Ait Saghir et al. 2025 - Coffee-enset agroforestry soil metals
Ait Saghir and colleagues measured potentially toxic elements in surface soils under coffee-enset agroforestry systems in southern Ethiopia. This is in-scope supply-chain pathway and source-attribution evidence for agroforestry soil reservoirs and amendment-linked metal loading; it is not coffee-bean, enset, or finished-food occurrence evidence.
Key numbers
The abstract reports 46 surface soil samples analyzed by ICP-OES for total arsenic, lead, zinc, copper, manganese, barium, strontium, and titanium. Source-reported average concentrations across the study are:
| Element | Average concentration (mg/kg) |
|---|---|
| Ti | 4570.7 |
| Mn | 2358.3 |
| Ba | 229.8 |
| Zn | 102.8 |
| Sr | 43.0 |
| Cu | 24.4 |
| Pb | 13.6 |
| As | 5.8 |
Table 1 reports descriptive statistics by soil type, in mg/kg:
| Soil type | Statistic | As | Cu | Ba | Pb | Zn | Sr | Mn | Ti |
|---|---|---|---|---|---|---|---|---|---|
| Cambisols | Min | 1.00 | 0.00 | 110.00 | 2.00 | 98.00 | 9.00 | 1774.00 | 2318.00 |
| Cambisols | Ave | 3.40 | 10.60 | 255.60 | 15.00 | 134.60 | 44.00 | 2810.20 | 5369.40 |
| Cambisols | Max | 5.00 | 17.00 | 320.00 | 30.00 | 188.00 | 68.00 | 3657.00 | 8018.00 |
| Luvisols | Min | 2.00 | 3.00 | 96.00 | 2.00 | 31.00 | 15.00 | 1312.00 | 1012.00 |
| Luvisols | Ave | 6.22 | 18.88 | 208.81 | 14.06 | 99.75 | 41.59 | 2295.75 | 4483.22 |
| Luvisols | Max | 11.00 | 44.00 | 436.00 | 25.00 | 196.00 | 178.00 | 3657.00 | 7960.00 |
| Nitisols | Min | 4.00 | 13.00 | 166.00 | 4.00 | 71.00 | 35.00 | 1651.00 | 2534.00 |
| Nitisols | Ave | 6.14 | 60.00 | 307.57 | 10.86 | 94.57 | 49.14 | 2321.71 | 4400.57 |
| Nitisols | Max | 8.00 | 95.00 | 649.00 | 17.00 | 136.00 | 79.00 | 3165.00 | 5702.00 |
The source reports LOD and LOQ values in mg/kg: As LOD = 0.3 and LOQ = 1; Cu LOD = 0.3 and LOQ = 1; Ba LOD = 0.9 and LOQ = 3; Pb LOD = 0.3 and LOQ = 1; Zn LOD = 0.3 and LOQ = 1; Sr LOD = 0.3 and LOQ = 1; Mn LOD = 0.3 and LOQ = 1; Ti LOD = 0.3 and LOQ = 1.
Table 2 reports single pollution index values by soil type:
| Soil type | Statistic | As | Cu | Ba | Pb | Zn | Sr | Mn | Ti |
|---|---|---|---|---|---|---|---|---|---|
| Cambisols | Ave | 0.47 | 0.42 | 0.44 | 0.79 | 2.24 | 0.18 | 5.11 | 1.85 |
| Cambisols | Max | 0.69 | 0.68 | 0.55 | 0.89 | 3.13 | 0.28 | 6.65 | 2.76 |
| Luvisols | Ave | 0.86 | 0.76 | 0.36 | 0.74 | 1.66 | 0.17 | 4.17 | 1.55 |
| Luvisols | Max | 1.53 | 1.76 | 0.76 | 5.37 | 3.27 | 0.74 | 6.55 | 2.74 |
| Nitisols | Ave | 0.90 | 2.66 | 0.50 | 0.63 | 1.54 | 0.20 | 4.23 | 1.41 |
| Nitisols | Max | 1.11 | 8.84 | 1.12 | 0.89 | 2.10 | 0.33 | 6.33 | 2.17 |
The abstract and conclusion highlight localized moderate contamination for Pb, with max SPI = 5.37 in Luvisols, Zn, with max SPI = 3.13 in Cambisols, and slight Cu contamination in Nitisols, with SPI = 2.66. Arsenic showed moderate contamination across soil types, including Luvisols where SPI = 1.53 and I-geo = 2.29 were reported.
