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
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- West Pomeranian University of Technology in Szczecin https://orcid.org/0000-0001-8465-7509
- License: This work is licensed under a Creative Commons Attribution 4.0 International License.
- treatment process reduced the concentrations of these compounds in water by a range of 48.5 to 97%.
- 28.6 to 60.8%. Trace element concentrations in treated sewage were below MAC values in all the samples
- tested, and were from 1.15% (Pb) to 6.23% (As) MAC for toxic elements. Concentrations of both essential
- had a significant (p<0.05) effect on decreasing concentrations of trace elements.
- Reductions in the most dangerous elements fluctuated from 48.5 (As) to 97% (Pb).
- Wastewater treatment reduced the concentration of Pb and As by over 50%.
- manganese, and copper, but it can also be a source of harmful elements (Vriens et al. 2017). Water
- techniques are combined with the aim of increasing treatment efficiency (Crini and Lichtfouse 2019).
- recovered from wastewater treatment sludge (Barakat 2011). This is why it is so important to have
- globally (Bos et al. 2016). In European Union (EU) countries, the quality of water intended for human
- consumption is regulated by Directive 98/83/WE (1998, 2015), and in Poland additionally by the
- Regulation of the Minister of Health of 2017 (Council Directive 2015; Journal of Laws item. 2294 2017).
- potentially toxic, and the high consumption of drinking water of 2.0 – 2.5 l/day (EFSA 2010).
- focused on reducing organochlorine compounds (Cybulski et al. 2021).
- 2 Materials And Methods
- 2.1 Study material
- has an area of 35 km2 and is the fifth largest in Poland and the second largest in the voivodeship. The
- that are located in the deep-profundal zone. The intakes are fitted with 40 mm mesh gratings. The raw
- (Fig. 1). The wastewater tested was from the Pomorzany Wastewater Treatment Plant, from which raw
- outflow canal. The study began in March 2017, and ran until March 2019. The parameters analyzed are
- presented in Table 1.
- Sampling was performed four times monthly. Each time, three samples of 5 l of raw water,
- elements (zinc, nickel, iron, manganese, copper, lead, and arsenic), and a total of 1,152 samples of all
- Production Plant through a pipeline fitted with a rotary 2 mm mesh capable of retaining particles larger
- coagulant (Kemipol, Poland; with the following properties – pH - 3.6±0.4; alkalinity - 85±5%, density -
- 1150 kg/m3,aluminium content - 6.0±0.5%; chlorides - 5.0±1.0%), flocculation using polyelectrolytes, and
- 2.1.2 Treating wastewaters
- years. This plant treats wastewater from approximately 50% of the urban area. The treatment stages are
- presented in Fig. 3. The wastewater treatment process utilizes two types of coagulators: PIX (Kemipol,
- Poland; PIX 113 with the following properties—total iron (Fe) 11.8 ± 0.4%; density in kg/m3 (20°C) 1500 –
- 1570; pH of less than 1— and PAX 16 (Kemipol, Poland) with the following properties—Al2O3 content –
- 15.5± 0.4%; chlorides (Cl–) – 19.0 ±2.0%; alkalinity – 37.0± 5.0%; density in kg/m3 (20°C) 1330 ± 20; pH
- pH < 2 with the aim of avoiding contamination and trace element precipitation. Additionally, immediately
- before beginning the analysis, all the samples were filtered through 0.45 μm glass fiber filter paper
- 2.2.1 Digestion and ICP-AES analysis
- to the procedure PN-EN ISO 15587-2: 2005 (Polish Norm 2005). For this, 200 ml of water was
- concentrated in quartz beakers on a heating plate, 3 ml of concentrated HNO3 (Merck, Germany) was
- added, and the solution was evaporated to dryness. For wastewater digestion, larger amounts of HNO3
- (from 5 to 20 ml) were added until the light-color of sample. The resulting pellet was dissolved in 2 ml of
- 15% HNO3 (Merck) and transferred quantitatively with deionized water (Barnstead Easy pure UV) to a
Methods (brief)
- performed with inductively coupled plasma atomic emission spectrophotometry (ICP-AES). The water
- The concentrations of trace elements (>LOD) in drinking water were below maximum acceptable
- 28.6 to 60.8%. Trace element concentrations in treated sewage were below MAC values in all the samples
- The raw water was sampled from Lake Miedwie, which is a drinking water source and the largest
- wastewater was sampled at the grating station, while treated wastewater samples were collected at the
- Sampling was performed four times monthly. Each time, three samples of 5 l of raw water,
- drinking water, raw wastewater, and treated wastewater were collected to be tested for levels of trace
- elements (zinc, nickel, iron, manganese, copper, lead, and arsenic), and a total of 1,152 samples of all
- samples were preserved with nitric acid (Merck, GmbH Germany).
- Immediately after collection, water samples were acidified with concentrated HNO3 to a solution
- before beginning the analysis, all the samples were filtered through 0.45 μm glass fiber filter paper
- 2.2.1 Digestion and ICP-AES analysis
- Water samples for determinations of the general forms of the elements selected were digested according
- added, and the solution was evaporated to dryness. For wastewater digestion, larger amounts of HNO3
- (from 5 to 20 ml) were added until the light-color of sample. The resulting pellet was dissolved in 2 ml of
- inductively coupled plasma atomic emission spectrophotometry (ICP-AES; Yobin Yvon JY-24) fitted with a
- 257.610 nm; Ni – 231.604 nm; Zn – 213.856 nm; As – 228.812 nm; Pb – 220.353. All samples were
- Fe (97.2%), Mn (99.0%), Cu (96.4%), Pb (98.6%), and As (97.7%). The limit of detection (LOD) and limit 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)
- Cadmium
- Lead
- Arsenic
- Nickel
- Aluminum
- Tin
- Chromium
Verification notes
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Update history
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