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HONORABLE BOARD OF SUPERVISORS <br /> May 5, 1982 <br /> Page Fourteen <br /> The same principle is true for all the chemical elements <br /> known to man. An excess of any material applied to soil can <br /> be harmful, but with proper soil tests and monitoring, those <br /> levels can be maintained precisely within safe levels. <br /> There are more than 100 chemical elements known today. <br /> Present information indicates the essential need for 16 <br /> elements in plant growth. These are carbon, hydrogen, oxygen, <br /> nitrogen, phosphorus, potassium, calcium, magnesium, sulfur, <br /> boron, chlorine, copper, iron, manganese, molybdenum, and zinc. <br /> Other elements commonly found in plants are aluminum, <br /> arsenic, barium, bromine, cobalt, fluorine, iodine, lithium, <br /> nickel, selenium, silicon, sodium, strontium, titanium, and <br /> vanadium. This is not a complete list since practically <br /> all of the known chenical elements have been found in plant <br /> materials. <br /> Individual waste constituents are the basis for the <br /> overall site design and operation methodology so that each <br /> waste stream must be quantified on an individual parameter <br /> basis. Obviously, regardless of concentration, all compounds <br /> cannot be analyzed for in an industrial waste. This approach <br /> is based on an understanding of which parameters are important <br /> with respect to the soil system receiving the waste, which <br /> components are of particular environmental concern, and the <br /> chemical and manufacturing process inputs and products. <br /> Because of the basic pathways involved in land-based treatment, <br /> mass generation of waste components (lbs/year) is generally <br /> more important than concentration (mg/1) . Therefore , waste <br /> characterization involves obtaining an analysis of a true <br /> composite sample and generation rates that will give the <br /> annual rate of waste component generation from a specific <br /> plant waste stream. <br /> The soil loading capacity determines what waste stream <br /> components can be accomodated in an environmentally acceptable <br /> manner per unit area and per unit time. Calculation categories <br /> for soil assimilative capacity for components of industrial <br /> waste resource recovery residuals are : <br /> 1) Compounds that are biodegradable, such as oils or <br /> specific organics. <br /> 2) Compounds that are relatively immobile and non- <br /> degradative, that are permitted to accumulate in <br /> soil to a predetermined level, such as heavy metals. <br />