It has been suggested that sources of P could be used to remediate metal-contaminated soil. The toxicity
of four potential P sources, potassium hydrogen phosphate (PHP), triple superphosphate (TSP), rock
phosphate (RP) and raw bone meal (RBM) to Eisenia fetida was determined. The concentration of P that
is statistically likely to kill 50% of the population (LC50) for PHP, TSP and RBM was determined in OECD
acute toxicity tests. 14 day LC50s expressed as bulk P concentration lay in the range 3319–4272 mg kg−1
for PHP, 3107–3590 mg kg−1 for TSP and 1782–2196 mg kg−1 for RBM (ranges present the 95% confidence
intervals). For PHP and TSP mortality was significantly impacted by the electrical conductivity of the
treated soils. No consistent relationship existed between mortality and electrical conductivity, soil pH
and available (Olsen) P across the PHP, TSP and RBM amendment types. In RP toxicity tests mortality was
low and it was not possible to determine a LC50 value. Incineration of bone meal at temperatures between
200 and 300 ◦C, pre-washing the bone meal, co-amendment with 5% green waste compost and delaying
introduction of earthworms after bone meal amendments by 21 days or more led to significant reductions
in the bone meal toxicity. These results are consistent with the toxicity being associated with the release
and/or degradation of a soluble organic component present in raw bone meal. Bone meal can be used as
an earthworm-friendly remedial amendment in metal-contaminated soils but initial additions may have
a negative effect on any earthworms surviving in the contaminated soil before the organic component in
the bone meal degrades in the soil
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