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Old 04-12-2007, 03:09 AM   #31
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Hi all, came acroos this little goodie. Enjoy.

Building Soil For Better Crops. 2nd Edition. Complete book (4.1mb PDF)
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Old 07-19-2007, 08:44 AM   #32
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Mary Jane Soil Quality Terms
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The National Resources Conservation Services has a cool glossary that might be of some use here if you want to dive into the terms used in our hobby also. I thought I'd snag it and drop it over here for the GC.com family


Jah Bless
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It is important to have access to the terms used in soil quality work. Below are two glossaries that can be helpful:

Soil Quality Terms (including soil properties, soil quality indicators, and assessment terminology)

Soil Ecology Terms (including soil organisms, biological processes, and ecology terminology)

The Soil Science Society of America, Madison WI maintains an Internet Glossary of Soil Science Terms.


Soil Quality Terms



Aggregate Stability: The ability of soil aggregates to resist degradation. An aggregate is many soil particles held together in a small mass. In a “well-aggregated soil” the aggregates and pores between them hold up well to forces such as rain, wind, and compaction. (Compare to slake test.)

Amoozemeter: A tool that uses a constant head of water to measure the rate of water movement in a saturated soil, and thus estimates saturated hydraulic conductivity.

Anthropogenic: Generated by humans. Used to indicate soil conditions, disturbances, or stresses that are created by people.

Assessing Soil Quality: Estimating the functional capacity of soil by comparing a soil to a standard such as an ecological site description, a similar soil under native vegetation, a reference soil condition, or quality criteria. The objective of the assessment dictates the standard to be used. (Compare to monitoring.)

Attributes of Soil Change: Quantifiable properties used to describe the nature of soil change, including drivers, types, rates, reversibility, and pathways of change.

Baseline: The initial soil condition before monitoring soil quality over time. Subsequent measurements on the same soil are compared to the baseline measurement.

Benchmark Soil: A benchmark soil is one of large extent, holds a key position in the soil classification system, or is of special significance to farming, engineering, forestry, livestock production, or other uses. The purpose of benchmark soils is to focus data collection and research efforts on soils that have the greatest potential for expansion of data and interpretations.

Bulk Density (Db or BD): The density of soil, i.e., the weight of soil divided by its volume. The BD of agricultural soils normally ranges from 1.0 to 1.6 g/cm3.

Cation Exchange Capacity (CEC): The capacity of soil to hold nutrients for plant use. Specifically, CEC is the amount of negative charges available on clay and humus to hold positively charged ions. Effective cation exchange capacity (ECEC) is reported for acid soils (pH<5). Expressed as centimoles of charge per kilogram of soil (cmolc/kg).

Cotton Strip Assay: Measures the amount of biological activity as determined by the degree of degradation of a standardized strip of cotton buried in the soil.

Disturbance: An event or its change in intensity or frequency which alters the structure or functional status of an ecosystem. Examples of disturbances that can affect soil include drought, fire, harvest, tillage, compaction, overgrazing, or addition of pesticides.

Dynamic Soil Properties: Soil properties that change over the human time scale in response to anthropogenic (management, land use) and non-anthropogenic (natural disturbances and cycles) factors. Many are important for characterizing soil functions and ecological processes and for predicting soil behavior on human time scales. (Compare to use-dependent soil properties.)

Electrical Conductivity (EC): How well the soil conducts an electrical charge. EC is a measure of salinity, generally expressed as decisiemens per meter at 25ºC (dS/m).

Fatty Acid Analysis: Examination of the fatty acid methyl esters (FAMEs) in the soil using gas chromatography. Fatty acids are within the cell walls of soil organisms, so the types of fatty acids found in soil are an indicator of the structure and diversity of the soil community.

Function: A service, role, or task that meets objectives for sustaining life and fulfilling humanity’s needs and is performed by soil or an ecosystem. (Compare to soil function.)

Functional Capacity: The quantified or estimated measure of physical and biophysical mechanisms or processes selected to represent the soil’s ability to carry out the function.

Human Time Scale: That portion of the pedogenic time scale that covers periods of centuries, decades, or less.

Hydraulic Conductivity (Ksat): A quantitative measure of how easily water flows through soil. (Compare to infiltration and permeability.).

Indicator of Soil Quality: A quantitative or qualitative measure used to estimate soil functional capacity. Indicators should be adequately sensitive to change, accurately reflect the processes or biophysical mechanisms relevant to the function of interest,, and be cost effective and relatively easy and practical to measure. Soil quality indicators are often categorized into biological, chemical, and physical indicators.

