Table 4.
Waste by-product category and amendment |
Source | Availability and general costs |
Metal uptake | Benefits of using | Limitations and unintended consequences |
Targeted metal(s) | |
---|---|---|---|---|---|---|---|
Organic | Digestates (from anaerobic digester) | Anaerobic digestion of organic wastes (e.g., biosolids) | • Availability dependent on the location of anaerobic digesters | Presumed to be similar to biosolids due to the high organic matter content–sorption, complexation of the metal fractions associated with organic matter, metal oxides, or carbonates53 | • High nutrient content | • Relatively new material and not well characterized; may contain metals | No studies were identified through the literature review that specifically investigated immobilization of metals in soil or sediment |
• Relatively new product, and costs are undetermined | • Source of OM | • Not regulated | |||||
• Not routinely treated for pathogen reduction, although digestion temperatures are adequate to kill off pathogens | |||||||
• Potential odor issues | |||||||
• Possible leaching of phosphorous (P) | |||||||
Organic | Biochar (also charcoal and activated C) | Pyrolysis or gasification of biomass (e.g., wood, straw, and tree bark) | Approximately 20+ biochar manufacturers across the United States162 | Adsorption due to large surface areas | • High surface area and cation exchange capacity (CEC); most effective for organic compounds | • Low-temperature pyrolyzed biochars may degrade quickly and remobilize any sorbed metals | As, cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), lead (Pb), and zinc (Zn) |
• C-rich | • Application of biochar increases OM and may either increase or decrease dissolved organic carbon (DOC); if it increases DOC, metals may mobilize (e.g., arsenic [As]) | ||||||
• Attracts microbes and beneficial fungi | |||||||
• Has a long life in soils compared to fertilizers | |||||||
Organic | Rice residues biochar (e.g., hulls/husks, straw, bran) | By-product from rice processing | • Major rice-producing states are Arkansas, California, Louisiana, Mississippi, Missouri, and Texas163 | • Adsorption | • Husks have low solubility in water, good chemical stability, and structural strength as a result of a high silica content | See Biochar | Pb, Cd, Zn, Ni, and As |
• More than 19 billion pounds of rice are produced, but the amount of wastes generated were not determined | • Complexes and chelates are formed | • See Biochar | |||||
Red gypsum (or titano-gypsum) | Titanium dioxide (TiO2) production (pigment industry) | Of 142,000 metric tons (MT) of raw material processed, 70,000 MT of red gypsum produced | Adsorption | • Rich in iron (Fe) oxides | Some variability exists due to raw material properties | As, Cu, Pb, Cd, Zn, and Ni | |
• Useful as a soil amendment | |||||||
Organic and liming/alkaline | Alperujo | Olive oil extraction processes | • Olive oil is produced in California, Arizona, Texas, Georgia, Florida, Oregon, and Hawaii164 | Free ions can complex and co-mobilize with organic ligands during leaching events due to the addition of OM | • Addition of organic matter and potassium (K) | • Not widely available in the United States | As, Cd, Cu, Pb, Zn, and Mn |
• Annual amount of waste generated was not determined | • Provides nutrients (C, nitrogen [N], and P) | • May mobilize As in multicontaminant sites as a result of increases in soil pH | |||||
• Lower levels of metals than biosolids or municipal solid waste (MSW) compost | |||||||
• Slow release of nutrients as evidenced by low mineralization rate165 | |||||||
Organic | Spent mushroom substrate (compost) | Mushroom crops | Approximately an equal ratio of spent mushroom substrate is generated per weight of mushrooms ready for consumption | Adsorption | • Addition of nutrients and OM | • May require additional processing after composting to obtain the desired and most effective particle size | Cd, Pb, Cr, and As |
• High pH buffering capacity due to the addition of lime during composting of the substrate | • Competing uses (e.g., crop production, reuse in the cultivation of mushrooms, animal and fish feed, pest management) | ||||||
• Generates relatively high volumes of waste | |||||||
Organic | Silkworm excrement | Silkworm culture | • China leads the world production; approximately seven companies in the United States operate silkworm farms166 | Sorption | Addition of nutrients and organic matter | Unknown at this time | Cd and Pb |
• Information was not obtained regarding annual quantities of excrement generated or cost | |||||||