Table 3 reports selected geoaccumulation-index values:
| Soil type | As average I-geo class | As max I-geo class | Pb max I-geo class | Zn max I-geo class | Mn max I-geo class |
|---|---|---|---|---|---|
| Cambisols | 0.60, UC-MC | 1.15, MC | 0.51, UC-MC | 0.74, UC-MC | 1.36, MC |
| Luvisols | 1.47, MC | 2.29, MC-HC | 0.25, UC-MC | 0.80, UC-MC | 1.36, MC |
| Nitisols | 1.45, MC | 1.83, MC | -0.30, UC | 0.27, UC-MC | 1.15, MC |
The enrichment-factor discussion reports Luvisols maximum EF values of 1.99 for Pb, 3.39 for Zn, 3.44 for Sr, and 1.97 for Mn. The authors attribute this localized enrichment to anthropogenic sources, especially intensive organic-matter amendments including manure and animal waste, with compost, poultry litter, sewage sludge, and household waste named as possible contributors.
Methods (brief)
The study sampled the Gedeo Zone of southern Ethiopia, a coffee-enset agroforestry region with Cambisols, Luvisols, and Nitisols. Forty-six surface composite soil samples were collected from 0-20 cm depth between 16 and 23 August 2023. Each composite consisted of 25 subsamples from approximately 250 m2, collected with a stainless-steel auger; about 1 kg fresh soil was collected per sampling point, GPS coordinates were recorded, and samples were air-dried, mixed, and sieved to 2 mm.
Soil pH, electrical conductivity, cation exchange capacity, total organic carbon, and particle-size distribution were measured using standard methods. Total potentially toxic elements were determined after 5 mL aqua-regia digestion and ICP-OES analysis following ISO 54320:2020. QA/QC included blanks, independent calibration standards, certified reference materials every ten samples, 5% duplicates, and 5% spikes at 1 mg/kg. Acceptance criteria included R2 >= 0.995, standard deviation ⇐ 5%, duplicate difference < 10%, and recoveries within +/- 10%; the authors state all results met these criteria.
Implications
Certification: Do not use these values as coffee, enset, or finished-food occurrence. They are agricultural-soil values and contamination-index values.
Courses: Useful supply-chain example for showing how the same crop system can have different soil-metal profiles depending on soil type, amendment history, and geochemical background.
App: Context only. The source can support upstream risk narratives for coffee-enset agroforestry systems and organic-amendment controls, not product scoring.
Wiki pages this source may touch
- soil-to-plant-transfer
- irrigation-and-soil-amendments
- source-attribution-environmental-burden-apportionment
- arsenic
- lead
- copper
- zinc
- manganese
- barium
- titanium
Verification notes
Recovered from skip:not-food-occurrence under the 2026-06-10 inclusion-by-default rule. The old skip treated the paper as out of scope because no coffee-bean or food concentration table was reported. On reading, it is in-scope lane a3 supply-chain pathway and source-attribution evidence because it measures PTE reservoirs in coffee-enset agroforestry soils and names organic amendments as a plausible anthropogenic loading source.
Numbers were checked against the abstract, methods, Table 1, Table 2, Table 3, the enrichment-factor discussion, spatial-distribution discussion, and conclusion in the extracted PDF text. Arsenic is labeled tAs in frontmatter because the source reports total arsenic in aqua-regia digests and does not report inorganic arsenic speciation. Chromium, cadmium, mercury, and methylmercury are not reported by this paper. Strontium is preserved as Sr in frontmatter and key numbers, but no wiki/metals/strontium.md page exists today, so it is not listed in the “may touch” wikilinks. Products and ingredients are intentionally empty.
Page history
The five most recent substantive edits to this page. The full version history lives in git; when DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.
| Commit | Date | Description |
|---|---|---|
| 7412baa | 2026-06-11 | recover-ingest 2026-06-10: basalamah2018-lead-vitamin-d-rats (lane a4, was skip:no-occurrence-data) |