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:
- mg/kg) > European eel (0.160 mg/kg) ≈ roach (0.100 mg/kg) (P<0.05). A positive correlation was found between the mercury content and
- and decreases the phospholipids, cholesterol, and esteri- The detection limit (LOD): 0.02 μg/kg.
- blood vessels (Ulbricht and Southgate, 1991; Monteiro recovery rate of Hg: 100.2% (n=4).
- diovascular health (CVH). EPA + DHA (eicosapentae- X(%) = (b – c/a – c) × 100
- Linnaeus, 1758) (n=14), Eurasian perch (Perca fluvia- The content of fat (%) was calculated according to the
- in the Warmia and Mazury region (the north-east of Po- X(%) = ((b – a) × 100) / c
- tograph with a flame-ionization detector (FID) under the RfD – the oral reference dose (RfD = 3.00E-04 mg/kg/
- Total length (cm) 27.06±4.81 0.9459 0.8580 Data are presented as means ± standard deviation
- (±SD, n=14). Analysis of the results was performed us-
- Hg (mg/kg) 0.8580 0.9473
- European eel (n=14) was confirmed by Shapiro–Wilk test and the homogene-
- Hg (mg/kg) 0.8509 0.8163
- Water (%) component analysis (PCA) and a 2-D Biplot were pre-
- Hg (mg/kg) 0.8631 0.9227
- (34.52 g/person/day; BW – the average body weight (70 higher amounts of mercury (0.297 mg/kg) than other
- Target hazard quotient (THQ) (Ahmed et al., 2016) eel having a slightly higher content (0.160 mg/kg)
- than roach (0.100 mg/kg). In all cases, there was
- Table 1. Nutritional indices
- FLQ Flesh-lipid quality 100 × (EPA+DHA)/(% of total fatty acids) (Abrami et al., 1992; Senso et
- PI Peroxidizability index 0.025× (%monoenoic)+1×(%dienoic)+2×(%trienoic)+ (Zula et al., 2021)
- Health risk assessment (P>0.05) (Table 4). The percentage of MUFA in mus-
- permissible standards of 0.5 mg/kg for roach and perch, lar trend was observed in the case of ∑ HUFA (highly
- Figure 1. Interspecific differences (mean ± SD) in the concentration of mercury in fish examined.
- Table 3. The hazard quotient calculated for mercury content in the muscle tissue of fish
- THQ – target hazard quotient; RfD – oral reference dose (mg/kg/day) (US EPA 2022); HI – hazardous index; BRQ – benefit–risk quotient;
- Table 4. Fatty acid contents (% of total fatty acids) and nutritional indices in the muscle lipids of the studied fish
- Table 5. Fatty acid contents (expressed as mg/g of muscles) and indices of the studied fish
- and roach (P>0.05) (Table 4). The opposite regularity significant differences between the fish studied.
- of muscles) than other fish examined (P≤0.05) (Table 5). tion of mercury in predatory fish is higher than in ben-
- (Table 6). For Factor 2, a significant correlation between of roach from Vistula Lagoon (Poland) and feeding on
- cumulates and biomagnifies easily in the food chain, (north-eastern Poland) was 0.415 mg/kg (Luczynska et
- Table 6. Values of the charge factors and their respective contribution to the total variance after performing a PCA analysis (Principal compo-
- 0.10 and 1.23 mg/kg (Rask et al., 2021). According et al. (2021) found that predatory fish such as perch
- varied at three sites (river, lake and Gulf of Riga) and tion of mercury in their muscle tissue (0.216 mg/kg)
- was 188.2, 154.2 and 110.8 µg/kg, respectively. The compared to non-predatory fish like roach (0.123 mg/
- this species to inhabit a wide range of feeding grounds Luczynska et al., 2020).
- Table 7. Review of nutritional indices in the muscle lipids of different fish species
- connected with the Sawica River (north-eastern Poland) perch and other fish (Bulgaria) was below 0.5 mg/kg as
- ska et al., 2023). In Table 2, a stronger correlation was by various health organizations and is acceptable for hu-
- term use of fish for food purposes and the risk of mer- the abundant group of fatty acids was SFA (48.43%), fol-
- cury bioaccumulation to human health should be taken lowed by MUFA (28.05%), n-6 PUFA (16.87%) and n-3
- into account in the case of the consumption of these fish PUFA (5.72%). The ratio of n-3/n-6 was less than 1.0
Methods (brief)
- atomic absorption thermal decomposition using Milestone DMA-80 (Italy), whereas fatty acids were measured by gas chromatography
- dex, whereas the saturated fatty acids C12:0, C14:0 and performed on disposable plastic plates. The samples were
- rated) and anti-thrombogenic fatty acids (monounsaturat- tion thermal decomposition using Milestone DMA-80
- saturated fatty acids (PUFA/SFA) ratio. This is because able autosampler. Total mercury was measured under the
- and decreases the phospholipids, cholesterol, and esteri- The detection limit (LOD): 0.02 μg/kg.
- dices, PUFA/SFA, AI, TI, HH (hypocholesterolemic/ Approximately 1 g samples (± 0.0001 g) in duplicate
- are rich in n-3 PUFAs. analyzed sample before drying (g); b – mass of a quartz
- The aim of the research was to determine the ben- evaporation dish with the analyzed sample after drying
- contamination of the tested species with mercury. In ad- Approximately 1 g samples (±0.0001 g) in duplicate
- the concentration of this metal in the muscles of fish was ter drying, the samples were transferred to glass tubes with
- Sampling and sample preparation collected in the tank. Fat was dried in a beaker at 100°C to
- Linnaeus, 1758) (n=14) were sampled from a reservoir
- ble 2). Muscles (without skin) from the dorsal part were extracted fat (g), c – weight of samples (g).
- (100:100:1 v/v) (Zegarska et al., 1991). All samples were BW – the average body weight of local residents (70 kg);
- peaks in the test sample.
- The THQ and HI as individual foodstuffs collected from discriminating between feeding behaviors and determin-
- Balzani P., Haubrock P.J., Russo F., Kouba A., Haase P., Vesely L., Fernandes Azevedo B., Barros Furieri L., Peçanha F.M., Wiggers
- ron. Res. Public Health, 17: 2545. tion, fatty acid profile and total amino acid contents in samples of
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, predatory (tuna, swordfish, shark, king mackerel)
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Mercury
- Mercury
- Cadmium
Verification notes
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Update history
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