posted on 2019-01-04, 00:00authored byXiaojing Zhu, Larissa Dsikowitzky, Sebastian Kucher, Mathias Ricking, Jan Schwarzbauer
Nonextractable residues (NER) are
pollutants incorporated into
the matrix of natural solid matter via different binding mechanisms.
They can become bioavailable or remobilize during physical–chemical
changes of the surrounding conditions and should thus not be neglected
in environmental risk assessment. Sediments, soils, and groundwater
sludge contaminated with DDXs (DDT, dichlorodiphenyltrichloroethane;
and its metabolites) were treated with solvent extraction, sequential
chemical degradation, and thermochemolysis to study the fate of NER-DDX
along different environmental aquatic-terrestrial pathways. The results
showed that DDT and its first degradation products, DDD (dichlorodiphenyldichloroethane)
and DDE (dichlorodiphenyldichloroethylene), were dominant in the free
extractable fraction, whereas DDM (dichlorodiphenylmethane), DBP (dichlorobenzophenone),
and DDA (dichlorodiphenylacetic acid) were observed primarily after
chemical degradation. The detection of DDA, DDMUBr (bis(p-chlorophenyl)-bromoethylene), DDPU (bis(p-chlorophenyl)-propene)
and DDPS (bis(p-chlorophenyl)-propane) after chemical
treatments evidenced the covalent bindings between these DDXs and
the organic matrix. The identified NER-DDXs were categorized into
three groups according to the three-step degradation process of DDT.
Their distribution along the different pathways demonstrated significant
specificity. Based on the obtained results, a conceptual model of
the fate of NER-DDXs on their different environmental aquatic-terrestrial
pathways is proposed. This model provides basic knowledge for risk
assessment and remediation of both extractable and nonextractable
DDT-related contaminations.