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GUIDE TO THE LITERATURE
LABORATORY TESTING OF CCB MATERIALS
(Updated 10/15/98)

OUTLINE


ENGINEERING CHARACTERISTICS RELATED TO PRODUCT USE

ASTM Specifications Pertaining to Coal Ash (Fly Ash or Bottom Ash): Report provided by the American Coal Ash Association ACAA.

LEACHING TESTS

Leaching Tests: Commonly Used Methods, Examples of Applications to Coal Combustion By-Products, and needs for the next generation. Sorini. 1996.


ABSTRACTS and LOCATION

ACAA. ASTM Specifications Pertaining to Coal Ash (Fly Ash and Bottom Ash)

FOR USE AS CONCRETE

C14/C14M-95: Standard Specification for Concrete Sewer, Storm Drain, and Culvert Pipe. ASTM Vol. 4.05.

C227-90: Standard Test Method for Potential Alkali Reactivity of Cement-Aggregate Combinations (Mortar-Bar Method) ASTM Vol. 4.02.

C311-97: Standard Test Methods for Sampling and Testing Fly Ash or Natural Pozzolans for Use as a Mineral Admixture in Portland Cement Concrete. ASTM Vol. 4.02.

C330-89: Standard Specification for Lightweight Aggregates for Structural Concrete. Includes aggregates prepared by expanding, pelletizing, or sintering products such as blast furnace slag, clay, diatomite, fly ash, or slate. ASTM Vol. 4.02.

C331-94: Standard Specification for Lightweight Aggregates for Concrete Manonry Units. Includes aggregates prepared by expanding coal fly ash; from end products of coal combustion such as bottom ash; by crushing or pelletizing cementitious mortars manufactured by various processes that mix materials such as portland cement, lime, coal fly ash, and chemical admixtures. ASTM Vol. 4.02.

C332-91: Standard Specification for Lightweight Aggregates for Insulating Concrete. Intended for use in concrete not exposed to weather. Includes aggregates prepared by expanding, calcining, or sintering products such as blast furnace slag, clay, diatomite, fly ash, shale, or slate. ASTM Vol. 4.02.

C441-89: Standard Test Method for Effectiveness of Mineral Admixture of Ground Blast Furnace Slag in Preventing Excessive Expansion of Concrete Due to the Alkali-Silica Reaction. ASTM Vol. 4.02.

C593-95: Standard Specificiation for Fly Ash and Pozzolans for Use with Lime. Covers fly ash and other pozzolans for use with lime in plastic mortars, non plastic mixtures, and other mixtures that affect lime pozzolanic reaction. Evaluation of Class C fly ash containing available lime is given consideration. ASTM Vol. 4.01.

C595/C595M-95a: Standard Specification for Blended Hydraulic Cements. Covers five classes of blended hydraulic cements using slag, pozzolan, or both, with portland cement portland cement clinker, or slag with lime. ASTM Vol. 4.01.

C618-97: Standard Specification for Coal Fly Ash or Calcined Natural Pozzolan for Use as a Mineral Admixture in Portland Cement Concretes. Covers fly ash where cementitous or pozzolanic action or both is desired. ASTM Vol. 4.02.

C938-91: Standard Practice for Proportioning Grout Mixtures for Preplaced Aggregate Concrete. The cementitious material shall consist of two parts of portland cement to one part of pozzolan, by weight. ASTM Vol. 4.02.

C1141-94: Standard Specification for Admixtures for Shotcrete. Pozzolanic admixtures shall be sampled and tested in accordance with the requirements established in C311. ASTM Vol. 4.02.

C1157/C1157M-95: Standard Performance Specification for Blended Hydraulic Cement. A specification giving performance requirements. There are no restrictions on the composition of the cement or its constituents. ASTM Vol. 4.01.

C1260-94: Standard Test Method for Potential Alkali Reactivity of Aggregates (Mortar-Bar Method). Permits detection within 16 days. ASTM Vol. 4.02.

