Soil leaching tests are commonly used to evaluate the leachability of hazardous materials, such as heavy metals, from the soil. Batch leaching tests often enhance soil colloidal mobility and may require solid-liquid separation procedures to remove excess soil particles. However, batch leaching test results depend on particles that can pass through a 0.45μm membrane filter and are influenced by test parameters such as centrifugal intensity and filtration volume per filter. To evaluate these parameters, we conducted batch leaching experiments using metal-contaminated soils and focused on the centrifugal intensity and filtration volume per filter used in solid-liquid separation methods currently employed in standard leaching tests. Our experiments showed that both centrifugal intensity and filtration volume per filter affected the reproducibility of batch leaching tests for some soil types. The results demonstrated that metal concentrations in the filtrates significantly differed according to the centrifugal intensity when it was 3000 g for 2h or less. Increased filtration volume per filter led to significant decreases in filtrate metal concentrations when filter cakes formed during filtration. Comparison of the filtration tests using 0.10 and 0.45μm membrane filters showed statistically significant differences in turbidity and metal concentration. These findings suggest that colloidal particles were not adequately removed from the extract and contributed substantially to the apparent metal concentrations in the leaching test of soil containing colloidal metals.
A large amount of excavated soils with low-level As contamination
caused by civil construction projects is of great concern in Japan.
This study investigated the chemical speciation and extractability
of As in 24 soil samples from the sites affected and unaffected (naturally
contaminated) by anthropogenic pollution. The results of As K-edge
XANES demonstrated that naturally contaminated soils were grouped
into two types: (i) soils containing FeAsS-like and As2S3-like species (ave. 53%, hereafter As-S species) and
(ii) soils with no or minor As-S species (ave. 3%). Clear differences
were found in As, Fe, and S fractionations by sequential extraction.
From naturally contaminated soils enriched with As-S species, more
than 50% of As was extracted in the oxidizable fraction. Arsenic was
mainly recovered in the reducible fraction for naturally contaminated
soils with no or minor As-S species and anthropogenically contaminated
soils. The μ-XRF and μ-XAFS revealed that the naturally
contaminated soils containing As-S species were abundant in pyrite
framboids (∼20 μm in diameter) in which As occurred as
multiple oxidation states. The results suggest that framboidal pyrite
becomes a source of As in naturally contaminated soils after being
excavated and exposed to the surface environment.
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