Organic | Vermicompost | Vermicomposting of various organic wastes such as vegetable or food waste using worms | • Large quantities available near large-scale vermicom-posting facilities | Adsorption by negatively charged functional groups | • Produces nutrient-rich humus | Potential metal contamination depending on feedstock (e.g., pig manure, sewage sludge, fly ash, and cow dung) | Cd, Pb, Zn, and Cu |
• Relatively low cost | • Addition of nutrients and organic matter | ||||||
Organic | Palm oil waste by-products (e.g., palm kernel pie, boiler ash, empty fruit bunches) | Palm oil manufacturing | Palm oil by-products are not available in the United States; would need to be sourced internationally | Adsorption | Fertilizer | Unknown at this time | Cd and Zn |
Organic and liming/alkaline | Sugarcane filter cake | Residue from sugarcane juice filtration | • Sugarcane is produced in Florida, Louisiana, Hawaii, and Texas, with Florida producing the most167 | Adsorption | • Addition of P and organic matter | Unknown at this time | Cd and Zn |
• By-products are generally free | • Use of by-products would offset effects from field burning (where applicable) | ||||||
Organic and liming/alkaline | Bagasse | By-product after crushing sugarcane or sorghum stalks to extract their juice | • See Sugarcane filter cake | Adsorption | Use of by-products would offset effects from field burning (where applicable) | • Potential for fugitive dust | Cd and Zn |
• Used as a fuel source for sugar mills, so its availability for other uses is limited | • Unpredictability in annual generation due to weather and economics | ||||||
Organic and liming/alkaline | Sugar foam (SF) | By-product from sugar manufacturing | See sugarcane filter cake | • Adsorption | • Addition of CaCO3 | • Potential for fugitive dust | As, Cd, thallium (Tl), Zn, Mn, Cu, aluminum (Al), and Fe |
• Formation of Al-hydroxy polymers | • Can increase pH | • Unpredictability in annual generation due to weather and economics | |||||
Organic and liming/alkaline | Sugar beet lime | Spent lime from the purification of sugar from sugar beets or sugarcane (lime is added to neutralize organic acids present in the plant material) | • Grown in 5 regions encompassing 11 states, primarily in the western United States167 | • Adsorption | • Increases pH | • Potential for fugitive dust | Cu, Zn, Pb, and Cd |
• By-products are generally free | • Chelation, complexation with carboxyl groups | • High calcium (Ca), magnesium (Mg), and K | • Relatively high water content, which affects transportation costs | ||||
• Can contain organic matter | • Unpredictability in annual generation due to weather and economics | ||||||
• Fine particle size | |||||||
Liming/alkaline | Wood ash | Wood-fired utilities | • Available in small to moderate amounts from wood-fired utilities | Sorption | • Increases pH | • Highly variable content | No studies were identified through the literature review that specifically investigated the immobilization of metals in soil or sediment |
• Materials are generally free | • Source of Ca, Mg, and K | • May contain contaminants if other fuels (e.g., tires or waste oil) are co-combusted | |||||
• May have dioxin and should be confirmed through testing | |||||||
• Lime equivalent will vary by burn temperature and age of material | |||||||
Liming/alkaline | Seashell grit | Seafood processing | Available near coastlines with fishing or seafood processing operations; low costs | Adsorption | • pH increase and addition of Ca | None identified | As, Cu, and Zn |
• Used in horticulture and poultry industry | |||||||
Odor? | |||||||
Liming/alkaline | Chitin, chitosan (as found in the exoskeletons of shellfish and crustaceans, as well as lobster, mushrooms, and bacteria) | Seafood processing | • Seasonally available near coastlines with fishing or seafood processing (canning) industries | Adsorption | • Source of Ca from CaCO3 | None identified | Al, As, Cd, Cr, Cu, Fe, mercury (Hg), manganese (Mn), Ni, and Zn |
• Presumed low costs | • Slow release of N, P, and Mg | ||||||
• May contain some K and chitin | |||||||
• Second most abundant natural biopolymer (after cellulose) and can be assumed to be of plentiful supply | |||||||
Odor | |||||||
Mineral/inorganic | Hydroxyapatite (phosphate in the form of apatite from fish bones) | Seafood processing | Available near coastlines with fishing or seafood processing operations; presumed low costs | Precipitation, solid solution | • Addition of P to the soil | None identified | Pb in soil, numerous other metals in aqueous solution |
• Used as a fertilizer in land application and horticulture | |||||||
Odor | |||||||
Mineral/inorganic | Bone char, bonemeal, bonemeal biochar (finely ground, poorly crystalline apatite, Ca10(PO4)6OH2) | Meat processing (e.g., cow bones) | Readily available near animal farms | • Adsorption | Free of metal and other types of contaminants | See Biochar | Cd, Pb, and Zn168 |
• Formation of metal phosphates |