Indicators of Soil Quality, Biological: Measures of living organisms or their activity used as indicators of soil quality. Measuring soil organisms can be done in three general ways: 1) counting soil organisms or measuring microbial biomass, 2) measuring their activity (e.g. soil basal respiration, cotton strip assay, or potentially mineralizable nitrogen), or 3) measuring diversity, such as diversity of functions (e.g., biolog plates) or diversity of chemical structure (e.g. cell components, fatty acids, or DNA). Each approach provides different information.

Indicators of Soil Quality, Chemical: These include tests of organic matter, pH, electrical conductivity, heavy metals, cation exchange capacity, and others.

Indicators of Soil Quality, Physical: Physical characteristics that vary with management include bulk density, aggregate stability, infiltration, hydraulic conductivity, and penetration resistance.

Infiltration Rate: The rate at which water enters soil. (Compare to hydraulic conductivity.)

Inventory: The systematic acquisition of resource information needed for planning and management.

Microbial Biomass: The total amount of organisms in the soil, excluding macrofauna and plant roots. Microbial biomass is typically determined through substrate-induced respiration, or fumigation-extraction methods.

Minimum Data Set (MDS): The smallest set of soil properties that can be used to characterize or measure soil quality. The MDS will vary based on the intended land use, soil type, and climate. The first MDS was suggested by Larson and Pierce and included the following: nutrient availability, total organic C, particle size or texture, labile organic C, plant-available water capacity, soil structure, soil strength, maximum rooting depth, pH, and electrical conductivity.

Monitoring Soil Quality: Tracking trends in quantitative indicators or the functional capacity of the soil in order to determine the success of management practices or the need for additional management changes. Monitoring involves the orderly collection, analysis, and interpretation of data from the same locations over time. (compare to assessing.)

Organic Matter: Any material that is part of or originated from living organisms. Includes soil organic matter, plant residue, mulch, compost, and other materials.

Soil Organic Matter (SOM): The total organic matter in the soil. It can be divided into three general pools: living biomass of microorganisms, fresh and partially decomposed residues (the active fraction), and the well-decomposed and highly stable organic material. Surface litter is generally not included as part of soil organic matter.

Organic Matter, Active Fraction: The highly dynamic or labile portion of soil organic matter that is readily available to soil organisms. May also include the living biomass. Particulate organic matter (POM) and light fraction (LF) are measurable indicators of the active fraction. POM particles are larger than other SOM and can be separated from soil by sieving. LF particles are lighter than other SOM and can be separated from soil by centrifugation.

Organic Matter, Stabilized Organic Matter: The pool of soil organic matter that is resistant to biological degradation because it is either physically or chemically inaccessible to microbial activity. These compounds are created through a combination of biological activity and chemical reactions in the soil. Humus is usually a synonym for stabilized organic matter, but is sometimes used to refer to all soil organic matter.

Pedotransfer Function (PTF): A mathematical relationship between two or more soil properties that shows a reasonably high level of statistical confidence. PTF’s are used to predict difficult-to-measure soil properties from readily obtained properties of the same soil.

Penetration Resistance or Penetrability: The ease with which a probe can be pushed into the soil.

Permeability: The qualitative estimate of the ease with which fluids, gases, or plant roots pass through soil.

Pitfall Trap: A small container (trap) buried so the rim is at the level of the soil surface. It is used to catch soil arthropods that move across the ground surface.

Porosity: The volume of pores in a soil sample divided by the bulk volume of the sample. Air-filled porosity is the fraction of the bulk volume of soil that is filled with air at any given time or under a given condition, such as a specified soil-water content.

Potentially Mineralizable Nitrogen (PMN): A test measuring the amount of soil organic nitrogen converted to plant available forms under specific conditions of temperature, moisture, aeration, and time. It is a measure of biological activity and indicates the amount of N that is relatively rapidly available.

Primary Ecological Processes: Ecological processes including the water cycle (the capture, storage and redistribution of precipitation), energy flow (conversion of sunlight to plant and animal matter), and the nutrient cycle (the cycle of nutrients such as nitrogen and phosphorus through the physical and biotic components of the environment).

Processes: Physical, chemical and biological mechanisms that follow fundamental scientific laws. Examples include pedogenic processes, geomorphic processes, and ecological processes.

Reference Soil Condition: The condition of the soil to which functional capacity is compared. . Soil quality is usually assessed by comparing a soil to a reference condition. The reference condition may be data from a comparable benchmark soil, baseline measurements taken previously on the same soil, or measurements from a similar soil under undisturbed vegetation, or under similar management.

