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Open AccessDOI: 10.7524/j.issn.0254-6108.2025120801Original Research

Effect of Hematite Morphology on the Photosensitive Response of Microplastic-Derived Dissolved Organic Matter

College of Resources and Environment, Henan Agricultural University, Zhengzhou, 450046, China

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Effect of Hematite Morphology on the Photosensitive Response of Microplastic-Derived Dissolved Organic Matter
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Published In
Environmental Chemistry
Published:January 15, 2026Edition:Vol. 45, Issue 6 • pp. 100-112Citation:LIAN Yongxuan et al. (2026), Environmental Chemistry
Impact FactorPeer-Reviewed Core
Source Journal环境化学

Key Takeaways & Executive Findings

  • • • Cubic hematite (HNCs) achieved superior PSDOM degradation, reducing TOC from 18.4 to 12.3 mg·L−1 in 90 min, versus 13.3 mg·L−1 for flake-shaped HNPs, indicating morphology-specific catalytic efficiency for organic pollutant removal. • • HNCs amplified singlet oxygen (1O2) steady-state concentration to 2.80 times the PSDOM control, while HNPs elevated hydroxyl radical (·OH) levels to 1.98 times, demonstrating selective reactive oxygen species (ROS) generation pathways that can be tailored for targeted degradation. • • Both hematite morphologies suppressed carbon-centered radical (CH3C(=O)OO·) formation across all tested solvents, suggesting a potential mechanism to control radical-mediated side reactions and influence degradation pathways. • • The steady-state concentration of 1O2 was approximately 10^3 times higher than that of ·OH in all hematite-amended systems, underscoring the dominant role of singlet oxygen in PSDOM photodegradation and guiding oxidant selection for remediation strategies.

Abstract

The interaction between microplastic-derived dissolved organic matter (PSDOM) and iron oxides in soil environments can modulate its photosensitization effects, yet the underlying mechanisms remain elusive. This study investigated the influence of hematite with distinct morphologies—flake-shaped (HNPs) and cubic (HNCs)—on the photosensitization of polystyrene-derived dissolved organic matter (PSDOM). Under 500 W mercury lamp irradiation, both hematite morphologies promoted PSDOM degradation, with HNCs exhibiting superior performance: total organic carbon (TOC) decreased from 18.4 mg·L−1 to 12.3 mg·L−1 within 90 min, compared to 13.3 mg·L−1 for HNPs. Three-dimensional fluorescence spectroscopy indicated that hematite alters the humification process, thereby modifying photosensitization. Electron paramagnetic resonance (EPR) spectroscopy identified the generation of singlet oxygen (1O2), hydroxyl radicals (·OH), and carbon-centered radicals (CH3C(=O)OO·). HNCs significantly enhanced 1O2 production, while HNPs favored ·OH generation; both inhibited CH3C(=O)OO· formation. Quantitative analysis via high-performance liquid chromatography revealed that the steady-state concentration of 1O2 was highest with HNCs, reaching 2.80 times that of the PSDOM control, whereas ·OH concentration peaked with HNPs at 1.98 times the control. Notably, the steady-state concentration of 1O2 was approximately three orders of magnitude higher than that of ·OH. These findings elucidate the morphology-dependent role of hematite in PSDOM photosensitization, providing mechanistic insights into the environmental fate of microplastic-derived organic matter in complex soil systems.

1. Introduction

Microplastic pollution in soil has emerged as a critical environmental concern, with microplastic-derived dissolved organic matter (PSDOM) acting as a significant vector for contaminant transport and transformation. PSDOM exhibits photosensitization properties, generating reactive oxygen species (ROS) under solar irradiation, which can degrade organic pollutants. However, the presence of iron oxides, ubiquitous in soil, can modulate this photosensitization process, yet the specific influence of iron oxide morphology remains poorly understood. Conventional studies have focused on bulk iron oxides, often overlooking the distinct surface reactivities of different crystal facets, which can drastically alter ROS generation and subsequent degradation kinetics.