D5370-96: New Standard Specification for Pozzolanic Blended Material in Construction Applications. Covers pozzolanic blended material consisting of an intimate unIAOrm blend of Class F and Class C fly ashes, or a blend of Class F fly ash with cement kiln dust. ASTM Committee D34. ASTM Vol. 11.04.


FOR USE WITH BITUMINOUS PAVING MIXTURES

D242-89: Standard Specification for Mineral Filler for Bituminous Paving Mixtures. Mineral filler shall consist of finely divided mineral matter such as rock dust, slag dust, hydrated lime, hydraulic cement, fly ash, or loess. ASTM Vol. 4.03.



FOR USE AS CONTROLLED LOW STRENGTH MATERIAL (CLSM)

D4832-95: Standard Test Method for Preparation and Testing of Controlled Low Strength Material (CLSM) Test Cylinders. ASTM Vol. 4.09.

D5971-96: Standard Practice for Sampling Freshly Mixed CLSM. This practice includes sampling from revolving drum truck mixers and from agitating equipment used to transport centrally mixed CLSM. ASTM Vol. 4.09.

D6023-96: Standard Test Method for Unit Weight, Yield, and Air Content (gravimetric) of CLSM. This test method covers determination of the weight per cubic foot (cubic meter) of freshly mixed CLSM and gives formulas for calculating the yield, cement content, and air content of the CLSM. The method is based on Test Method C138 for Concrete. ASTM Vol. 4.09.

D6024-96: Standard Test Method for the Ball Drop on CLSM to Determine Suitability for Load Application. This specification covers the determination of the ability of CLSM to withstand loading by repeatedly dropping a metal weight onto the in-place material. ASTM Vol. 4.09.

D6103-97: Standard Test Method for Flow Consistency of CLSM. This covers the porcedure for determination of the flow consistency of fresh CLSM containing aggregate not larger than 3/4 inch (19.0mm). ASTM Vol. 4.09.


FOR USE IN STRUCTURAL FILLS

E1266-88: Standard Practice for Processing Mixtures of Lime, Fly Ash, and Heavy Metal Wastes in Structural Fills and Other Construction Applications. This practice provides descriptions and references of existing test methods and commercial practices relating to the processing of lime, fly ash, and heavy metal wastes in construction applications. ASTM Vol. 11.04.

E1861-97: Standard Guide for Use of Coal Combustion Fly Ash in Structural Fills. This guide covers the design and construction of engineered structural fills using coal combustion fly ash. The guide suggests procedures for consideration of engineering, economic, and environmental factors in the development of fly ash structural fills. ASTM Vol. 11.04.


FOR USE AS A SOIL AMENDMENT

D5239-92: Standard Practice for Characterizing Fly Ash for Use in Soil Stabilization. Covers procedures for characterizing fly ash to be used in soil stabilization. ASTM Vol. 4.09.

D5434-93: Standard Test Method for Diagnostic Soil Test for Plant Growth and Food Chain Protection. Covers the determination of quantity (Q) and intensity (I) results for several elements in soils, spoils, fly ash, and other soil substitutes to ascertain their suitability for the growth of vegetation and possible adverse effects for metals on the food chain. ASTM Vol. 4.09.

Ordering Info: American Coal Ash Association, 2760 Eisenhower Ave., Suite 304, Alexandria, VA 22134-4553, (703) 317-2400, FAX (703) 317-2409, Website www.acaa-usa.org/pubs/publist.htm



FOR DISPOSAL IN A LAND FILL

D 422: Grain Size Distribution

D 2216: Moisture Content

D 854: Specific Gravity

D 698, D 1557: Density

D 2166, D 3080, D 2435: Shear Strength

D 2435: Compressibility

D 2434: Permeability

D 2325: Capillarity

D 560: Frost Susceptibility

Sorini. S.S. 1996. Leaching Tests: Commonly Used Methods, Examples of Applications to Coal Combustion By-Products, and Needs for the Next Generation. In Chugh Y. P. et al. Proceedings of Coal Combustion By-Products Associated with Coal Mining - Interactive Forum. Southern Illinois University at Carbondale. p 3-11.

