Over 60% of all land applied biosolids are used on agricultural
land. Application rates are usually determined by the
nitrogen demand of the crop and cumulative metal
loadings. For example, if you had a crop the needed 130 kg
N/ha and you were applying a perfectly "clean" sludge
that contained 3% N (2% organic and 1% inorganic with 30%
mineralization in the soil). The total application rate
would be 130/(0.01 + 0.30 * 0.20) = 1857 kg/ha/year or 1.86
Mg/ha/year.
On the other hand, if your biosolids had an
arsenic (As) content of 6 mg As/kg of dry sludge and your site
had a proposed 20 year lifetime, then to meet the 18 kg As/ha
cumulative loading limit your yearly As loading would be (18/20)
= 0.9 kg As/year. The corresponding sludge application rate
would be (0.9 kg As/year)(1000000 mg/kg)/(6 mg As/kg of dry
sludge) = 150000 kg/ha/year or 150 Mg/ha/year.
Typical application rates in moderate climate
would be 15 Mg/ha/year.
Images of common Application techniques.
According to 40 CFR-257, PSRP's must be accomplished and access must be restricted to sludge applied land.
or PSRPs must be used.
Forest soil-plant systems are ideal for biosolids application for several reasons:
EPA suggests a one-time loading of 47 Mg/ha can improve growth for up to 5 years with negligible nitrogen leaching.
Example of forest application system.
Marginal
land, such as surface mines, mine tailings, quarries, clear
forests, landfills, lack nutrients. Specifically, old mines
can have very compacted and acidic soils (pH<3). These
conditions are very difficult and expensive to restore using
traditional remediation techniques. Lime-stabilized,
dewatered biosolids have had great success restoring these
soils. The lime increases the pH and the high organic
matter content helps restore soil structure.
Initially, trace metal and nitrate
concentrations in percolate can increase, but these drawbacks are
short term. After two years these concentrations usually
return to normal.