Skip to content
Heavy Metal Index

Mercury Dynamics in the Sea of Azov: Insights from a Mass

This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus.

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:

  • outflow from and into the Black Sea. About 90% of all riverine inflow is discharged from
  • total suspended solids (TSS, 18.1 and 125 mg/L, respectively (37,38)). The SoA receives
  • discharge into the Black Sea constitutes around 53–55 km3 /yr, while the total inflow ranges
  • 19.1 mg/L (31,40)), with an average organic carbon content of 16.5% (40). Due to the
  • large discharge of nutrients and sediment (~25.8 mg/L TSS), the river deltas not only
  • and low resuspension rate (64%), bottom sediments contain only 2.42% organic carbon.
  • mass balance (4.6%) (37,42,43).
  • increased to 6.0 ng/m3 . Further, Fedorov et al. stated that 28% of the total Hg (tHg)
  • hotspots and concentration gradients observed in empirical surveys (Table 1).
  • Table 1. Mercury concentration data from the literature for water and sediment in the Sea of Azov.
  • ance model (90%). Due to the spatiotemporal variability in water temperature andspeeds
  • model (90%). Due to the spatiotemporal variability in water temperature and wind wind
  • As documented in Table 1, Hg concentrations in water and sediment are highly
  • As documented in Table 1, Hg concentrations in water and sediment are highly de-
  • (Rutilus heckeli) between 1992 and 2012 (max. 0.1 µg/kg) and decreasing levels until 2018 (4).
  • resulting in a range of unspecific adverse effects (23,69), which could threaten the stability
  • (0.68 ppm vs. 0.17 ppm (73)). During the last 200 years, approximately 10 billion tons of
    1. Fedorov, Y.; Mikhailenko, A.; Dmitrik, L.; Dotsenko, I.; Solodko, D.; Chepurnaya, V. Mercury and Iron in Atmospheric Precipitation
  • Mercury Budget from a Coupled Atmosphere-Land-Ocean Model: 40% More Re-Emissions Buffer the Effect of Primary Emission

Methods (brief)

    1. Fedorov, Y.; Mikhailenko, A.; Dmitrik, L.; Dotsenko, I.; Solodko, D.; Chepurnaya, V. Mercury and Iron in Atmospheric Precipitation
  • Electrothermal Atomic Absorption Spectrometry. J. Anal. Chem. 2019, 74, 1184–1191. (CrossRef)

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

Verification notes

  • Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing the linked reference record pages before creation.
  • Full-PDF read: pdftotext -layout was 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

No substantive edit history is available in this build. The full commit record is available in git.