Scoring Function: A standardization procedure used to convert measured values or subjective ratings to unitless values usually between 0 and 1. This allows all soil property measurements to be integrated into one value or index for soil quality.

The four general types of scoring functions used in soil quality assessments are:

- more is better (higher measurements mean higher soil quality, e.g. SOM)
- less is better (lower measurements mean higher soil quality, e.g. salinity)
- optimum range (a moderate range of values is desirable, e.g. pH)
- undesirable range (a specific range of values is undesirable)

Slake Test: A measure of disintegration of soil aggregates when exposed to rapid wetting.

Soil Change: Temporal variation in soil at various time scales at a specific location.

Soil Function: Any service, role, or task that soil performs, especially: 1) sustaining biological activity, diversity, and productivity; 2) regulating and partitioning water and solute flow; 3) filtering, buffering, degrading, and detoxifying potential pollutants; 4) storing and cycling nutrients; and 5) providing support for buildings and other structures and to protect archaeological treasures. (Compare to function, functional capacity.)

Soil Quality or Soil Health: The capacity of a specific kind of soil to function, within natural or managed ecosystem boundaries, to sustain plant and animal productivity, maintain or enhance water and air quality, and support human health and habitation. In short, the capacity of the soil to function. There are two aspects of the definition: inherent soil quality and dynamic soil quality.
(Compare to functional capacity.)

Soil Quality, dynamic: That aspect of soil quality relating to soil properties that change as a result of soil use and management or over the human time scale.

Soil Quality, inherent: That aspect of soil quality relating to a soil’s natural composition and properties as influenced by the factors and processes of soil formation, in the absence of human impacts.

Soil Resilience: The capacity of a soil to recover its functional capacity after a disturbance.

Soil Resistance: The capacity of the soil to maintain its functional capacity through a disturbance.

Soil Respiration: The amount of carbon dioxide given off by living organisms and roots in the soil.

Soil Respiration, basal: The level of carbon dioxide given off by a soil sample. Basal respiration is a measure of the total biological activity of microorganisms, macroorganisms, and roots.

Soil Respiration, substrate-induced: A measure of the carbon dioxide given off by a soil sample after adding sugar or other food. It is used to estimate microbial biomass in the sample.

Soil Structure: The arrangement of soil particles into aggregates which form structural units. Size, shape, and distinctness are used to describe soil structure. Farmers often describe soil structure with words such as crumbly or cloddy.

Tilth: The overall physical character of soil with regard to its suitability for crop production.

Use-Dependant or Management-Dependent Properties: Soil properties that show change and respond to use and management of the soil, such as soil organic matter levels and aggregate stability. This is a narrower term than dynamic soil properties which encompasses all changes on the human time scale including those induced by natural disturbances or cycles.

Use-Invariant Properties: Soil properties that show little change over time and are not affected by use and management of the soil, such as mineralogy and particle size distribution.

Water Holding Capacity: The amount of water that can be held in soil against the pull of gravity.

Available Water Capacity (AWC): Loosely, the amount of water available for plants to use. Specifically, the volume of water released from soil between the time the soil is at field capacity (the maximum water held in soil against the pull of gravity) until the time it is at the wilting point (the amount of water held too tightly in soil for commonly grown crops to extract). Loamy soils and soils high in organic matter have the highest AWC.
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Old 07-19-2007, 09:27 AM   #33
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Soil Ecology Terms



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David Sylvia at Penn State University maintains a glossary of Soil Microbiology Terms that you may wish to consult.


Actinomycetes: A large group of bacteria that grow in long filaments that are too small to see without magnification. Actinomycetes generate the smell of “healthy soil,” and are important in decomposing cellulose, chitin, and other hard-to-decompose compounds, especially at higher pH levels. Many produce antibiotics.

Aerobic: With oxygen. Aerobic organisms, including animals and most soil organisms, require environments with oxygen. See anaerobic.

Algae: Non-vascular photosynthetic plant-like organisms, some of which live in or on the soil. They are informally divided into groups by their dominant pigments (i.e., green, blue-green, etc.)

Anaerobic: Without oxygen. Anaerobic organisms, including some soil bacteria, need oxygen-free environments such as saturated soils. Facultative anaerobes can function as either aerobes or anaerobes depending on environmental conditions. See aerobic.

AM (arbuscular mycorrhizae): The group of endomycorrhizal fungi important in non-woody plants, including many agricultural crops. Sometimes called vesicular-arbuscular mycorrhizae (VAM).

