CMMMech

Millerite mineral

Millerite is the trigonal NiS mineral species, distinct from hexagonal alpha-NiS, hydrated or unresolved nickel-sulfide precursors, elemental nickel and mixed ores. The September 2026 IMA-CNMNC list gives grandfathered status and original-description year 1845; that year is not a unique approval accession. The curated mechanism concerns a synthetic mineral-assigned component of laboratory precipitates. No nickel criticality designation or industrial deployment is inherited.

Microbial & Biochemical Mechanisms (1)

Millerite-assigned nanocrystals in sulfate-reducing culture products

biomineralization Microbial

Associated Organisms: Nitratidesulfovibrio vulgaris str. Hildenborough (NCBITaxon:882)

Hildenborough cultures produced mixed nickel-sulfide particles containing a millerite-assigned crystalline component. Similar particles also appeared in abiotic preparations after aging. The accepted observation is a source-assigned phase in processed culture solids, not exclusive microbial production of pure millerite or extraction from a pre-existing millerite ore.

Experimental Context & Analytical Limits:
Mansor2019 Methods pp.3–4: the reported culture is Desulfovibrio vulgaris DSM 644, Hildenborough/ATCC 29579; current authority name is Nitratidesulfovibrio vulgaris str. Hildenborough. Anoxic modified metal toxicity medium contained lactate, sulfate, yeast extract, tryptone and HEPES, initially pH 7.2. NiCl2 and FeSO4 stocks supplied a nominal total of 500 micromolar Ni plus Fe across No Fe, 5:1, 1:1 and 1:5 Ni/Fe arms. No Fe means no intentionally added Fe stock, not a demonstrated trace-Fe-free medium. After 72 h pre-growth at 30 degrees C with shaking, 1% volume inoculum was transferred into 100 mL metal-amended medium; the actual mineral-incubation temperature and shaking rate are not restated separately. Biotic products were sampled after 6–25 days. XRD pellets were rinsed and dried on glass; TEM pellets underwent detergent, lysozyme and proteinase K treatment for 1 h at 45 degrees C, followed by washing, shipping and up to 1 h sonication. The abiotic comparison instead titrated 50 mL of 15 mM sodium sulfide at 2 mL/h into 50 mL double-strength medium, aged 5–36 days and harvested solids by filtration. This gives a nominal 7.5 mM final chemically added sulfide, not a measured biotic sulfide concentration. Final bulk pH was approximately 7.1 in biotic arms versus approximately 8.0–8.2 in abiotic arms; the arms are not matched for pH, sulfide delivery, sampling times or harvesting. These are laboratory salt-solution experiments, not treatment of an industrial waste or natural ore.
Curated Evidence Points:
Results pp.4–5 and Figure 2d–f identify increasingly resolved electron-diffraction spots in No Fe biogenic or aged abiogenic spheroids as most consistent with millerite. Figure 3 shows larger and more crystalline culture-associated particles at selected times. These results support a millerite-assigned component of the mixed products; predominantly amorphous XRD patterns do not quantify its mass fraction.
Results pp.4–5 and Figure 2a–c explicitly do not exclude alpha-NiS, godlevskite or polydymite in the diffuse-ring early precursors. The crystalline-core/amorphous-shell model partly relies on earlier studies. Neither every spheroid nor all of its material is demonstrated to be millerite; later abiotic formation shows that a millerite assignment is not a unique biosignature.
The annotated Figure 2f panel documents the reported diffraction spots, including the approximately 2.91 angstrom 101 reflection. Table S1 records the reference spacings and overlapping candidate reflections. The broad early diffraction rings alone are not phase-specific; the more resolved spots support the narrower millerite-assigned component. The Figure 5a annotation concerns a different Fe-containing mixture.
Methods pp.3–4, Table 2 and Figures 2–4: no independent bottle-replicate count or killed-cell, cell-free metabolite, pH-matched or sulfide-flux-matched comparison is reported. Table 2 n values count EDS analyses and the particle-size histograms count individual particles, not independent cultures. EDS is explicitly semi-quantitative; XRD mostly shows poorly crystalline mixtures. No phase-specific yield, isolated product purity, Ni recovery mass balance or long-term stability challenge is demonstrated.
Discussion pp.8–12 and Figures 9–11 propose acidic cell-surface microenvironments, secreted organics and altered nucleation/growth as explanations. Local pH, specific metabolites and enzymes were not directly measured in this experiment; Figure 9 is a proposed sequence and Figure 10 a literature-derived solubility model, not direct observations of a cell-local pathway. Preparation can affect phase identity: the authors observed later oxidation of some Fe-rich samples and analyzed grids within 24 h. Their short air-drying comparison does not establish that all phase formation preceded harvest. No industrial deployment or universal microbial requirement is inferred.
Context_only Source: dsm644
The DSMZ catalogue links DSM 644 to Hildenborough and ATCC 29579 under the current Nitratidesulfovibrio name. Together with NCBI strain entry 882 this grounds the reported strain label; it is not a genomic authentication of the inoculum or a separate precipitation experiment.

Sources & References

  1. ima202609: IMA-CNMNC (September 2026). The New IMA List of Minerals. Definitions p.1; Millerite row p.144: NiS, G (grandfathered), original-description year 1845.
    https://cnmnc.units.it/files/editor/IMA_Master_List_(2026-09).pdf (accessed 2026-10-14)
  2. mansor2019: Mansor, M., Winkler, C., Hochella, M. F. Jr. and Xu, J. (2019). Nanoparticulate Nickel-Hosting Phases in Sulfidic Environments: Effects of Ferrous Iron and Bacterial Presence on Mineral Formation Mechanism and Solid-Phase Nickel Distribution. Frontiers in Earth Science 7:151. DOI 10.3389/feart.2019.00151. Full primary PDF, Methods pp.3–4, Results pp.4–6, Figures 1–11, Tables 1–2 and Discussion pp.6–13.
    https://doi.org/10.3389/feart.2019.00151 (accessed 2026-10-14)
  3. mansor2019_si: Mansor et al. (2019), associated Supplementary Material, Table_1 DOCX. DOI 10.3389/feart.2019.00151.s001; Frontiers Figshare article 8323754, file 15598037. Nine annotated diffraction panels and Table S1.
    https://doi.org/10.3389/feart.2019.00151.s001 (accessed 2026-10-14)
  4. taxonomy_hildenborough: NCBI Taxonomy 882 — Nitratidesulfovibrio vulgaris str. Hildenborough, strain rank; historical Desulfovibrio vulgaris ATCC 29579 name retained as equivalent.
    https://www.ncbi.nlm.nih.gov/Taxonomy/Browser/wwwtax.cgi?id=882&mode=Info (accessed 2026-10-14)
  5. dsm644: DSMZ catalogue DSM 644 — Nitratidesulfovibrio vulgaris, Hildenborough; lists ATCC 29579, NCIMB 8303 and VKM B-1760. Current name and collection equivalence, not an independent authentication of the experimental inoculum.
    https://www.dsmz.de/collection/catalogue/details/culture/DSM-644 (accessed 2026-10-14)

Curation History

Timestamp Curator Action Summary
2026-10-14T10:05:48Z codex (GPT-6) CREATE Created an evidence-backed mineral record from current IMA identity and full Mansor2019 primary study with its diffraction supplement; retained mixed-phase, abiotic, preparation, replication and mechanistic uncertainties. This shares one experiment with the other round68 nickel-sulfide owners.

Record source: data/records/millerite.yaml