Clair-Caliot et al. 2021 — Arsenic uptake by irrigated vegetables and cooked foods in Burkina Faso
This greenhouse study characterizes the transfer of arsenic from geogenic As-contaminated irrigation water to seven vegetables commonly grown and consumed in Burkina Faso (amaranth, carrot, green bean, lettuce, okra, spinach, tomato), and separately assesses how cooking with As-spiked or As-free water affects final As content in both greenhouse vegetables and locally purchased staple foods. Arsenic was measured as total As (tAs) by ICP-MS after HNO3/H2O2 digestion; speciation into inorganic vs organic arsenic was not performed. At the mid-point irrigation concentration of 500 µg/L As(V), edible-part concentrations were: spinach 6.6, lettuce 3.9, carrot 3.5, amaranth 2.2, okra 0.9, green bean 0.8, and tomato 0.2 µg/g dry mass. Cooking contaminated vegetables with As-free water reduced As content by an average of 39%, while cooking with As-contaminated water transferred As to the cooked food; steaming reduced As by 8- to 18-fold compared to boiling.
Key numbers
Speciation note: All As values in this study are total arsenic (tAs) measured by ICP-MS. No speciation into iAs and organic As was performed. Irrigation water As was applied as arsenate As(V) (sodium arsenate dibasic heptahydrate), so the arsenic entering plants was inorganic arsenate, but the measurement in plant tissue is total As and is recorded here as tAs per wiki convention.
Experimental design:
- 168 pots: 7 species × 4 As irrigation concentrations (0, 100, 500, 1,000 µg/L) × 6 replicates
- Greenhouse at 2iE, Ouagadougou; dry season November 2017–February 2018
- Culture period 65–130 days; harvested at maturity
As in edible parts at 500 µg/L irrigation water (µg/g DM):
- Spinach (leaves): 6.6 ± 0.5
- Lettuce (leaves): 3.9 ± 0.1
- Carrot (root): 3.5 ± <0.1
- Amaranth (leaves): 2.2 ± <0.1
- Okra (pods): 0.9 ± <0.1
- Green bean (pods): 0.8 ± <0.1
- Tomato (fruits): 0.2 ± <0.1
Average across all As-spiked irrigation levels (µg/g DM, edible parts):
- Spinach: 8.1 ± 5.6
- Lettuce: 3.6 ± 2.5
- Amaranth: 3.0 ± 2.5
- Carrot (all organs, edible): included in root-vegetable category
- Green bean: 1.5 ± 1.5
- Okra: 0.7 ± 0.4
- Tomato: 0.3 ± 0.2
Edible-part category averages (µg/g DM, across all spiked levels):
- Leafy vegetables (amaranth, lettuce, spinach): 4.9 ± 4.5
- Root vegetables (carrot): 2.9 ± 2.0
- Fruit/pod vegetables (tomato, okra, green bean): 0.8 ± 1.1
Cooking effects (greenhouse vegetables cooked in As-free water):
- Amaranth: 61% mean As extraction (up to 69%)
- Spinach: 3–31% As extracted (9% at 500 µg/L)
- Okra: 35–49% As extracted at 500–1,000 µg/L
- Overall average: 39% reduction from cooking with As-free water
Market food As content (uncooked, local Ouagadougou market):
- Local rice (Boulkiemdé): 0.127 µg/g tAs
- Maize flour (for tô): 0.06 µg/g tAs
- Black-eyed peas (bean/niébé): 0.04 µg/g tAs
Steaming vs boiling:
- Steamed yam: 7.9× lower As than boiled yam
- Steamed rice: 17.9× lower As than boiled rice (absorb-method)
Soil properties (experimental substrate):
- As: 0.684 µg/g, Cd: 0.029 µg/g, Pb: 6.620 µg/g
- Soil As was below EU maximum acceptable limit for agricultural soil (20 µg/g)
Translocation factors (TF = shoot As / root As):
- Only carrot had TF > 1 (leaves concentrate more than roots); all other species had TF < 1
- Tomato had lowest TF among measured species (~0.6)
Cancer risk (CR): Exceeded 1 in 10,000 for leafy vegetables (amaranth, lettuce, spinach) and carrot under 500 and 1,000 µg/L irrigation; tomato and okra had CR < 1 in 10,000 across all treatments. Risk characterization used EPA OSF for inorganic arsenic (1.5 (mg/kg/day)^-1) applied to total As — a conservative assumption.
Detection limits: 0.05 µg/L in digest liquid; 0.05 µg/g in food dry mass.
Methods (brief)
Greenhouse experiment at 2iE, Ouagadougou; sandy loam soil (subsurface 2–25 cm) spiked with As(V) as sodium arsenate dibasic heptahydrate. Plants harvested at maturity, freeze-dried, ground, digested in Burkina Faso by HNO3 at 80°C (Bhatti et al. 2013 protocol) or in Switzerland by HNO3/H2O2 at 240°C (ultraCLAVE microwave). Both methods compared for okra and spinach with good agreement for concentrations 0.5–20 µg/g. As determined by ICP-MS (Agilent 7500cx) at Eawag, Switzerland. Standard reference materials: NIST 1568b rice flour (118% mean recovery), NIST 1573a tomato leaves (125% mean recovery). Cooking experiments: greenhouse vegetables boiled in excess distilled water; market foods boiled, steamed, or prepared with cold water according to traditional Burkinabe recipes, in As-free or As-spiked cooking water. No arsenic speciation was performed; all values are total As.
Implications
Certification: This study is most relevant as evidence for the processing lever (cooking method) affecting final As in food, and for ranking vegetable types by relative As accumulation potential from contaminated irrigation water. The concentrations reported are from an experimental system with irrigated As concentrations far exceeding normal ambient conditions; they are not suitable as baseline contamination profile values for typical commercial production contexts. They establish ceiling values under high-As irrigation stress.
Courses: Excellent teaching case on irrigation-water-to-plant As transfer, translocation factors, differential accumulation by vegetable type (leafy > root > fruit/pod), and the effectiveness of cooking method (steaming vs boiling) as a mitigation strategy. The Burkina Faso context adds geographic equity dimension.
App: Not suitable for contamination_profile typical_ppb values — these are experimental high-dose exposure data, not field survey data from commercial vegetable markets. Use only for directional ranking (spinach and lettuce accumulate more As than tomato and okra under As-contaminated irrigation).
Microbiome: Not applicable.