Arthropods: Invertebrate animals with jointed legs. They include insects, crustaceans, sowbugs, springtails, arachnids (spiders), and others.

Bacteria: Microscopic, single-celled organisms. They include the photosynthetic cyanobacteria (formerly called blue-green algae), and actinomycetes (filamentous bacteria that give healthy soil its characteristic smell).

Bacterial-Dominated Food Web: A soil food web in which the ratio of fungal biomass to bacterial biomass is less than one.

Biological Soil Crust: Also called microbiotic, microphytic, cryptobiotic or cryptogamic crusts. A living community of bacteria, microfungi, cyanobacteria, green algae, mosses, liverworts, and lichens that grow on or just below the soil surface. Biological crusts can heavily influence the morphology of the soil surface, stabilize soil, fix carbon and nitrogen, and can either increase or decrease infiltration. The percent cover and the components of the crust can vary across short distances. Identification of biological crust organisms is simplified through the use of three broad morphological groups: The cyanobacteria group includes cyanobacteria and green algae. The moss group includes short and tall mosses, but not club moss mats, such as those in northern latitudes, or spike moss. The lichen group includes crustose, gelatinous, squamulose, foliose, and fruiticose lichen, as well as liverworts.

Comminuters: Organisms that shred organic material into smaller pieces.

Compost Tea: An infusion made by leaching water through compost, sometimes with nutrients added, such as molasses and kelp, to encourage certain organisms. Soluble organic matter and the organisms in the compost are rinsed out of the solid phase and left suspended in the water. This "liquid compost" is easier to apply than solid compost.

Cyanobacteria: Filamentous or single-celled bacteria that fix carbon and nitrogen (formerly called blue-green algae). Only the filamentous species can be seen without a microscope. Cyanobacterial crusts with low biomass are generally the color of the soil and those with high biomass and diversity are dark (brown to black)

Decomposition: The biochemical breakdown of organic matter into organic compounds and nutrients, and ultimately into its original components.

Denitrification: A process performed by a few species of anaerobic soil bacteria in which nitrite or nitrate is converted to nitrogen gas (N2) or nitrous oxide (N2O). Both N2 and N2O are volatile and lost to the atmosphere.

Detritivores: Organisms that eat detritus, that is, dead plants and animals.

Diversity: Biological diversity can refer to the number of species in an area, the number of types of species (e.g. microbial functional groups, or plant structural types), the degree of genetic variability within a species, or the distribution of species within an area.

Ectomycorrhizal Fungi: A type of mycorrhizal fungi that grows between root cells and forms a sheath around roots, but does not actually invade cells. They are important to many woody plants.

Emergent Properties: Properties of a whole system that are not apparent from examining properties of the components of the system.

Endomycorrhizal Fungi: A type of mycorrhizal fungi that invades the cells of plant roots.

Exudates: Soluble sugars, amino acids and other compounds secreted by roots.

Food Web, Soil: The interconnected community of organisms living all or part of their lives in the soil.
functional redundancy
The presence of several species that serve similar functions (e.g. nitrification).

Fungal-Dominated Food Web: A soil food web in which the ratio of fungal biomass to bacterial biomass is greater than one.

Fungi: Multi-celled, non-photosynthetic organisms that are neither plants nor animals. Fungal cells form long chains called hyphae and may form fruiting bodies such as mold or mushrooms to disperse spores. Some fungi such as yeast are single-celled.

Fungivores : Organisms that eat fungi.

Generalist: A species that will eat or prey on a wide variety of food resources. (See specialist)

Grazers: Organisms such as protozoa and nematodes that eat bacteria and fungi.

Habitat: The environment where an animal, plant, or microbe lives and grows.

Hyphae: Long chains of cells formed by fungi usually occurring between aggregates rather than within micropores. (Compare to mycelium.)

Immobilization: The conversion by soil organisms of inorganic nutrients such as ammonium or nitrate into organic compounds that are part of their cells. This makes the nutrients temporarily immobile in the soil and unavailable to plants. (See mineralization.)

Keystone Species: A species which, if removed from an ecosystem, causes a dramatic change in the system, and which has been proposed as an indicator of the functional capacity of the system.

Lichen: A composite of fungi and algae or cyanobacteria. The fungi capture and cultivate photosynthetic organisms which together provide themselves needed water and nutrients. Lichen species occur in many colors including black, brown, dark olive green, red, yellow and white.

Lignin: A hard-to-degrade compound that is part of the structure of older or woody plants. The carbon rings in lignin can be degraded by a few fungi.

Liverworts: Small non-vascular plants.

