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Open AccessDOI: 10.7524/j.issn.0254-6108.2025010607Original Research

Multi-media Distribution, Source Apportionment, and Risk Assessment of Polycyclic Aromatic Hydrocarbons in the Forest-Grassland Transition Zone of Inner Mongolia

College of Resources and Environmental Sciences, Inner Mongolia Agricultural University, Inner Mongolia Key Laboratory of Soil Quality and Nutrient Resources, Hohhot, 010018, China

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Multi-media Distribution, Source Apportionment, and Risk Assessment of Polycyclic Aromatic Hydrocarbons in the Forest-Grassland Transition Zone of Inner Mongolia
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Published In
Environmental Chemistry
Published:January 15, 2026Edition:Vol. 45, Issue 5 • pp. 100-112Citation:WANG Mao et al. (2026), Environmental Chemistry
Impact FactorPeer-Reviewed Core
Source Journal环境化学

Key Takeaways & Executive Findings

  • • • Soil PAH concentrations (mean 168.8 ng·g⁻¹, range 34.9–465.3 ng·g⁻¹) exceed those in several natural forest areas, indicating significant accumulation from combustion sources; this necessitates monitoring in remote ecosystems. • • Litter exhibited the highest PAH concentrations (mean 465.1 ng·g⁻¹, up to 2262.5 ng·g⁻¹), with 3- and 4-ring PAHs dominating, suggesting that litter acts as a major temporary sink and potential secondary source. • • Dead bark showed a concentration range of 123.3–241.6 ng·g⁻¹ and was identified as the primary accumulation medium with high carcinogenic contribution (TEQ), underscoring its role in long-term ecological risk. • • Spearman correlation analysis found no significant correlations (P > 0.05) among PAH concentrations in soil, litter, and bark, indicating independent accumulation processes and necessitating multi-media assessment for comprehensive risk evaluation.

Abstract

This study investigated the occurrence, sources, and ecological risks of polycyclic aromatic hydrocarbons (PAHs) in soil, litter, and bark samples collected from the forest-grassland transition zone of Inner Mongolia. A total of 12 PAHs were detected in soil, with concentrations ranging from 34.9 to 465.3 ng·g⁻¹ (mean 168.8 ng·g⁻¹), predominantly 3–5 ring compounds. Litter contained 14 PAHs at concentrations between 106.4 and 2262.5 ng·g⁻¹ (mean 465.1 ng·g⁻¹), dominated by 3- and 4-ring PAHs. Both living and dead bark exhibited 14 PAHs, with concentration ranges of 119.2–240.0 ng·g⁻¹ and 123.3–241.6 ng·g⁻¹, respectively, mainly composed of 4-ring PAHs. Spearman correlation analysis revealed no significant correlations among PAH concentrations across the three media (P > 0.05). Source apportionment using diagnostic ratios and principal component analysis indicated that soil PAHs primarily originated from biomass, coal, and gasoline combustion; litter PAHs from petroleum volatilization and coal/natural gas combustion; and bark PAHs from petroleum volatilization and fossil fuel combustion, with high-molecular-weight PAHs dominating. Ecological risk assessment using the risk quotient (RQ) method showed that soil PAHs posed low overall ecological risk, though certain individual PAHs exhibited higher risk. The toxic equivalent (TEQ) method indicated that dead bark was the primary accumulation medium with high carcinogenic contribution, posing elevated ecological risk. Although litter and living bark had lower PAH concentrations, their long-term accumulation effects warrant attention. These findings provide crucial scientific evidence for understanding the environmental behavior and potential risks of PAHs in cold, high-latitude regions of northern China.

1. Introduction

The forest-grassland transition zone of Inner Mongolia represents a critical ecotone sensitive to anthropogenic pollution. Previous studies on PAHs in natural soils have often focused on single media, overlooking the differential accumulation and transfer across soil, litter, and vegetation compartments. This oversight hampers accurate ecological risk assessment, particularly in cold regions where PAH persistence is enhanced. Existing commercial monitoring approaches typically rely on soil-only measurements, which fail to capture the dynamic exchange and sink functions of litter and bark.

This study addresses this bottleneck by simultaneously analyzing PAHs in soil, litter, and bark from the same ecosystem. By employing diagnostic ratios and principal component analysis for source apportionment, and integrating risk quotient (RQ) and toxic equivalent (TEQ) methodologies, the research provides a holistic view of PAH distribution and risk. The findings reveal that dead bark, often neglected, serves as a major reservoir with high carcinogenic potential, challenging conventional soil-centric assessments. This multi-media approach offers a more robust framework for evaluating PAH contamination in boreal and alpine ecotones, informing targeted remediation and policy decisions.

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Cite This Research Paper
WANG Mao, ZHANG Yufei, LI Baicheng, LI Junwen, WANG Yiqun, XU Xuehui (2026). Multi-media Distribution, Source Apportionment, and Risk Assessment of Polycyclic Aromatic Hydrocarbons in the Forest-Grassland Transition Zone of Inner Mongolia. Environmental Chemistry. https://doi.org/10.7524/j.issn.0254-6108.2025010607
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Frequently Asked Questions

What are the dominant PAH sources in the soil of the forest-grassland transition zone, and how were they identified?

Soil PAHs primarily originate from biomass, coal, and gasoline combustion, as determined by diagnostic ratios and principal component analysis. The mean concentration of 168.8 ng·g⁻¹, with a predominance of 3–5 ring PAHs, supports a pyrogenic source signature.

Why is dead bark considered a high-risk medium for PAH accumulation, and what are the implications for ecological risk assessment?

Dead bark exhibited PAH concentrations up to 241.6 ng·g⁻¹ and showed the highest toxic equivalent (TEQ) values, indicating significant carcinogenic potential. This suggests that bark, particularly dead bark, acts as a long-term sink for PAHs, and its inclusion in monitoring programs is critical for accurate risk characterization.

How do PAH concentrations in litter compare to those in soil, and what does this imply for PAH dynamics in the ecosystem?

Litter had substantially higher PAH concentrations (mean 465.1 ng·g⁻¹) compared to soil (mean 168.8 ng·g⁻¹), indicating that litter serves as a major temporary reservoir. The lack of significant correlation between media (P > 0.05) suggests independent accumulation processes, possibly due to different exposure pathways and degradation rates.

What is the overall ecological risk posed by PAHs in the study area, and which specific compounds contribute most to the risk?

The risk quotient (RQ) method indicated low overall ecological risk in soil, but certain individual PAHs, such as high-molecular-weight compounds, exhibited higher risk levels. The TEQ method highlighted dead bark as having high carcinogenic contribution, emphasizing the need for compound-specific risk management.

How do the PAH concentrations in this study compare to other natural forest areas, and what factors might explain the differences?

Soil PAH concentrations in this study (mean 168.8 ng·g⁻¹) are higher than those reported in some other natural forest areas, likely due to regional atmospheric deposition from local combustion sources and the cold climate, which slows degradation. This underscores the importance of regional source control.

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