# The Levels, Speciation, and Influencing Factors of Mercury in MSWI Fly Ashes of a High Geological Background Area

**Authors:** Liangliang Yang, Li Tang, Qingfeng Wang, Guangyi Sun, Peng Liu, Tianrong He, Zhonggen Li

PMC · DOI: 10.3390/toxics14030226 · Toxics · 2026-03-06

## TL;DR

This study examines mercury levels in fly ash from waste incineration in Guizhou, China, finding high mercury content and environmental risks.

## Contribution

The study provides new insights into mercury speciation and influencing factors in fly ash from a region with high geological mercury background.

## Key findings

- Total mercury in fly ash ranged from 0.52 to 444 mg/kg, with a weighted geometric mean of 22.14 mg/kg.
- Most mercury exists in elemental form (over 80%), but up to 26–29% is in water-soluble or ion-exchangeable forms.
- Mercury enrichment is influenced by heterogeneous waste compositions and transient thermochemical conditions.

## Abstract

Fly ash (FA) captures most mercury (Hg) in the waste stream during municipal solid waste incineration (MSWI), and the content and speciation of Hg in MSWI fly ash (MSWI-FA) have a significant impact on the ecological environment. In this study, 245 fly ash samples were collected from 18 MSWI facilities in Guizhou Province, a fragile karst area with a high Hg background in Southwest China. The results indicate that total Hg ranged from 0.52 to 444 mg/kg among samples, while the geometric means varied from 0.85 to 223.33 mg/kg for different incinerators, with a weighted geometric mean of 22.14 mg/kg, more than double the national average. Substantial temporal variability in Hg content suggested intermittent inputs of Hg-rich waste into the MSW stream. While positive correlations (p < 0.05) were observed between Hg and chlorine, potassium, and cadmium, the moderate to low R2 values indicate that Hg enrichment is a complex multi-factor system influenced by heterogeneous waste compositions and transient thermochemical conditions. Speciation analysis revealed that most of the Hg exists in its elemental form (F4), constituting over 80% of the total Hg. However, the water-soluble fraction (F1) and the ion-exchangeable fraction (F2) each reached up to 26–29% in some samples, indicating substantial environmental mobility. These findings demonstrate that MSWI-FA in Guizhou contains elevated Hg levels, posing considerable ecological and environmental risks. Enhancing the classification and management of Hg-containing waste in MSW is critical to mitigating the environmental risks of fly ash, particularly in karst ecological areas.

## Linked entities

- **Chemicals:** mercury (PubChem CID 23931), Hg (PubChem CID 23931), chlorine (PubChem CID 312), potassium (PubChem CID 813), cadmium (PubChem CID 23973)

## Full-text entities

- **Diseases:** FA (MESH:C000719189), injury to (MESH:D014947), toxicity (MESH:D064420)
- **Chemicals:** Mg (MESH:D008274), Na (MESH:D012964), lime (MESH:C016538), F2 (MESH:D005461), SnCl2 (MESH:C023599), dioxin (MESH:D004147), hydroxylamine hydrochloride (MESH:D019811), salt (MESH:D012492), thiourea (MESH:D013890), SO2 (MESH:D013458), PVC (MESH:D011143), Pb (MESH:D007854), Na2CO3 (MESH:C005686), HgCl2 (MESH:D008627), Rh (MESH:D012238), Metalloids (MESH:D058955), S (MESH:D013455), HCl (MESH:D006851), Metal (MESH:D008670), sodium bicarbonate (MESH:D017693), water (MESH:D014867), Se (MESH:D012643), Cu (MESH:D003300), Mn (MESH:D008345), Ca (MESH:D002118), HNO3 (MESH:D017942), MgO (MESH:D008277), AFS (-), HF (MESH:D006195), Cd (MESH:D002104), PTFE (MESH:D011138), Antimony (MESH:D000965), carbon (MESH:D002244), Hg (MESH:D008628), chloride (MESH:D002712), heavy metal (MESH:D019216), potassium borohydride (MESH:C028371), aqua regia (MESH:C022102), SDS (MESH:D012967), Fe (MESH:D007501), BrCl (MESH:C016271), Hg2Cl2 (MESH:C015728), Chlorine (MESH:D002713), Arsenic (MESH:D001151), sulfide (MESH:D013440), K (MESH:D011188), Zinc (MESH:D015032), H2SO4 (MESH:C033158), gold (MESH:D006046)
- **Species:** Homo sapiens (human, species) [taxon 9606]

## Full text

_Full body text omitted from this summary view._ Fetch the complete paper as Markdown: https://tomesphere.com/paper/PMC13029934/full.md

## Figures

7 figures with captions in the complete paper: https://tomesphere.com/paper/PMC13029934/full.md

## References

69 references — full list in the complete paper: https://tomesphere.com/paper/PMC13029934/full.md

---
Source: https://tomesphere.com/paper/PMC13029934