Metabolic Quotient (qCO2): The ratio of microbial activity to microbial biomass.

Microbe or Microorganism: An imprecise term referring to any organism too small to see with the naked eye. Generally, “microbes” refers to bacteria, fungi, and sometimes protozoa.

Mineralization: The conversion of organic compounds into inorganic, plant-available compounds such as ammonium. This is accomplished by soil organisms as they consume organic matter and excrete wastes. (See immobilization.)

Moss: Photosynthetic plants with small leaves that unfurl when moistened (thus the moss appears to swell). When dry, mosses are dark and dull-colored; when moistened, the color changes markedly to a bright, light green to brown. This makes them easy to distinguish from lichens.

Mutualists: Two species that have evolved together into a mutually beneficial relationship. For example, mycorrhizal fungi get carbon compounds from plant roots and help deliver water and nutrients to the root.

Mycelium: A bundle of fungal hyphae that form the vegetative body of many fungal organisms.

Mycorrhizal Associations: A symbiotic association of certain fungi with roots. The fungi receive energy and nutrients from the plant. The plant receives improved access to water and some nutrients. Except for brassicas (mustard, broccoli, canola) and chenopods (beets, lamb’s-quarters, chard, spinach), most plants form mycorrhizal associations.

Nematodes: Tiny, usually microscopic, unsegmented worms. Some are parasites of animals or plants. Most live free in the soil.

Nitrification: A process accomplished by a few groups of aerobic organisms in which ammonia is converted to nitrite and then nitrate.

Population: All the individuals of a species in a given area.

Protozoa: Single-celled organisms with animal-like cells, including amoeba, ciliates, and flaggelates.

Rhizine: Root-like structure of lichen and other organisms.

Rhizoid: Root-like structure of mosses and ferns used to attach to a substrate.

Rhizosphere: The narrow region around roots where most soil biological activity occurs. Soil organisms take advantage of the sloughed and dead root cells and the root exudates found in this region.

Saprophytic Fungi: Fungi that decompose dead organic matter.

Sheath: Tubular structure formed around a chain of cells or around a bundle of filaments. The fine, polysaccharide sheaths formed by some filamentous cyanobacteria help bind soil particles together and can be seen dangling from soil surface fragments. Ectomycorrhizal fungi form a sheath of hyphae around plant roots.

Soil Ecology:
The study of interrelations among soil organisms and between organisms and the soil environment.

Specialist: A species that consumes only one or a few types of food sources or forms associations with a narrow range of hosts. For example, certain collembola (tiny insects called springtails) specialize in eating specific species of fungi. (See generalist)

Trophic Levels: Levels of the food chain. The first trophic level includes photosynthesizers that get energy from the sun. Organisms that eat photosynthesizers make up the second trophic level. Third trophic level organisms eat those in the second level, and so on. It is a simplified way of thinking of the food web. In fact, some organisms eat members of several trophic levels.
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Old 07-21-2007, 11:06 AM   #34
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This maybe a little location soecific. Anyway some good principles to follow.

US based links at the bottom of page.

Beating Pests with Biology - By Helen McKerral

Biological Pest Control is a commonsense, long-term method of minimising pests. Helen McKerral untangles the ecology for home gardeners.

Natural Balancing Acts

In their country of origin, plants, animals and insects have evolved over millions of years to balance each other’s populations. Insects evolved to feed on particular plants, or parts of plants, and then other insects evolved to feed on the insects feeding on the plants. If the plant becomes more prolific, the added food supply for the leaf-eating insect (pest or prey) increases their population as well. So the extra insects eat the extra plants, reducing their abundance to "normal" levels.

At the same time, with the extra prey insects as food, the predator insect population has risen as well, reducing the numbers of prey insect after a short lag.

In their home environment, therefore, and without outside intervention, abnormal events or chemicals, plant and insect populations remain in balance, with the abundance of plants, prey and predator insects fluctuating constantly but marginally, keeping each other in check and preventing excessive peaks in population.

The following links indicate the natural predator-prey fluctuation (don’t worry about the math, just scroll down to the graphs)

Predation
The dynamics of biological exploitation

Upsetting the Balance

What happens when we take something out of the equation? Move a plant to an environment without bringing along the insect that feeds upon it, for example? Or transporting the insect and plant, without bringing along the insect’s predator? Or having all present, but spraying a chemical to kill the pest insect? Clearly, there are several potential scenarios.


In Australia

Although Australia is known for some of the greatest successes in biological pest control, it also has the dubious distinction of having some of the worst failures. First, a success.

