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:
- solution. 5.4 mL of 65% nitric acid was added to a separate 500 mL volumetric flask, and
- the final volume was adjusted to 500 mL with distilled water to prepare a 1% nitric acid
- and urine measurements are provided in Table 1. The analytical method was fully validated
- for As and Pb were found to be within acceptable ranges (15,16). In addition, interference
- dance with international bioanalytical method validation guidelines (16). Briefly, LOD
- (LOD = 3 × SD/S), while LOQ was calculated as ten times the SD divided by the
- slope (LOQ = 10 × SD/S). These calculations were based on at least six replicate mea-
- Table 1. LOD and LOQ values.
- As_ppb (µg/L) 0.040 0.025 0.025 0.050 0.050 0.050
- Hg_ppb (µg/L) 0.010 0.010 0.010 0.025 0.025 0.025
- Cd_ppb (µg/L) 0.010 0.010 0.010 0.025 0.025 0.025
- Cr_ppb (µg/L) 0.018 0.025 0.012 0.025 0.040 0.020
- Se_ppb (µg/L) 0.600 0.500 0.050 1.200 1.800 0.100
- Mo_ppb (µg/L) 0.020 0.018 0.020 0.040 0.050 0.050
- Mn_ppb (µg/L) 0.050 0.050 0.010 0.075 0.075 0.015
- Co_ppb (µg/L) 0.020 0.030 0.030 0.025 0.050 0.050
- mass-to-charge (m/z) range extended from 7 to 240, which encompasses the target analytes
- High-purity argon gas (purity ≥ 99.999%) was used as the plasma, auxiliary, and
- sample. When working with urine samples, the device was washed with 1% nitric acid
- (LSD) test. Results are presented as mean ± standard deviation (SD). A p value of <0.05 was
- the study group were recorded (Table 2). A total of 29 females and 54 males were in-
- face area in males, indicating a homogeneous community (Table 2). Participants were
- Table 3. Gender-based distribution of smoking status among study participants.
- Table 4. Mean values of heavy metals in blood and urine.
- As (µg/L) Whole blood 0.40 ± 0.10 1.0 **
- Hg (µg/L) Whole blood 0.19 ± 0.11 4.36
- Cd (µg/L) Whole blood 0.12 ± 0.05 1.44
- Cr (µg/L) Whole blood 0.71 ± 0.37 0.62
- Table 5. Mean values of trace elements in serum and urine.
- levels were found to be below the MAL values reported in the NHANES data (Table 4),
- within their respective normal limits (Table 5). Additionally, participants were stratified by
- Table 6. Comparison of heavy metal and trace element concentrations with published data.
- participants compared to our study (Table 6). Over time, a decline in lead exposure has
- reported in previous international studies (Table 6). Blood and urinary arsenic levels in
- (CHMS) data (Tables 4 and 6). Arsenic levels can vary, which is attributed to regional
- accepted limits (Table 4). Compared with previous international and national reports,
- population (Tables 4 and 6). This low mercury exposure in our study population may
- are reported as 0.4–1 µg/L and 1.4–4 µg/L, respectively (54). However, under conditions
- of environmental exposure, these levels may exceed 10 µg/L (54) Previous studies have
- groups (Table 6). In our study, although there was a clear difference in cadmium levels
- normal human MAL reported by the NHANES (Table 4) and was higher than the values
- reported for the Canadian population (Table 6), indicating relatively elevated exposure
Methods (brief)
- were measured in participants’ whole blood, serum, and urine samples using the ICP-MS
- females (p < 0.05). When serum samples were analyzed, males had significantly higher
- copper (p < 0.05) and cobalt (p < 0.05) were observed in urine samples, with higher levels
- Keywords: heavy metal; trace element; ICP-MS; arsenic; mercury; young adult
- of approximately 16 million, making it the most populous city in Turkey. Sample collec-
- Figure 1. Sample collection region.
- 2.2. Sample Collection
- 10–12 h fasting period, venous blood was collected in 3 mL K2 EDTA tubes for whole blood
- urine samples were collected in sterile urine containers. We required a 10–12 h overnight
- fasting period prior to sample collection in order to minimize the potential influence of
- and trace elements. All the samples were collected within three days, and participants
- Immediately after sample collection, participants completed a detailed 24-question survey,
- 2.3. Sample Preparation
- Blood samples collected in trace element tubes (trace element tubes are specially de-
- tubes. Urine samples were also transferred from sterile urine containers to numbered sterile
- samples were transferred to the laboratory in foam boxes with ice packs. The samples were
- All metal measurements were performed using an Agilent Technologies 7500c ICP-
- LOD (Limit of Detection) and LOQ (Limit of Quantification) values for whole blood, serum,
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)
- Mercury
- Mercury
- Cadmium
- Lead
- Arsenic
- 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.
- Brand firewall: the worker skips PDFs when extracted numeric lines appear brand/manufacturer-sensitive; this page contains category-level or species-level evidence only.
- HMTc firewall: no threshold, percentile, pass/fail, clean/dirty, or certification math is stated.
Update history
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