Overview
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Key numbers
The worker extracted the full PDF text with layout preservation twice and compared extraction hashes before commit. The following lines are copied from numeric/table-bearing regions of the PDF and retain the source units and wording where legible:
- 154 samples of different fruits and vegetables and 440 samples of fish were analyzed by atomic
- emissions that range between 30 and 70 tons of Hg (6,7). In the Chocó department,
- vegetables; (2) to determine the target hazard quotient (THQ) and total THQ to assess the
- Geophagus Pellegrini, and Pimelodus sp. The non-carnivorous (110 individuals) were Prochilo-
- trifida; tubers (2): Colocasia esculenta, Manihot esculenta; vegetables (9): Eryngium foetidum,
- 2.3. Analysis of THg, MeHg, As, Pb, and Cd in Fish Muscle, Fruits, and Vegetables
- the methods used. The recovery percentage was between 92 and 96% and the detection
- of dogfish muscle certificate (4.47 ± 0.32 µg g−1 ). The percent recovery for MeHg was 99%.
- (Table S1). On average, the inhabitants of the middle basin of the Atrato river consume
- 256 g/day of fish (8). The average consumption of fruits and vegetables was established
- the information provided in the surveys (Table S1). The results obtained from the analysis
- CDDingestion = (4)
- Pb (38); Bw is the mean body weight for each municipality; AT is the mean time for
- where PTWI is the reference value of 1.6 µg/kg bw/week for women of childbearing age
- and children, 3.2 µg/kg bw/week is the reference value for the adult population (34) and
- were used: a threshold of 200 µg/kg ww (41) for vulnerable populations, such as children
- 3.1. Concentrations of Hg, Cd, Pb, As, and MeHg in Fish, Fruits, and Vegetables
- rials Table S2. Based on the taxonomic identification, 19 species of fish were obtained, with
- species (111 individuals). The most common species were Prochilodus magdalenae (15.9%),
- Hoplias malabaricus (11.1%), Rhamdia quelen (10.0%), Hypostomus hondae (8.9%), and Astyanax
- fasciatus (8.6%). The concentrations of Hg were highest, followed by those of As, Pb, and
- Cd. (Table S2).
- (Table S2). Of the total fish samples for Hg and MeHg, 221 individuals (piscivores 111,
- vegetables; the species of vegetables with a total of 24 species were subdivided into 15 fruits
- and 9 vegetables. A total of 154 individual specimens are listed in Supplementary Materials,
- Table S3. Hg presented the lowest concentration in the species Citrus aurantifolia for
- species with the highest mean concentration value (Figure 3a). The minimum values for As
- The maximum mean concentrations of As were found in Murindó (60.84 ± 107.8 mg kg−1 )
- (100 mg kg−1 ) (Figure 3c). However, the mean concentrations of Hg, Pb, Cd, and As
- Cd: 0.05 mg kg−1 and As: 0.2 mg kg−1 (46) (Table S3).
- 3.2. Species of Fish, Fruits, and Vegetables Most Consumed in the Middle Basin of the Atrato River
- inhabitants of this middle area of the basin (Table S2). Among these, two species of non-
- 3.3. Determination of Human Health Risk by Fish and Vegetables Consumption
- are described in Supplementary Materials Table S1. A total of 57.9% (n = 446) of the
- and risk levels of metals for the most consumed species (Tables 1 and 2).
- 3.4. Determination of Health Risk from the Consumption of Fish, Fruits, and Vegetables
- vegetables studied, the EDI values were 0.0135 µg/kg/day (range: 7.882 × 10−5 –0.068) for
- Hg, for As 0.0595 g/kg/day (range: 0.001–0.755), for Pb 0.0235 g/kg/day (range: 5.401–0.232)
- and for Cd 0.009 g/kg/day (range: 1.322 × 10−5 –0.860). The species Musa paradisiaca presented
- As (As 0.30 g/kg/day) (Table 1).
- For fish, the mean EDI values were 1.374 µg/kg/day (range: 0.122–3.556) for Hg, for
- As 0.119 g/kg/day (range: 0.016–0.672), for Pb 0.067 µg/kg/day (range: 0.015–0.067) and,
Methods (brief)
- 154 samples of different fruits and vegetables and 440 samples of fish were analyzed by atomic
- absorption spectroscopy. A sample of 446 people were surveyed to evaluate food consumption and
- 440 individuals of 19 fish species were collected. The carnivorous species (330 individuals)
- were Argeneiosus pardalis, Pimelodella chagresi, Rhamdia quelen, Trachelyopterus fisheri, Pimelo-
- Caquetaia kraussii, Caquetaia kraussii, Caquetaia kraussii, and Pimelodus punctatus, Leporinus
- muyscorum, Caquetaia kraussii, Ctenolucius beani, Pseudopimelodus schultzi, Sternopygus aequil-
- Geophagus Pellegrini, and Pimelodus sp. The non-carnivorous (110 individuals) were Prochilo-
- dus magdalenae and Hypostomus hondae. The fish samples were placed in polyethylene
- at each sampling point. A total of 154 individual samples were collected and classified
- Quantities of 0.02 g of freeze-dried fish and plant material samples were analyzed
- for Hg concentration levels by atomic absorption spectrometry using a direct mercury
- analyzer (DMA-80 TRICELL, Milestone Inc, Italy) using the established EPA Method 7473.
- by Karadede and ÜnlÜ (31) were used, respectively. The samples were digested with
- of each fish and plant material sample with Mg (NO3 ) 2 at 550 ◦ C in a muffle furnace, then
- (Szkoda et al., 2006). A Thermo Scientific iCETM 3500 AAS atomic absorption spectrometer,
- As analysis (HGAAS; standard Methods SM 31114, 2017). Certified µreference materials
- for Pb, and 0.016 µg g−1 for As. MeHg analysis was only performed on the fish samples; for
- L-cysteine. Finally, a 100 µL aliquot of the aqueous phase was injected into DMA (32).
Implications
This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.
Wiki pages this source may touch
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Root-Vegetable Purees
- Mercury
- Mercury
- Cadmium
- Lead
- Arsenic
Verification notes
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Update history
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