There are a variety of tests available for characterizing the leaching behavior of waste materials. These vary in test type, leaching aspects that are addressed, and the particular use for which the test is designed. Types of leaching tests include agitated extraction tests, serial batch tests, flow-through tests, flow-around tests, etc. These tests address different aspects of leaching, such as the physical mechanisms involved, chemical interactions between the waste and the leaching fluid, the kinetics of leaching, leaching as a function of time, etc. Some of the uses of leaching tests include regulatory purposes, scientific research, and environmental assessment. This paper discusses some of the commonly used leaching methods, results of specific application of some of these to coal combustion by-products, and what is needed for the next generation of test methods to more accurately assess the release of contaminants into the environment.

COMMONLY USED LEACHING PROCEDURES

EPA METHODS

Toxicity Characteristic Leaching procedure (TCLP) (US EPA Method 1311): The TCLP (US EPA 1990) is designed to simulate the leaching a waste will undergo if disposed in an unlined sanitary landfill. It is based on a co-disposal scenario of 95% municipal waste and 5 % industrial waste. The method is an agitated extraction test using leaching fluid that is a function of the alkalinity of the solid phase of the waste. Either a sodium acetate buffer solution having a pH of 4.93 ± 0.05 or an acetic acid solution having a pH of 2.88 ± 0.05 is uses. The procedure requires particle size reduction to less than 9.5 mm. The TCLP is designed to determine the mobility of 40 Toxicity Characteristic (TC) constituents in liquid, solid and multi phasic wastes. The TC constituents include both inorganic and organic species. Teachability of volatile organic compounds is determined using a zero-head space extractor and the sodium acetate buffer solution. The TCLP was developed in 1984 under the Hazardous and Solid Waste Amendments to the Resource Conservation and Recovery Act (RCRA) (1984) and is the US EPA regulatory method for classifying wastes as hazardous or nonhazardous based on toxicity. If the TCLP extract contains any one of the TC constituents in an amount equal to or greater than the concentrations specified in 40 CFR 261.24 (1992), the waste possesses the characteristic of toxicity and is a hazardous waste.

Synthetic Precipitation Leaching Procedure (SPLP) (US EPA Method 1312): The SPLP (US EPA 1990), which is an agitated extraction method, was developed in 1988 by the US EPA for use in evaluating the impact that contaminated soils may have on groundwater. The procedure calls for use of simulated acid rain or reagent water was the extraction fluid, depending on the constituents of interest. The extraction fluid used to determine the teachability of soil from a site that is east of the Mississippi River is a solution of sulfuric and nitric acids in reagent water having a pH of 4.2 ± 0.05. This extraction fluid is also used to extract waste or wastewater using the procedure. The extraction fluid used to determine the teachability of soil from a site that is west of the Mississippi River is a solution of sulfuric and nitric acids in reagent water having a pH of 5.0 ± 0.05. When the teachability of volatile organic compounds or cyanide is being evaluated, reagent water is used as the extraction fluid. The procedure requires particle size reduction to less than 9.5 mm, and as with the TCLP, extraction for volatile constituents is performed in a zero-head space extractor.

Multiple Extraction Procedure (MEP) (US EPA Method 1320): The MEP (US EPA 1990) is designed to simulate the leaching a waste will undergo from repeated precipitation of acid rain on an improperly designed sanitary landfill. The repetition extraction are to reveal the highest concentration of each constituent that is likely to leach in a natural landfill. The MEP is a serial batch test in which the first extraction is performed according to the Extraction Procedure (EP) Toxicity Test (US EPA 1990). The EP is the US EPA regulatory method that was replaced by the TCLP for determining the characteristic of toxicity. It is a leaching procedure that involves monitoring the pH of the waste in reagent water and using an acetic acid solution to maintain the pH of the slurry at 5.0 ± 0.2. After the first extraction in the MEP is completed, the remaining solid is re-extracted nine times (or more) using synthetic acid rain as the leaching fluid. If the concentration of any constituent of concern increases from the 7th or 8th extraction to the 9th extraction, the procedure is repeated until the concentrations decrease. The synthetic acid rain leaching fluid is prepared by adding the appropriate amount of 60/40 weight percent sulfuric acid and nitric acid mixture to distilled, deionized water to give pH of 3.0 ± 0.2. The method is applicable to liquid, solid, and multi phasic materials.

