Overview
This source page is a mechanical bulk-ingest record for a PDF in the methylmercury infant-formula research pull. 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:
- Quality Assurance and Safety of Crops & Foods, 2023; 15(3): 22–35
- Genxin Nie1,2, Tianhua Tu1,2, Lifang Hu1,2, Ling Wu3, Yaomin Zhou1,2*
- China; 2Key Laboratory of Quality and Safety of Agricultural Products of Jiangxi Province, Nanchang, China; 3Institute of
- (Pb) in soil were 5.99, 0.373, 17.8, 5.94E-02, and 28.9 mg kg–1, respectively; Cd exceeded the background value
- etables was 0.204 mg kg-1, with the highest concentration of Cd (0.147 mg kg–1) in Ganzhou leafy vegetables. The
- Hg concentration of leafy vegetables in Jiujiang was 1.41E-02 mg kg–1, which exceeded the maximum limit. The
- bioconcentration factor of HMs was negatively correlated with pH (P ≤ 0.05). The migration ability of Cd in root
- vegetables was 1.7-fold to that of leafy vegetables, and was strongest. The TTHQ of all vegetables was less than
- 1.0, which indicated that there was no significant noncarcinogenic risk in adults. The TTHQ of root vegetables
- factors (Wang et al., 2021; Wen et al., 2020). Researchers
- sources of food for humans (Wang et al., 2022). Heavy and vegetables. HM pollution in vegetables has been fre-
- soil and may cause potential risks (Tariq et al., 2019). In etables is a possible threat to human health (Tariq, 2021).
- 22 ISSN 1757-837X online, DOI 10.15586/qas.v15i3.1222
- et al., 2018; Gupta et al., 2021; Hossain et al., 2021; Ji et al., the noncarcinogenic risk assessment of vegetables. The
- 2018; Liu et al., 2021; Quispe, 2021; Tomno et al., 2020). results showed that Cd and Hg were the primary pollut-
- bles, and vegetable intake health risks are unacceptable collecting data, Meng et al. (2021) evaluated the soil and
- (Su et al., 2023). Vegetables pose a noncarcinogenic health vegetables in Chinese greenhouses using transfer factor
- risk because of HMs (Sadee and Rasul, 2022). and target hazard quotient (THQ), and found that the
- China’s vegetable production and consumption is Cd in spinach should be considered. Gupta et al. (2019)
- of polymers (Yuan et al., 2022). These are hard to degrade more than 1 because of the consumption of fenugreek
- cesses (O’Kelly et al., 2021). They are carriers for organic less than unity because of the consumption of eggplant
- pollutants and HMs (Bhagat et al., 2021). They affect the and chilli. Jalali and Meyari (2022) evaluated the trans-
- biophysical properties of the soil (Yang et al., 2021) and fer factor and health risk of soil and vegetables in west
- effects (Kumar, et al., 2022). At the same time, multiple (RI) values for adults were less than 1, except for Cd
- cropping and excess chemical fertilization have led to and Pb. Birghila et al. (2023) evaluated the transfer fac-
- pollution problems (Chen et al., 2021; Huang et al., 2018; tor and health risk of the soil and tomato in southeast-
- Kianpoor Kalkhajeh et al., 2020), and HM pollution in ern Romania. The BCF was less than 1, indicating that
- al., 2017). Concentrations of Cd and Pb being 72.4% and index value were below the acceptable level. Laboni et al.
- 35.5%, respectively, in the soil samples have exceeded (2023) evaluated vegetables grown in the industrial areas
- maximum limits in northern China (Fan et al., 2017). Cd, of Bangladesh, and found THQ < 1.0, indicating that it
- Hebei Province, northern China (Meng et al., 2021). Cd of historical wastewater irrigation in Kaifeng City, central
- with the maximum values being 3.77-fold higher than tion index, BCF and heath risk assessment. The Nemerow
- the limits in northwest China (Chen et al., 2021). Cr pollution index of Cd was highest, and most soil sam-
- and Pb exceeded 1.86–2.63-fold higher than the lim- ples were slightly or moderately polluted by HMs. The
- China (Wang et al., 2022). Liu et al. (2021) studied the risks (Ruan et al., 2023). Many studies evaluated the soil
- and vegetables across Chinese provinces (except Jiangxi et al. 2021; Meng et al. 2021; Su et al. 2023). It is a quan-
- significant (Bai et al., 2020), and acidic soil promotes the concentration of HMs and background value.
- enrichment of HMs (Meng et al., 2021).
- pollution in the soil and vegetables. Fan et al. (2017) ered shed vegetables. Thus, to protect the dietary safety
- tables. Sawut et al. (2018) used the Nemerow integrated acterized by strong acidity and biological enrichment.
- Quality Assurance and Safety of Crops & Foods 15 (3)23
- The aims of this research were as follows: (1) to determine
Methods (brief)
- 35.5%, respectively, in the soil samples have exceeded (2023) evaluated vegetables grown in the industrial areas
- content in some soil samples was more than the limits, China, was evaluated by the Nemerow integrated pollu-
- etable production and decreasing human health risks. Sample site
- water was used to wash vegetable samples, and vegetable
- Jiangxi Province is located in southeastern China, samples were dried at room temperature. To determine
- bounded between 113°34’36”–118°28’58” E and the concentrations of HMs, samples (0.1 g) were digested
- 24°29’14”–30°04’ 41” N. In recent years, Jiangxi has made with microwave digestion apparatus (CEM mars6, USA),
- great efforts to speed up the development of vegeta- soil samples were digested with HNO3-H2O2-HF (guaran-
- ble bases and has become the main production base for teed reagent (GR)), and vegetable samples were digested
- in northeastern, Fuzhou city in western, and Ganzhou tion of HMs was determined by ICP–MS (NexION2000,
- city in southern Jiangxi Province. PerkinElmer, USA). The operating parameters of ICP-MS
- Sample collection step length of 0.1 mL/min, RPq value of 0.45–0.80, RF
- ples were collected from plastic-covered sheds in men- reaction cell (DRC) operating parameters were as follows:
- tioned five cities of Jiangxi Province. The sample quantity mode CPV-21V, mode QRO-6.5V, and mode CRO-1V.
- sample was collected from each site with five soil and using a pH meter (s470k, Mettler Toledo, China). Quality
- vegetable subsamples. control was ensured with the use of reagent blanks and
- Sample analysis certified reference materials produced by the Institute
- Soil samples were dried at room temperature, finely Academy of Geological Sciences. Each sample was deter-
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
- Cadmium
- Lead
- Arsenic
- Nickel
- Aluminum
- Chromium
Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
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Update history
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