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Polycyclic aromatic hydrocarbons (PAHs) persistence, bioavailability and toxicity in sewage sludge- or sewage sludge-derived biochar-amended soil
被引:54
作者:
Tomczyk, Beata
[1
]
Siatecka, Anna
[2
]
Jedruchniewicz, Katarzyna
[2
]
Sochacka, Aleksandra
[2
]
Bogusz, Aleksandra
[1
]
Oleszczuk, Patryk
[2
]
机构:
[1] Natl Res Inst, Dept Ecotoxicol, Inst Environm Protect, Ul Krucza 5-11D, PL-00548 Warsaw, Poland
[2] Marie Curie Sklodowska Univ, Fac Chem, Dept Radiochem & Environm Chem, Pl M Curie Sklodowskiej 3, PL-20031 Lublin, Poland
关键词:
Biochar;
Sewage sludge;
Soil;
Polycyclic aromatic hydrocarbons;
Toxicity;
ORGANIC-COMPOUNDS;
BLACK CARBON;
PHENANTHRENE;
SORPTION;
MATTER;
FIELD;
SEQUESTRATION;
DECOMPOSITION;
CONTAMINANTS;
GERMINATION;
D O I:
10.1016/j.scitotenv.2020.141123
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
Soils can be contaminated with polycyclic aromatic hydrocarbons (PAHs) when either sewage sludge (SSL) or biochar (BC) are used. There are no comparative studies regarding the effects of soil amendment with SSL or BC on the persistence, bioavailability and toxicity of PAHs. This research compared the persistence of PAHs (based on the extractable content, C-tot) and their bioavailability (freely dissolved, C-free) as well as the toxicity (solid phase: Phytotoxkit F with Lepidium sativum and the Collembolan test with Folsomia candida; leachates: Phytotestkit F with L. sativum and Microtox (R) with Aliivibrio fischeri) of soil amended with SSL or with SSL-derived BCs. BCs were produced from three different sewage sludges at a temperature of 500 degrees C. SSLs or BCs were added to the soil at a rate of 1% (30 t/ha). Adding SSL to the soil increased more the PAH content in it than after BC application, which was associated with a higher content of PAHs in SSL. Losses of Sigma 16 C-tot and C-free PAHs were higher than those observed for biochar only in the case of one SSL. In the other cases, PAH losses were either higher for biochar or did not differ significantly between SSL and BC. On the other hand, the analysis of the individual groups of PAHs showed significant differences between SSL and BC, both for C-tot and C-free. Nonetheless, these differences were largely driven by the type of sewage sludge and biochar. Only in the case of root
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