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:
- 94 Even though the median Pb isotope ratio of the honey samples (median 206Pb/207Pb ratio of
- 123 A large range of elements were analyzed on the diverse samples collected in NDdP: the
- 128 building, the Pb stable isotope ratio was also measured on “construction” Pb samples from
- 160 substrates (wood, metal, glass, fabric – described in Table S1) at the ground and first floors
- 168 revealed dust trapped in a fiber aggregate (Table S1). The two different matrices were
- 174 using a chisel at 2 sites of the vaults (Table S1). To summarize, 23 samples are analyzed in this
- 178 in the studied buildings: Chartres cathedral (n=14) and the Sainte-Chapelle of Paris (n=8).
- 187 65-71% HClO4: TraceMetal grade, Fisher Scientific). The first step consisted of adding 4 mL HF
- 203 analyzed and its interferants (Table S2). The certified riverine water standard SRM-1640a
- 206 obtained for the CRMs were within 15% of the certified values, and within 10% (except Mg
- 207 and Al: 30 %) for BCR-723 and SL-1, respectively. The standard deviation (SD) was lower than
- 208 5% except for Ag (10 %). For more details, see the Supporting Information.
- 216 ± 0.0008. The 2σ errors (2SD) of isotope ratios are 0.29% and 0.27% for the 206Pb/207Pb and
- 220 0.13% and 0.09%, 0.16% and 0.16%, for IAEA lake sediment SL-1 and IRMM road dust BCR-
- 231 isotopic ratios are better than 250 ppm (2SD). The 208Pb/206Pb and 206Pb/207Pb ratio results
- 235 The Pb concentrations of the NDdP samples ranged from 24.6 to 967.9 g kg -1 (median:
- 237 glass, metal substrates and the painting fragment were very close to the median value
- 244 dusts; yellow = crust; gray = metal; pink = painting; blue = fabric; green = stained glass) and the symbol
- 256 measured elements are given in Table S4.
- 260 range between 1.1584 ± 0.0040 and 1.1780 ± 0.0033 (median: 1.1684) and 208Pb/206Pb values
- 267 window and metal substrate (Figure 3; Table S4). The Pb isotope ratios of samples collected
- 272 and the color corresponds to substrate type where samples were collected in cathedral (brown =
- 273 wood; black = vault dusts; yellow = crust; gray = metal; pink = painting; blue = fabric; green = stained
- 276 The samples representative for the NDdP fire dust (n=9, see section 5.1) were also
- 278 ratios at SARM. The Pb isotopic signatures average (median values) 18.252 ± 0.001 for
- 206Pb/204Pb, 15.634 ± 0.002 for 207Pb/204Pb and 38.307 ± 0.007 for 208Pb/204Pb (Table S7).
- 281 The Pb isotopic signatures obtained in construction Pb of the Sainte-Chapelle ranged
- 282 between 1.1760 ± 0.0089 and 1.1856 ± 0.0138 (median: 1.1829) for 206Pb/207Pb values and
- 283 between 2.0736 ± 0.0086 and 2.1011 ± 0.0259 (median: 2.0828) for 208Pb/206Pb values. They
- 285 1.1793 ± 0.0065 and 1.1882 ± 0.0103 (median: 1.1858) for 206Pb/207Pb ratios and between
- 286 2.0616 ± 0.0202 and 2.0914 ± 0.0139 (median: 2.0771) for 208Pb/206Pb ratios (Table S5).
- 331 samples collected on wood furniture, the Pb concentration range was between 70.9 and 281.6
- 360 cathedral (brown = wood; black = vault dusts; yellow = crust; gray = metal; pink = painting; blue = fabric;
- 361 green = stained glass). The sample matrix is represented by the outline color of the dots; the black
- 377 median values at 1.1664 ± 0.0034 and 2.1000 ± 0.0051 respectively. These ratio values are
- 394 dust, called the “urban” Pb, is characterized by relatively high 208Pb/206Pb ratios (range: 2.088–
- 395 2.115; median: 2.107) and low 206Pb/207Pb ratios (range: 1.142–1.166; median: 1.155) (Figs 4
- 403 Chartres Cathedral; Table S5) and the 17th century (Versailles Palace; Pons-Branchu et al.,
- 405 1.1882 ± 0.0103 (Chartres Cathedral) (Table S5; Figure 5). Three of the 8 undated Pb artifacts
- 438 the concentrations of these elements are correlated (Table 1). Tin (Sn) presents also high
- 444 tables and/or the use of Sn in solder used for welding. These diverse uses of Sn may explain
- 447 environmental atmospheric particle and street dust samples Table 1). In literature, several
Methods (brief)
- 30 geochemical fingerprint of the roof lead, as well as no particle collected during the fire, were
- 36 ratios) and elemental ratios were determined in 23 Pb-rich samples collected inside NDdP. We
- 37 determined that the dust collected on wood substrates on the first floor was most
- 38 representative of fire emissions. These samples were the analyzed for the 4 Pb isotopes (204,
- 62 (Tognet and Truchot, 2019). Another study, based on the analysis of various soil samples,
- 68 of an environmental impact of the fire is less clear. The analysis of dusts and soils collected in
- 70 samples collected under the plume (van Geen et al., 2020). Nevertheless, high Pb
- 92 high Pb concentrations. Indeed honey samples were collected in Paris in the months following
- 94 Even though the median Pb isotope ratio of the honey samples (median 206Pb/207Pb ratio of
- 96 of 1.157±0.003, Ayrault et al., 2014), the Pb content of the honey collected under the plume
- 98 drawn without a comparison of the environmental samples with the fire emission signature.
- 99 Unfortunately, no atmospheric particle was sampled during the fire.
- 100 Glorennec et al. (2021) determined the Pb isotope ratio in dust collected during July
- 102 sampling method used did not allow any elemental analysis or observations of the collected
- 104 contamination of the samples with pre-fire dust. The determined fire isotopic signature
- 112 using all the available dust samples collected inside the cathedral. First, (1) we developed an
- 113 appropriate step-by-step strategy to reveal the samples most representative of the fire
- 117 samples representative of the dust emitted during the fire, we determined the geochemical
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)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Baby Wipes
- Lead
- Tin
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Update history
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