Prickly pear (Opuntia stricta) was first recorded as introduced in the early 1800s as stock feed and a hedging and garden plant, but it spread incredibly quickly, covering 25 million ha by 1925 in NSW and Queensland. Paddocks were overrun with prickly pear; with no room for stock or crops, numerous farmers were driven off their land. Parliaments passed Control Acts, poisons and physical methods of control were tried to no avail. And then, in 1926, Cactoblastis caterpillars, which feed on prickly pear, were introduced after rigorous testing to ensure they would not attack other plants. In just six years, most of the impenetrable stands of pear were gone, and farmers restocked their land. The Cactoblastis caterpillar in Australia is still considered one of the most successful examples of biological control in the world.

For an example of biological control gone wrong, we only need look at the cane toad, which was introduced in 1935 to eat the cane beetles that damaged sugar cane crops. Unfortunately, the toads ate everything but the beetles and, without natural predators or diseases in Australia to control their own population, they thrived; we all know what has happened since then.


Other combinations

So biological controls may be insect predators to control plants (Cactoblastis), insect predators or parasites to control insect pests (parasitic wasps on aphids, nematodes on millipedes, predator mites against red spider mite), viruses or diseases (pathogens) to control pest plants (eg. rust on blackberry, bacteria on caterpillars) or pest animals (myxomatosis, calicivirus for rabbits). Because biological controls are living populations, they are unlike chemicals, which need to be repeatedly reapplied over a wide area. Instead, the biological control population will spread and increase – and then decrease – in response to the pest population (remember those graphs?). In fact, a single release of a biological control agent in one place can spread throughout an entire pest population, throughout the country.


In the Home Garden

Most of the insect pests in our gardens can be controlled via biological means, and organic, permaculture, sustainable and biodynamic principles to varying degrees all encourage the development of a more natural, balanced ecosystem within the garden. Your patience, and NOT SPRAYING insecticides, are essential for success. Remembering those graphs, you know that in a healthy garden, predator populations build up after a short lag time to control pests – but not if you go spraying the pest first!

Although organic pesticides are regularly promoted as less toxic than chemical ones, in the context of establishing biological control, both are equally damaging as they severely disrupt the natural predator-prey response cycle. In fact, biological controls often require a few years and the sacrifice of a few blooms for predator populations to build and, during this time, you’ll need to resist the temptation to spray even heavily pest-infested plants, for it is these that will provide prey for control insects.

Systemic pesticides such as Confidor, which are consumed only by insects feeding on the plant, still upset the prey-predator cycle. Start spraying, and you are stuck with spraying.

At Jurlique’s Ngeringa Farm, no chemical sprays have been used by them at all. At Urrbrae, no pesticides – organic or chemical – have been sprayed on the roses for more than a decade. Instead, biological controls, such as the predatory wasp Aphidius rosae, have been introduced. The complete absence of pesticides has allowed large predator populations of wasps, ladybirds, spiders, hoverflies and lacewings to become firmly established, and this permanent foundation ensures their numbers soar correspondingly quickly in response to aphid explosions, reducing pest numbers before they can cause serious damage.

Although predator insects will gradually build up in your garden over time, you can speed the process by purchasing them to control everything from aphids, mealybugs, two-spotted mites, codling moth, whitefly and more:

Click here for info on available predator insects

And of course Dipel, whose active ingredient is Bacillus thuringiensis, a bacteria that attacks caterpillars, has long been available to control caterpillars on crops. "Integrated Pest Management" in plant nurseries, greenhouses, and in broadscale farming nowadays often includes biological control principles.

Fortunately, unlike monoculture crops or broadscale farming, home gardens can tolerate a much higher level of pests, and home gardeners can afford a few years of higher pest numbers, without losing our income as predators establish. The old spray-everything-in-sight philosophy has long gone, with gardeners today knowing that a sterile garden equates to an unnatural and unhealthy one. The plethora of organic products and options in gardening stores is testament to that increased knowledge; biological control of garden pests is one further step in the right direction.
________________________________

Linkage:

Pest Control Tactics

Biological Control Information Centre

Approaches to biological control of insects

History of biological pest control

Natural enemies and biological control
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Old 07-25-2007, 07:18 PM   #35
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Roles of Mycorrhizas



Try this link for a very decent read
The Roles of mycorrhizas

Jah Bless
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Old 07-25-2007, 08:15 PM   #36
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Quote:
Try this link for a very decent read
The Roles of mycorrhizas
Nice find Pro!

