| Literature DB >> 27492071 |
W Montgomery1, G D Bromiley2, M A Sephton1.
Abstract
Impact ejected rocks are targets for life detection missions to Mars. The Martian subsurface is more favourable to organic preservation than the surface owing to an attenuation of radiation and physical separation from oxidising materials with increasing depth. Impact events bring materials to the surface where they may be accessed without complicated drilling procedures. On Earth, different assemblages of organic matter types are derived from varying depositional environments. Here we assess whether these different types of organic materials can survive impact events without corruption. We subjected four terrestrial organic matter types to elevated pressures and temperatures in piston-cylinder experiments followed by chemical characterisation using whole-rock pyrolysis-gas chromatography-mass spectrometry. Our data reveal that long chain hydrocarbon-dominated organic matter (types I and II; mainly microbial or algal) are unresistant to pressure whereas aromatic hydrocarbon-dominated organic matter types (types III and IV; mainly land plant, metamorphosed or degraded, displaying some superficial chemical similarities to abiotic meteoritic organic matter) are relatively resistant. This suggests that the impact excavated record of potential biology on Mars will be unavoidably biased, with microbial organic matter underrepresented while metamorphosed, degraded or abiotic meteoritic organic matter types will be selectively preserved.Entities:
Year: 2016 PMID: 27492071 PMCID: PMC4974657 DOI: 10.1038/srep30947
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.379
Figure 1Total ion current chromatograms of pyrolysis products of type I, II, III, and IV organic materials before (initial) and after (final) pressure treatment.
Type I and II organic materials are rich in straight chain hydrocarbons and are destroyed by pressure treatment. Type III and IV organic materials are rich in cross linked aromatic units and are relatively resistant to pressure. Type III and IV organic materials or are more likely to survive impact ejection from the subsurface.
Figure 2Extracted ion chromatograms (m/z 57) of pyrolysis products of type I, II, III, and IV organic materials before (initial) and after (final) pressure treatment.
The m/z 57 ion selectively highlights the presence of aliphatic hydrocarbons and displays the susceptibility of straight chain hydrocarbons to destruction by pressure (present in the initial samples but absent in the final pressure treated samples). The series of peaks in the starting materials represent n-alkene/n-alkane doublets, which are the pyrolysis products of high molecular weight aliphatic networks. All vertical scales have been expanded x20 relative to Fig. 1.
Compound identifications in pyrolysis products of types I to IV organic materials both before and after high pressure treatment.
| Sample | Before pressure treatment | After pressure treatment |
|---|---|---|
| Type I | C9-C35 alkenes/alkanes | toluene (contaminant) |
| C9-C34 alkenes/alkenes | decane (contaminant) | |
| pthalic acid ester (contaminant) | ||
| Type II | C9-C25 alkenes/alkanes | toluene (contaminant) |
| C1-thiophenes | decane (contaminant) | |
| C2-thiophenes | pthalic acid ester (contaminant) | |
| C3-thiophenes | ||
| C4-thiophenes | ||
| C5-thiophenes | ||
| C3-benzenes | ||
| C4-benzenes | ||
| benzothiophene | ||
| Type III | C5-C30 alkenes/alkanes | dichloromethane (contaminant) |
| C9-C34 alkenes/alkenes | decane (contaminant) | |
| toluene | pthalic acid ester (contaminant) | |
| phenol | C22-C26 alkenes/alkanes | |
| C2-benzenes | toluene | |
| C3-benzenes | naphthol | |
| C1-phenols | C1-naphthols | |
| C2-phenols | xanthene | |
| naphthalene | anthracene | |
| C1-naphthalene | phenanthrene | |
| C2-naphthalene | C1-anthracene | |
| C3-naphathalene | ||
| Type IV | benzene | dichloromethane (contaminant) |
| toluene | decane (contaminant) | |
| C1-thiophene | pthalic acid ester (contaminant) | |
| C2-benzenes | benzene | |
| C3 benzene | toluene | |
| phenol | C2-benzenes | |
| methoxy-methyl benzene | naphthalene | |
| C1-phenols | C2-naphthalenes | |
| benzofuran | phenanthrene | |
| C2-phenols | ||
| naphthalene | ||
| C4-phenols | ||
| C1-naphthalenes | ||
| dibenzofuran | ||
| xanthene |
Note that background contaminants become more prominent when the indigenous material has been removed.
Details of samples used for the high pressure experiments.
| Sample | Location | Age | TOC (%) | VRo% | Ref. | |
|---|---|---|---|---|---|---|
| Type I | Lacustrine shale | Port Edgar, west Lothian, Scotland, UK | Carboniferous | 13.43 | 0.9 | |
| Type II | Marine shale | Monmouth Beach, Dorset, UK | Jurassic | 8.14 | 0.6 | |
| Type III | High volatile bituminous coal | Schwalbach Coal Seam, Ensdorf Colliery, Saarland, Germany | Carboniferous | 56.4 (C%) | 0.79 | |
| Type IV | Charcoal | Wealden Beds, Durdle Door, Dorset, UK | Cretaceous | 100 | — |