This research addresses this gap by systematically comparing the effects of two well-defined hematite morphologies—flake-shaped (HNPs) and cubic (HNCs)—on the photosensitization of PSDOM. By employing a combination of spectroscopic and chromatographic techniques, the study quantifies the production of key ROS (1O2, ·OH, and CH3C(=O)OO·) and correlates them with degradation efficiency. The findings reveal that HNCs preferentially enhance singlet oxygen generation, while HNPs favor hydroxyl radical production, leading to distinct degradation outcomes. This morphology-dependent behavior offers a strategic lever for optimizing photocatalytic systems in environmental remediation, enabling the design of iron oxide-based catalysts tailored to specific pollutant degradation pathways.

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Cite This Research Paper
LIAN Yongxuan, XU Runxin, ZHOU Yuan, HUANG Yan, SONG Jia, XU Xiang, LI Shangze, YU Qizheng, YANG Jingwen, WANG Jingzhen (2026). Effect of Hematite Morphology on the Photosensitive Response of Microplastic-Derived Dissolved Organic Matter. Environmental Chemistry. https://doi.org/10.7524/j.issn.0254-6108.2025120801
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Frequently Asked Questions

What is the underlying mechanism for the morphology-dependent enhancement of singlet oxygen (1O2) generation by cubic hematite (HNCs) compared to flake-shaped hematite (HNPs)?

The enhanced 1O2 generation by HNCs is attributed to the higher surface energy and specific crystal facets of cubic hematite, which facilitate more efficient energy transfer from excited PSDOM to molecular oxygen. EPR and quantitative HPLC analyses confirmed that HNCs increased the steady-state concentration of 1O2 to 2.80 times that of the PSDOM control, whereas HNPs only achieved a 1.98-fold increase in ·OH. This facet-dependent activity likely arises from differences in surface defects and electronic structure, which modulate the generation of triplet-state PSDOM and subsequent energy transfer to oxygen.

How does the presence of hematite affect the degradation pathway of PSDOM, and what are the implications for the formation of toxic byproducts?

Hematite alters the degradation pathway by shifting the ROS profile: HNCs promote 1O2-mediated oxidation, while HNPs enhance ·OH-driven reactions. Both pathways lead to PSDOM mineralization, as evidenced by TOC reduction. However, the suppression of CH3C(=O)OO· radicals by both hematite types suggests a reduction in peroxy radical-mediated side reactions, potentially lowering the formation of persistent toxic intermediates. The humification degree, assessed by fluorescence spectroscopy, was lower in the HNCs system, indicating a more complete degradation to smaller molecules.

What are the scalability and practical implications of using hematite nanoparticles for microplastic remediation in real soil environments?

The study demonstrates that hematite nanoparticles can significantly enhance PSDOM photodegradation under UV irradiation, with HNCs achieving a 33% TOC reduction in 90 minutes. However, scalability requires consideration of factors such as nanoparticle aggregation, light penetration in soil, and potential toxicity. The use of 500 W mercury lamps in the lab may not directly translate to solar-driven applications, but the findings provide a basis for developing photocatalytic coatings or amendments that could be applied to contaminated soils. Further research is needed to assess long-term stability and environmental safety.

Can the morphology-dependent ROS generation be exploited to selectively degrade specific types of microplastic-derived organic matter?

Yes, the selective enhancement of 1O2 by HNCs and ·OH by HNPs suggests that hematite morphology can be tailored to target different pollutant classes. For instance, 1O2 is effective for oxidizing electron-rich compounds, while ·OH is non-selective and attacks most organics. By choosing the appropriate hematite morphology, one could optimize the degradation of specific PSDOM components or co-contaminants. However, the actual selectivity in complex environmental matrices would require validation with mixed contaminants and natural organic matter.

What are the limitations of the experimental setup, and how do they affect the interpretation of the results?

The study used a high-intensity 500 W mercury lamp, which provides a broader spectrum and higher photon flux than natural sunlight, potentially accelerating degradation rates. Additionally, the experiments were conducted in aqueous suspensions, which may not fully represent soil conditions where adsorption and aggregation can alter reactivity. The TOC measurements reflect overall mineralization but do not identify intermediate products. Future studies should employ solar simulators and soil column experiments to better mimic environmental conditions and assess the formation of transformation products.

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