Overview
This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus. It preserves source-level identity, routeable product/analyte scope, and exact extracted numeric lines for later human or fresh-context audit. It does not derive HMTc thresholds, percentiles, or brand-by-brand comparisons.
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:
- enderun Bay, where male shrimps exhibited concentrations (1.209 mg/kg wet weight)
- across all stations, with several samples surpassing EU maximum levels (0.50 mg/kg).
- was precisely weighed and transferred into digestion vessels. A mixture of 5 mL of 65%
- HNO3 and 1 mL of 37% HCl was added to each vessel (the addition of HCl ensured the
- and reference doses (RfD) used in these calculations are summarized in Table 1.
- version factor of 10% was applied to the total arsenic concentrations for the CR calculations,
- and Pb were 1.5, 0.01, 0.5, 1.7, and 0.38 mg kg−1 day−1 , respectively. The acceptable
- Table 1. Parameters and values used for THQ and CR calculations.
- Cu = 0.04; Fe = 0.7; Mn = 0.14; Zn = 0.3; Hg = 0.0001; Se = 0.005;
- centration (mg/kg) of each element by its respective atomic weight (Se: 78.96 g/mol; Hg:
- Table 2. Mean weights (g), total lengths (cm), and meat yield (%) of green tiger shrimp (P. semisulcatus).
- multiple range test (p < 0.05); values sharing the same superscript letter are not significantly different (p > 0.05).
- 58.00 ± 12.66 g, significantly surpassing the males (33.50 ± 5.35 g). As shown in Table 2,
- tably, males at Station 1 and Station 4 exhibited the highest meat yield percentages (59.84%
- TL, MW, and % MY columns in Table 2, reflecting the absence of significant station-based
- The mean concentrations of 12 analyzed metals (As, Cd, Co, Cr, Cu, Fe, Hg, Mn, Ni, Pb,
- Table 3. Mean concentrations (mg/kg wet weight ± SD) of analyzed metal(loid)s in the muscle tissue
- 1: Bozyazi; 2: Silifke; 3: Karatas; 4: Iskenderun. ♀: Female; ♂: Male; Values are expressed as Mean ± Standard
- 0.855. The mean As concentrations in the muscle tissue of P. semisulcatus ranged from
- 1.83 ± 0.22 mg/kg (Karatas, Female) to 5.66 ± 0.67 mg/kg (Silifke, Female). The highest
- with males in Iskenderun reaching 5.61 ± 0.73 mg/kg (Figure 2). Specifically, the lowest
- Figure 2. Mean As concentrations (mg/kg wet weight) in the muscle tissue of P. semisulcatus by
- Cd level was measured in males (0.041 ± 0.005 mg/kg). Across all sampling stations and
- sexes, Cd concentrations ranged from 0.014 ± 0.001 mg/kg to 0.041 ± 0.005 mg/kg.
- (1.209 ± 0.15 mg/kg), which was substantially higher than the levels observed in females
- at the same station (0.128 ± 0.01 mg/kg) (Figure 3). This significant difference indicates
- (0.147 ± 0.02 mg/kg) and Iskenderun females (0.128 ± 0.01 mg/kg).
- Figure 3. Mean Cd and chromium Cr concentrations (mg/kg wet weight) in the muscle tissue of
- the model explains approximately 90.7% of the total variance in Cu concentrations.
- (Karatas, Male) to 8.32 ± 1.00 mg/kg (Bozyazi, Male) (Figure 4). Notably, Cu concentrations
- were distinctively higher in Bozyazi (7.97–8.32 mg/kg) compared to other stations, which
- (18.18 ± 2.32 mg/kg), followed by Bozyazi males (18.05 ± 1.89 mg/kg). In contrast, the
- lowest Fe levels were measured in Karatas females (0.32 ± 0.03 mg/kg) (Figure 5).
- R2 = 0.998). Hg concentrations in Iskenderun (0.009 mg/kg) were approximately 9 times
- higher than those measured in Bozyazi (0.001 mg/kg).
- Figure 5. Mean Fe and Hg concentrations (mg/kg wet weight) in the muscle tissue of P. semisulcatus
- significant (p = 0.141), which is reflected by the lack of differentiating superscripts in Table 3.
- Figure 6. Mean Pb and Zn concentrations (mg/kg; wet weight) in the muscle tissue of P. semisulcatus
- in Bozyazi females (16.44 ±1.99 mg/kg) and Iskenderun females (15.95 ± 2.05 mg/kg)
- females (0.141 ± 0.01 mg/kg). Ni concentrations followed a similar pattern of geo-
- (0.403 ± 0.05 mg/kg) and Bozyazi females (0.384 ± 0.04 mg/kg) (Figure 7).
- Figure 7. Mean Mn, Ni, and Se concentrations (mg/kg wet weight) in the muscle tissue of
Methods (brief)
- across all stations, with several samples surpassing EU maximum levels (0.50 mg/kg).
- and metalloids in the edible tissues of female and male P. semisulcatus individuals collected
- were collected using commercial trawling nets. To ensure statistical robustness and compare
- biological variables, approximately 30 individuals were collected from each station, with
- Immediately after collection, the samples were rinsed with ambient seawater to remove
- mogenized. This procedure resulted in a total of 8 composite samples (4 stations × 2 sexes).
- 2.2. Microwave Digestion Procedure
- Sample preparation was performed by acid decomposition of the tissue matrix using
- a microwave digestion system (Berghof MSW-4, Eningen, Germany). From each of the
- 8 composite homogenized samples, approximately 250 mg (wet weight) of the tissue
- was precisely weighed and transferred into digestion vessels. A mixture of 5 mL of 65%
- The digestion process was carried out according to a specific multi-step thermal program:
- Following digestion, the resulting solutions were diluted to a final volume of 10 mL
- Spectrometry (ICP-MS) instrument (Perkin Elmer NexION 350X, Waltham, MA, USA). The
- 1.2 L/min, and nebulizer gas flow of 0.68 L/min. The sample uptake rate was maintained
- acceptable limits. All samples were analyzed in triplicate to verify reproducibility. The
- limits of detection (LOD) and quantification (LOQ) were calculated as three and ten times
- of the analyzed samples, the Target Hazard Quotient (THQ) was calculated for individual
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)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Mercury
- Mercury
- Cadmium
- Lead
- Arsenic
- Nickel
- Chromium
Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
wiki/sources/pages before creation. - Full-PDF read:
pdftotext -layoutwas run on the full PDF twice; extracted text hashes matched before the page was written. - Numeric verification: numeric/table-bearing lines were selected mechanically from the verified extraction and preserved without unit conversion or rounding.
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- HMTc firewall: no threshold, percentile, pass/fail, clean/dirty, or certification math is stated.
Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and 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.