CSIRO is a wealth of information.
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Old 08-04-2007, 01:21 AM   #37
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Long Brewing Compost Tea
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From Soil Foodweb Institute - Australia

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In this case, the red line is oxygen concentration in the water (in ppm or mg oxygen per L of water), and the green line is the active biology in the tea (micrograms of active bacteria and active fungi per ml of tea). When the organisms are growing the most rapidly, activity peaks (after about 16 hours in most brewers, although about hour 8 in small brewers).

The reason for the peak is that the microorganisms have maximized use of foods, and after that peak, their activity slows down, because they are running out of food. Activity usually stabilizes about 24 hours, so it is safe to take the tea out of the max aeration brewer and put it into a sprayer tank that has just re-circulation.

If the aeration is turned off, it typically takes some time for the organisms to use up the air, and plunge into anaerobic conditions. A truly stable tea would only slowly use up oxygen and go anaerobic, usually in about 5 to 6 hours. But if the tea is not in a stable condition, then when aeration is turned off, oxygen levels will plunge within mere minutes to low, anaerobic levels.




3c. Long-Brewing Compost Tea

Compost teas that start aerobic, move into the anaerobic ranges, and because they are brewed long enough, return to aerobic fall into this category. They contain aerobic bacteria, and put-to-sleep anaerobic bacteria. Beneficial fungi, protozoa and nematodes have been pretty much destroyed by the anaerobic phase, although if the brew didn’t actually go anaerobic, then the beneficials may still be present.

These brews may contain some remnant anaerobic smells and materials. The diversity of food resources has clearly been increased, but the question remains what bacteria exactly were grown? Beneficials, or detrimentals? Disease-suppressors, or disease?

Disease-causing organisms often prefer, and grow better, in reduced oxygen condition. But if the brew went quite anaerobic, then the diseases were killed too. How low is low enough? When do the “bad guys” die, and when do the really bad guys, like Clostridium botulinum, start to grow? We don’t know.

What mix of foods results in the fermentative bacteria or fungi winning, versus the human pathogens? Is stirring vigorously at 12, or 16 hours going to select for the good guys enough to maintain the good guys? Or do you need to stir at 8, 12 and 24 hours? No one really knows. (If you do, please let me know, I’d like to see your data).

Most Biodynamic brews fit this LBCT definition, except Biodynamic preps do not always use compost. The preparations are plant teas, which means plant material is placed into water, stirred and the biology on the leaf surfaces grows using the sugars, proteins, carbohydrates, cellulose, and more recalcitrant (hard-to-decompose, quite complex and thus hard to attack) kinds of substrates.

Does that mean plant teas have no benefit? Of course NOT. If beneficial organisms are on the plant surfaces (and usually roots are included in the plant teas), the beneficial organisms will grow and increase in numbers or biomass during the brew cycle. Which good guys? It depends on the same factors as actively aerated compost depends – temperature, mixing, aeration, foods added, the age and stage of the plant (and therefore the actual foods added), etc.

But, in these LBCTs, no aeration other than occasional stirring is added. That means, if there are organisms present on the plant material, or in the compost if this is truly compost tea, the brew is very likely to go anaerobic for some period of time.

But for how long? And how low did oxygen go? And when did the growing organisms begin to run out of food, so that their oxygen use rate slowed? When did their metabolism slow down enough that oxygen began to diffuse back into the water faster than the organisms were using the oxygen?

By the end of a LBCT brew, the tea should no longer stink in any way, which means the tea has returned to the aerobic condition. The things that may kill your plant have been re-cycled back into bacteria biomass. Sorry, no fungi left in a brew that went anaerobic. The beneficial fungi are, for the most part, aerobic.

The time, or the conditions to allow conversion from aerobic to anaerobic and back again are not documented at all for these kinds of teas. That means that sometimes positive effects have been observed using these kinds of teas, but other times the teas have had no observable effect, and sometimes these teas kill plants. I’ve killed quite a number of plants using anaerobically produced tea, and while I have not published this data (it is hard to publish negative results), lack of publication does not mean it doesn’t happen.

That is why compost tea has been regarded as witchcraft, or voo-doo, or snake oil for all these years. The results have been too variable to make sense of what is going on. When sometimes great results occur, sometimes nothing, and sometimes really bad things happen, no one is inclined to put much trust in the results.

But, the Biodynamic approach controls many of the factors involved in tea making, IF THE PRACTIONER PAYS ATTENTION TO WHAT STEINER SAID. I’ve watched a number of biodynamic brews being made where part, or just about all of Steiner’s advice was ignored. If people don’t understand WHY something was required by science, they may ignore it. But then typically the results aren’t what you would want, or they do not give you the benefit you should be able to get.

