Related Experiment Video
Updated: Aug 15, 2025

Physical, Chemical and Biological Characterization of Six Biochars Produced for the Remediation of Contaminated Sites
Published on: November 28, 2014
Interaction between biochar-dissolved organic matter and chlorophenols during biochar adsorption
Jin Zhang1, Nannan Huang2, Hui Li1
1Institute of Environmental Pollution and Health, School of Environmental and Chemical Engineering, Shanghai University, Shanghai, 200444, People's Republic of China.
Biochar dissolved organic matter (BDOM) interacts with chlorophenols (CPs) primarily through protein- and fulvic-like components. Understanding these interactions is key for effective biochar remediation of contaminated sites.
Area of Science:
- Environmental Chemistry
- Soil Science
- Bioremediation
Background:
- Biochar (BC) is used for chlorophenol (CP) remediation, but the role of its dissolved organic matter (BDOM) is poorly understood.
- Investigating BDOM interactions with CPs is crucial for optimizing BC-based remediation strategies.
- Peanut hull (PDOM) and corn stalk (CDOM) derived DOM were used to study interactions with 2,4,6-trichlorophenol (TCP).
Purpose of the Study:
- To elucidate the role and mechanisms of BDOM in the remediation of CPs.
- To analyze the interactions between PDOM/CDOM and TCP using spectroscopic and modeling techniques.
- To determine the binding affinity and quenching mechanisms between BDOM components and TCP.
Main Methods:
- Excitation-emission matrix (EEM) spectroscopy combined with fluorescence region integration (EEM-FRI) and parallel factor analysis (EEM-PARAFAC).
- Analysis of humic-like, protein-like, and fulvic-like materials within PDOM and CDOM.
- Application of the modified Stern-Volmer model to calculate stability constants (Log KTCP) and identify quenching mechanisms.
Main Results:
- Humic-like materials constituted over 60% of both PDOM and CDOM; CDOM had higher protein- and fulvic-like content.
- Protein- and fulvic-like components were the primary interactors with TCP, showing over 25% fluorescence decrease.
- Static quenching was the dominant mechanism, with stability constants (Log KTCP) ranging from 3.53 to 4.73 for PDOM and CDOM.
Conclusions:
- BDOM plays a significant role in CP remediation, with protein- and fulvic-like fractions being key.
- The sequential binding order of TCP to fluorescent components in BDOM was identified.
- Findings support biochar screening for CP remediation and understanding environmental DOM behavior during BC application.
More Related Videos
10:44Preparation of Biomass-based Mesoporous Carbon with Higher Nitrogen-/Oxygen-chelating Adsorption for CuII Through Microwave Pre-Pyrolysis
Published on: February 12, 2019
08:12Characterization, Quantification and Compound-specific Isotopic Analysis of Pyrogenic Carbon Using Benzene Polycarboxylic Acids BPCA
Published on: May 16, 2016
Related Concept Videos
Extraction: Advanced Methods
Hydrolysis of Chlorobenzene to Phenol: Dow Process
Complexation Equilibria: The Chelate Effect