AMERICAN STANDARD TEST METHODS (ASTM)

ASTM Method D-3987, Standard Test Method for Shake Extraction of Solid Waste with Water (ASTM 1995): This method is a procedure for rapidly generating a leachate from solid waste that can be used to estimate the mobility of inorganic constituents from the waste under the specified test conditions. The final pH of the leachate is to reflect the interaction of the leaching fluid with the buffering capacity of the waste. In the method, it is stated that the procedure is not intended to produce a leachate representative of leachate generated in the field, and the method does not simulate site-specific leaching conditions (ASTM 1995). ASTM Method D-3987 is an agitated extraction method that uses reagent water as the leaching fluid. The procedure involves an 18-hour contact time between a solid waste and reagent water with rotary agitation. The method calls for testing a representative sample of the waste, and as a result, it does not require particle size reduction. The method has been tested to determine its applicability to inorganic constituents, but it has not been tested for application to organic constituents.

ASTM Method D-4793, Standard Test Method for Sequential Batch Extraction of Waste with Water (ASTM 1995): This method is a procedure for obtaining serial leachates of a waste that can be used to estimate the mobility of inorganic constituents from the waste under the specified test conditions. The final pH of the leachate is intended to reflect the interaction of the leaching fluid with the buffering capacity of the waste. Similar to ASTM Method D-3987, this method also contains statements that it is not intended to produce leachates representative of leachate generated in the field, and that it does not simulate site-specific conditions. ASTM Method D-4793 is a serial batch test that uses reagent water as the leaching fluid. The method has been tested for its applicability to inorganic constituents only and can be used to test any waste containing at least 5 percent solids. The leaching steps are repeated so that 10 leachates are generated.

ASTM Method D-5284, Standard Test Method for Sequential Batch Extraction of Waste with Acidic Extraction Fluid (ASTM 1995): This method is a modification of ASTM D-4793. It calls for use of a leaching fluid having a pH that reflects the pH of acidic precipitation in the geographic region in which the waste being tested is to be disposed. The leaching fluid is prepared by mixing a 60/40 weight percent mixture of sulfuric acid/nitric acid with water. This method has only been tested for its use in leaching inorganic constituents. The information given in the method concerning its intent and limitations is the same as described above for ASTM Method D-4793.

ASTM Method D-4874, Standard Test Method for Leaching Solid Waste in a Column Apparatus (ASTM 1995): This is a column method using reagent water in a continuous up-flow mode to generate aqueous leachate from waste materials. The current published version of the method is applicable for evaluating the leach ability of inorganic constituents. However, a revised method will be published in 1996 that can be used to evaluate the leach ability of semivolatile and nonvolatile organic compounds, as well as inorganic constituents. The column method is intended to provide aqueous leaching in a dynamic partitioning manner. It is written so that many of the specific column operating conditions can be selected by the user to meet their specific objectives. The method states that analysis of the column effluent can provide information on the leaching characteristics of the waste under the testing conditions used. It is also stated that the method is not intended to produce results to be used as the sole basis for: (1) the engineering design of a landfill disposal site, or (2) classification of wastes based on leaching characteristics.

Ordering Info: Kimery Vories, Office of Surface Mining, 501 Belle St., Alton, IL 62002.
Interlibrary Loan Request: Debbie McGinnis, Office of Surface Mining, 1999 Broadway, Denver, CO 80202-5733, (303) 844-1436, FAX (303) 844-1545

 



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 Last modified: February 25, 2008