is morelikely to occur in sandy soils with low organic mattercontents and low cation exchange capacity. You candelay planting until amended soil has received rainfallor irrigation water to leach salts from soil. Solublesalts should not exceed 1.25 dS for seeds, youngseedlings or salt-sensitive crops (e.g. geraniums).

Unfinished composts can contain high ammonium,salts or other phytotoxic compounds. It couldsuppress weeds but also kill desired plants. Someunfinished composts have high C:N ratios, resulting inN tie-up in the soil. Many of these problems can beavoided if unfinished compost is applied to soil atleast one month prior to crop planting.

SummarySummarySummarySummarySummaryNow you know what soil organic matter is, how itbenefits your soil and how you can build it using anarray of organic amendments. Remember to identifyyour goals for building soil organic matter before youchoose a soil amendment. Do you want to build theamount of soil organic matter quickly? Do you wantto supply nutrients in the first year of amendmentapplication? Or is your main goal to improve thestructure of the soil, gradually over time?

Also, test any new soil amendment you plan to use forits chemical, physical and biological properties so youknow how it will affect your soil and crops. Lastly,remember that soil organic matter is a dynamicproperty, and you have the ability to manage it toimprove soil properties and grow healthier plants.

TTTTTable 7. Preferred compost characteristics forable 7. Preferred compost characteristics forable 7. Preferred compost characteristics forable 7. Preferred compost characteristics forable 7. Preferred compost characteristics forgrowing mediagrowing mediagrowing mediagrowing mediagrowing media(From U.S. Composting Councilís Field Guide to Compost Use.)

ParameterParameterParameterParameterParameter VVVVValue Rangealue Rangealue Rangealue Rangealue RangepH 5.5-8.0Moisture content 35-55%Particle size 1/2î screen or smallerStability Stable to highly stable; provide

nutrients for plant growth; nosubstantial shrinkage

Maturity/growth Demonstrated ability to enhancescreening seed germination and plant growthSoluble salt 3 dS (mmhos/cm) or lessconcentration

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ResourcesResourcesResourcesResourcesResources

Bierman, Peter. 2002. Recycling waste products onagricultural land. 4-page Extension Bulletin. Ohio StateUniversity, Piketon Research and Extension Center.www.ag.ohio-state.edu.

Chaney, David, Laurie Drinkwater and G. StuartPettygrove. Organic Soil Amendments and Fertilizers. 1992.UC Sustainable Agriculture Research and EducationProgram #21505. University of California. 36 pp.

Cogger, Craig, Andy Bary and Dan Sullivan. 2002.Fertilizing with yard trimmings. Washington StateUniversity Cooperative Extension “Farming West ofthe Cascades” Series No. EB1926E. 8pp.

Cook, R. James and Kenneth F. Baker. The Nature andPractice of Biological Control of Plant Pathogens. APSPress, 1983.

Cooperband, Leslie. The Art and Science of Composting.2002. Department of Soil Science and Center forIntegrated Agricultural Systems, University of Wiscon-sin-Madison. 14pp.

Foley, BJ and LR Cooperband. 2002. Paper millresiduals and compost effects on soil physical proper-ties in an irrigated vegetable rotation. Journal ofEnvironmental Quality (in press, Nov/Dec. 2002).

Goldstein, Nora and Celeste Madtes. 2001. The stateof garbage in America. Biocycle 42 (12): 42-54.

Gouin, R. Selecting Organic Soil Amendments forLandscapes. University of Maryland College Parkhttp://www.compostingcouncil.org/pdf/ORGANIC_SOIL_AMENDMENTS.pdf

Kelling, K.A. and L.G. Bundy. Optimum Soil Test Levelsfor Wisconsin (A3030). 1999. http://www1.uwex.edu/ces/pubs/pdf/A3030.PDF

Meyer, N. L. and M.J. Kopecky. 1998. Industrial woodash as a soil amendment for crop production. TappiJournal 8 (4):123-130.

Kluchinski, D, J.R. Heckman, J. Ingerson-Mahar and F.Kelley. 2002. On-Farm Leaf Mulching: Effects onSoils, Crop Yield and Pests. Rutgers CooperativeExtension, New Jersey Agricultural ExperimentStation. Extension Publ. No. FS822. 2pp.

Kopecky, M.J., N.L. Meyers and W. Wasko UsingIndustrial Wood Ash as a Soil Amendment. UWExtension A3635 http://extremist.uwex.edu/ces/pubs/pdf/A3635.PDF (.pdf file)

Madison, F., K. Kelling, J. Peterson, T. Daniel, G.Jackson, and L. Massie.1986. Guidelines for ApplyingManure to Pasture and Cropland in Wisconsin A3392. http://www1.uwex.edu/ces/pubs/pdf/A3392.PDF

Magdoff, Fred. Building Soils for Better Crops.Organic Matter Management. 1998. North EastRegion Sustainable Agriculture Research Program.

Peters, J.B. and LG. Bundy. 1997Sampling Soils for Testing (A2100) http://www1.uwex.edu/ces/pubs/pdf/A2100.PDF

Peterson, A.E.1991. Recycling leaves and yard waste: agrowing opportunity. Resource Recycling X(4): 52-57.

Rynk, R. On farm composting handbook, NRAES,Pub. 54, 1992.

Sarrantonio 1994. Northeast cover crop handbook.Rodale Institute Soil Health Series. Emmaus, PA.118pp.

Schulte, E.E. and K.A. Kelling SchulteOrganic Soil Conditioners. 1998. University of Wisconsin-Extension Bulletin #A2305.http://extremist.uwex.edu:80/ces/pubs/pdf/A2305.pdf

The Soil Quality Institutehttp://www.statlab.iastate.edu/survey/SQI/

Staver K. and R. Brinsfield 1997. Using cereal grainwinter cover crops to reduce groundwater nitratecontamination in the mid-Atlantic Coastal Plain. Journalof Soil and Water Conservation 53(3):230-240.

Woolenhaupt, N.C. and J. Pingry. Estimating ResidueUsing the Line Transect Method (A3533) http://www1.uwex.edu/ces/pubs/pdf/A3533.PDF

U.S. Composting Council. 1996 “Field Guide toCompost Use.” 128 pp. can be ordered from theUSCC website: http://www.compostingcouncil.org/index.cfm