The bottom line is, we need to put more effort into understanding these types of tea. But for now, until the work is done, either do what Steiner said, exactly, or use AACT. We are really getting a handle on how to guarantee that AACT is consistent, and beneficial, each time. Without an oxygen probe, and the time to monitor properly, FCT and LBCT remain of questionable benefit.

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Old 08-23-2007, 07:37 PM   #38
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Hen Manure
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Thanks for all the usefull info Profound. Thats an aweful lot of time and research you must have put into this.
I've recently found interest in trialing granulated Hen manure. Due to its high amount of Calcium it seems to give plants a very strong stem and an overall healthy plant. However it is very, very high in toxicity so I wouldn't want to risk to much.
I've been using soil and organic ferts. with Mychorize now for two years and was going to put in my two but the last article definitely covered it.
Cheers all
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Old 08-30-2007, 07:57 PM   #39
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Something dug up from way back.
Organic was showing the way to those interested
....I bumped Organic's thread too

enjoy....
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Quote:
Originally Posted by organic View Post
<sings> something like a recipe....bits and pieces and bits and pieces make Worm Science!

Chet: Yer stewed, buttwad!

Yes, maybe so, but I know about worms!

Here are some exceprts from a mysterious photocopied article I stumbled across recently:

Excerpts: "Earthworm composts as plant growth media"
(source unknown)

Characteristics of plant growth media produced by earthworms from organic wastes

The final physical structure of the plant growth media or vermicomposts produced from organic wastes depends very much on the original material from which they were produced. . .However, the final product is still usually a finely divided peat-like material with excellent structure, porosity, aeration, drainage and moisture-holding capacity. It has the appearance and many of the characteristics of peat.

The nutrient content of a vermicompost differs greatly, depending on the parent material. However when the nutrient content is compared with that of a commercial plant growth medium to which inorganic nutrients have been added, it usually contains more of most mineral elements, although there is often a deficiency of magnesium. An important feature is that during the processing of the wastes by earthworms, many of the nutrients they contain are changed to forms more readily taken up by plants, such as nitrate or ammonium, nitrogen, exchangeable phosphorus and soluble potassium, calcium and magnesium. Moreover, many organic wastes tend to be on the alkaline side of neutral whereas most plants prefer a growth medium on the acid side of neutral (e.g. with a pH of 6.0). The processing by earthworms does not change the pH of the material appreciably, so for ideal plant growth, worm-worked wastes benefit from some acidification or by mixing with an acid medium such as peat.

Growth of plants in worm-worked organic wastes

Handreck (1986) reviewed the utilization of vermicomposts as horticultural potting media. He concluded that they could supply most of the trace element needs of plants, but many vermicomposts may not have sufficient nitrogen to supply all the needs of the plants. However, it seems difficult to justify this conclusion since many organic wastes have excess amounts of nutrients and only a small proportion is lost during vermicomposting.

Growth has usually been better than in recommended commercial growing media, such as Levington compost, and seed germination has been found to be more rapid for most species of plant in worm-worked wastes. . .A wide range of tests of seedling emergence of pea, lettuce, wheat, cabbage, tomato and radish were made in small pots and trays using the standard EEC recommended seedling emergence test. The emergence of tomatoes, cabbage and radish seedlings tended to be as good, and usually better, in worm-worked animal wastes than in a commercial plant growth medium, and much better than in composted animal wastes with no earthworms. Similarly, the early growth of seedlings of ornamentals up to the stage when they were transplanted into larger pots or outdoors, was as good or better in the worm-worked animal wastes mixed with peat as in a commercial plant growth medium.

Some of the ornamentals, particularly chrysanthemums, salvias and petunias, flowered much earlier in worm-worked waste mixtures, and this could possibly be due to a hormonal effect resulting from microbial action. A number of other species of plants followed significantly different growth patterns in vermicomposts, another indication of a possible hormonal effect.

The effects of dilution of worm-worked animal wastes, with a commercial plant growth medium, on growth of ornamentals at a range of levels were quite dramatic (Scott 1988). . .The most surprising result was that addition of even 5% of worm-worked animal waste to the worm-worked waste/commercial medium mixture produced a significant improvement in the growth of the plants. . .These results, where a small amount of worm-worked waste has a significant effect, indicate that the response is not based only on nutrient content.

Thus, although much more research is needed, there is evidence that good worm-worked organic wastes, mixed with peat and other materials, make excellent growth media for a variety of purposes.

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Old 08-31-2007, 02:55 PM   #40
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Here's a page titled

Soil Biology Movies
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