Table 2.
Literature comparison of selected heavy metal concentrations (mg kg−1) in samples from quarry influenced environments
| Elements | Turhan et al., (2026) | Damola et al., (2021) | Etim and Adie (2012) | Mellese et al., (2025) | Ajibade et al., (2022) | Adetola et al., (2024) | In this study |
|---|---|---|---|---|---|---|---|
| XRF | ICP-OES | AAS | ICP-OES | ICP-MS | ICP-OES | ICP-OES | |
| 126 samples | 24 samples | 6 samples | 5 samples | 24 samples | 10 samples | 40 samples | |
| Perlite samples | Street dust in a quarry | Topsoil samples within the vicinity of limestone quarry | Exploitation sites of sandstones quarry sites | Quarry soil-dust samples | Soils from quarry sıte | Street dust samples within the vicinity of a quarry | |
| Ti | 528.3 | 4010 | |||||
| V | 7.1 | 59.75 | 24.72 | 49.42 | |||
| Cr | 64.9 | 126 | 11.81 | 115.41 | 52.46 | 0.84 | 298.17 |
| Mn | 383.5 | 716 | 512.50 | 192 | 3425.68 | ||
| Fe | 6585.4 | 43,900 | 11,220.17 | 4354 | 17,346.24 | ||
| Co | 7.0 | 24 | 13.39 | 12.40 | 3.81 | 432.64 | |
| Ni | 19.8 | 56 | 10.91 | 10.58 | 24.25 | 1.6 | 37.45 |
| Cu | 4.3 | 25 | 17.93 | 13.23 | 42.22 | 12.37 | 231.68 |
| Zn | 31.1 | 65 | 42.90 | 15.10 | 88.66 | 11.48 | 384.08 |
| As | 4.2 | 1.7 | 4.64 | 1.59 | 66.27 | ||
| Pb | 26.4 | 14.8 | 16.00 | 19.91 | 32.83 | 3.05 | 128.38 |
| Zr | 93.7 | ||||||
| Cd | 0.1 | 1.15 | 0.11 | 0.46 | |||
| Mo | 1.31 | 0.69 | 0.17 | ||||
| U | 6.97 | ||||||
| Th | 34.42 | ||||||
| Sr | 416.75 | ||||||
| Se | 0.73 | 11.63 | |||||
| Al | 80,400 | 1678 | 21,843.18 | ||||
| Hg | 1.51 | 0.06 | |||||
| Sb | 5.52 | 2.4 | |||||
| Sn | 3.6 | 47.21 |
Values reported for quarry influenced urban environments in selected international studies. Dust size fractions differ among studies and are reported where available. Concentrations are expressed as mg kg−1. Elements were selected according to their relevance to human health risk assessment discussed in the main text. NR indicates that the element was not reported