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:
- (Molnar et al. 2013). methyl bridge and two methyl groups (Table 1).
- uptake, and runoff (Arias-Estévez et al. 2008). These pro- 95 % of BPA produced in industry is used to make plastics,
- through the soil and their transfer from soil to water, air, (29 %) (RIKZ 2001; Huang et al. 2012). Due to the increasing
- Table 1 List of chemical compounds studied in the paper
- temperature (Table 2). It has low vapor pressure and does not
- route (80 %) was BPA cleavage to p-hydroxyacetophenone
- The remaining 20 % of BPA was converted into 2,3-bis-(4-
- IARC 2010) 2013b) microsomes, but only a minor pathway (less than 10 % BPA
- 2.07×10−2–0.3 (EC 2002; Table 3. Industrial activities (mainly chemical plants) and
- Units °C g/m3 Pa BPA concentrations in soils span between 0.55 and 147 μg/kg
- Table 3 BPA concentrations in various environmental matrices and in food (percentages between brackets represent the detection frequency)
- Kinney et al. (2008) Agricultural fields, USA μg/kg d.w. <32–147
- Xu et al. (2008) Golf course irrigated with reclaimed wastewater, μg/kg d.w. 0.55–2
- Gibson et al. (2010) Agricultural fields irrigated with μg/kg d.w. 1.6–30.2
- wastewater, Tula Valley, Mexico Mean 8.3
- Staples et al. (2010) Soils amended with biosolids, North America μg/kg d.w. Median 1.15
- Staples et al. (2010) Soils amended with biosolids, Europe (data collected μg/kg d.w. Median 0.24
- USEPA (2010a) Range of values in USA μg/kg d.w. 4–14
- Heemken et al. (2001) Elbe River and some of its tributaries, Germany μg/kg d.w. 66–343
- Kawahata et al. (2004) Estuarine and marine sediments from Okinawa and μg/kg d.w. <0.5–13
- Vethaak et al. (2005) Fresh, marine, and estuarine sediments, The Netherlands μg/kg d.w. <1.1–43
- Fu et al. (2007) Estuarine and marine sediments from Jiaozhou Bay μg/kg d.w. 0.7–27.3
- Pojana et al. (2007) Sediments from Venice Lagoon, Italy μg/kg d.w. <2.0–118
- Gorga et al. (2014) Ebro River basin, Spain μg/kg d.w. <0.24–100
- Stewart et al. (2014) Estuarine sediments from Auckland, New Zealand μg/kg d.w. <50–145
- Wu et al. (2013) Huangpu River and its tributaries, China μg/kg d.w. 0.96–14.44
- Gorga et al. (2015) Different rivers, Spain μg/kg d.w. <0.24–117
- USEPA (2010a) Range of mean values in USA mg/m3 0.004–1.9
- Félix-Cañedo et al. (2013) Groundwater in Mexico City, Mexico mg/m3 <0.0005–0.010 (63 %)
- Luo et al. (2014) Groundwater in Europe mg/m3 Mean 0.079, maximum 2.299
- Luo et al. (2014) Groundwater in USA mg/m3 Mean 2.550
- Table 3 (continued)
- USEPA (2010a) Range of mean values in USA mg/m3 0.012–0.14
- Félix-Cañedo et al. (2013) Surface water (dams) in Mexico City, Mexico mg/m3 <0.0005–0.007 (52 %)
- Luo et al. (2014) Canada mg/m3 Mean 0.0021
- Michałowicz (2014) Range of concentrations in rivers, Portugal mg/m3 0.029–0.098
- Xu et al. (2014) Cape D’ Aguilar Marine Reserve, Hong Kong, wet season mg/m3 0.011–0.41 Mean 0.0645
- Basheer et al. (2004) Seafood from supermarkets, Singapore μg/kg f.w. 13.3–213.1
- Sun et al. (2006) Canned vegetables, fruits, and meats from local μg/kg f.w. 32.8–164.5
- Isobe et al. (2007) Green mussel from India, Indonesia, Singapore, Malaysia, μg/kg d.w. 1.1–13.7
- Isobe et al. (2007) Tokyo Bay μg/kg d.w. 0.54–13.4
- Table 3 (continued)
Methods (brief)
- mental diffusion of CECs is the increase in the possible samples and belong to different classes of widely used emerg-
- (data collected in the period 1990–2006) 95th percentile 21
- Staples et al. (2010) Soils amended with biosolids, Europe (data collected μg/kg d.w. Median 0.24
- California irrigated with reclaimed wastewater, but the authors sediment samples collected at four stations in the Venice
- tamination due to the accumulation of BPA over time. Gibson charges; BPA was detected in seven out of eight samples at
- were measured by Heemken et al. (2001) in the Elbe River; water collected at an agriculture area of Catalonia (Spain)
- impacted sampling point, observing concentrations ranging ments in groundwater collected from agriculture sites in north-
- sediments collected in the Jiaozhou Bay (China) and at five about 12–13 mg/m3. In USEPA (2010a), the average concen-
- was detected in all samples from the bay at concentrations 0.0041 and 1.9 mg/m3, with a range of values of 0.006–
- between 2.4 and 27.3 μg/kg d.w. in samples from the river micropollutants in groundwater in England, with BPA con-
- the analyzed samples of river and coastal waters from Portugal; Many authors studied the migration of BPA and its derivatives
- municipal sewage plant. Basheer et al. (2004) collected surface 0.86 mg/m3 in drinking waters/commercial drinks from dif-
- seawater samples at different locations along the Singapore ferent countries. The highest values in canned food were due
- 2.47 mg/m3. In general, BPA concentration in samples polyethylene terephthalate films (Huang et al. 2012; Wright-
- samples. Kawahata et al. (2004) measured appreciable con- trations of BPA in seafood samples (prawn, crab, blood cock-
- centrations of BPA in water samples (between 0.036 and le, white clam, squid, fish) purchased from a local supermar-
- 0.08 mg/m3) in the most populated areas; values below detec- ket in Singapore, resulting in significant values in all samples
- (<0.009–1 mg/m3) in half of Dutch rainwater and surface samples purchased in Singapore; detectable amounts of BPA
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)
- Root-Vegetable Purees
- Baby Sunscreen, Mineral (ZnO + TiO2)
- Tin
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
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.