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Page Title: Table 1. Maximum Allowable Metal Concentrations in Sludge Amended Soils USEPA 503 Regulations (USEPA 1997)
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ERDC TN-DOER-C12
February 2000
beneficial uses such as manufactured topsoil, engineered soil capping material, building blocks, or
flowable fill. The following discussion will explain how to approach the evaluation of specific
beneficial uses of dredged material.
ENGINEERED PRODUCTS
Manufactured Topsoil: To evaluate the potential for manufactured topsoil in a particular
location, local sources and types of cellulose and biosolids will need to be identified. Cellulose can
be in many forms, such as yard waste, sawdust, wastepaper, storm debris, shredded paper, etc.
Biosolids can be animal manures, such as dairy cow, beef cow, chicken, turkey, or swine manures,
and/or sewage sludge biosolids. The quality, quantity, and availability of these materials must be
determined. Potential markets for the soil products will need to be identified. Potential markets
could include, but not be limited to, landscaping, nurseries, bagged soil products, highway
construction rights-of-way, parks, ball fields, golf courses, etc. Characterization tests of the dredged
material should be conducted in accordance with Winfield and Lee (1999) and Lee (1999).
Screening tests of blends of the dredged material, cellulose, and biosolids should be conducted as
described in Sturgis and Lee (1999).
Results of the characterization and screening tests should be presented to local authorities for their
review, comment, and approval as a potential acceptable product. There are no universal soil
contaminant concentration standards that are acceptable in all situations. A number of states have
or are attempting to establish acceptable contaminant screening levels for soils used for residential
and industrial purposes. The basis for these screening levels varies from state to state. In some
cases, background concentrations of contaminants in local soils
Table 1
are considered, while other screening levels are related to risk
Maximum Allowable
assessments. In either case, local regulatory authorities will
Metal Concentrations in
decide the acceptability of manufactured soil products and their
Sludge Amended Soils
uses for residential, industrial, or any other purposes. The
USEPA 503 Regulations
USEPA has established maximum levels of metals in agricul-
(USEPA 1997)
tural soils receiving biosolids derived from sewage sludge
(Table 1, USEPA 1997). These soil concentrations have been
Concentration
derived from risk assessments of various soil to plant to animal
Metal
ppm
scenarios. It would appear that manufactured topsoil with metal
41
concentrations below those listed in Table 1 could be used for
Cadmium
39
3,000
agriculture, or restoration of abandoned minelands, landfill cov-
Copper
1,500
ers, and Superfund sites that will be developed for wildlife
Lead
300
habitat. Coordination with local entities, such as municipal,
17
Mercury
Nickel
420
county, State, and Federal agencies, that have requirements for
2,800
Zinc
topsoil should be conducted to identify potential markets for
topsoil. A commercialization plan should be developed using
available resource materials. Participants in the development of the commercialization plan will
vary from location to location. Participants can be, but are not limited to, commercial entities
possessing patented technology (such as Recycled Soil Manufacturing Technology) or a properly
licensed commercial entity, sources of available cellulose and biosolids, and other interested entities.
The plan should then be submitted to the appropriate entity(ies) with authority over the dredged
material to be reclaimed.
3

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