Abstract
The study of well-preserved organic matter (OM) within mineral concretions has provided key insights into depositional and environmental conditions in deep time. Concretions of varied compositions, including carbonate, phosphate, and iron-based minerals, have been found to host exceptionally preserved fossils. Organic geochemical characterization of concretion-encapsulated OM promises valuable new information of fossil preservation, paleoenvironments, and even direct taxonomic information to further illuminate the evolutionary dynamics of our planet and its biota. Full exploitation of this largely untapped geochemical archive, however, requires a sophisticated understanding of the prevalence, formation controls and OM sequestration properties of mineral concretions. Past research has led to the proposal of different models of concretion formation and OM preservation. Nevertheless, the formation mechanisms and controls on OM preservation in concretions remain poorly understood. Here we provide a detailed review of the main types of concretions and formation pathways with a focus on the role of microbes and their metabolic activities. In addition, we provide a comprehensive account of organic geochemical, and complimentary inorganic geochemical, morphological, microbial and paleontological, analytical methods, including recent advancements, relevant to the characterization of concretions and sequestered OM. The application and outcome of several early organic geochemical studies of concretion-impregnated OM are included to demonstrate how this underexploited geo-biological record can provide new insights into the Earth’s evolutionary record. This paper also attempts to shed light on the current status of this research and major challenges that lie ahead in the further application of geo-paleo-microbial and organic geochemical research of concretions and their host fossils. Recent efforts to bridge the knowledge and communication gaps in this multidisciplinary research area are also discussed, with particular emphasis on research with significance for interpreting the molecular record in extraordinarily preserved fossils.
Introduction
The fossil record is fundamental to our understanding of major events in the evolution of life and our planet. However, the fossil record suffers from numerous biases, and not all fossils are created equally (Allison and Bottjer, 2011). The process of fossilization is a complex interplay of biological, microbial and geochemical processes including decay and preservation through mineralization (Briggs, 2003b).
Three broad modes of fossilization have been proposed previously (Grice et al., 2019), as summarized in Figure 1. In ‘normal’ fossil preservation, the remains of dead organisms are subject to a range of complex biogeochemical processes encompassing degradation via eogenesis and diagenesis (within the water column and surface sediments), burial, microbial activity, authigenic mineralization and metagenesis (in sediments), weathering and exhumation. These processes destroy nearly all OM. In ‘selective’ fossil preservation, certain extremely resistant or recalcitrant biopolymers are fossilized. These include, for example, leaf cuticles of higher plants (Nip et al., 1986; Goth et al., 1988; Gelin et al., 1994; Grice et al., 2001, 2003) and the cell walls of marine and freshwater algae, which are relatively persistent in geological sediments. High molecular-weight (MW), aliphatic biomolecules are some of the more recalcitrant organic compounds (Tissot and Welte, 1984). Finally, a small fraction of organisms die in environments conducive to soft tissue preservation, which is termed ‘exceptional’ fossil preservation. Exceptionally preserved fossils have the potential to preserve biomarkers, and in special cases intact biolipids (e.g., sterols), which retain important information about extinct organisms and are vital for establishing paleodiets and reconstructing paleoenvironments at the microbial level (Grice et al., 2019; Tripp et al., 2022).
Figure 1
One fossilization pathway that appears to have high potential for exceptional fossilization, and therefore for soft tissue preservation, is concretion formation (Irwin et al., 1977; Martill, 1990; Briggs and Kear, 1993a,c; Bojanowski and Clarkson, 2012; McCoy, 2014; Cotroneo et al., 2016). When this process is sufficiently rapid, it decreases permeability and consequently protects OM from significant degradation, allowing ‘closed chemical system’ preservation of soft tissues (Allison and Pye, 1994; Farmer and Des Marais, 1999; McCoy et al., 2015b). This is a relatively uncommon pathway, but has led to the soft parts of various organisms being fossilized and entombed in concretions across a vast spatiotemporal range (Martill, 1990, 1993; Trinajstic et al., 2007, 2022a,b; Marshall and Pirrie, 2013; McCoy, 2014). Concretionary lagerstätten are known to represent a variety of different palaeoenvironments, from hypersaline to marine, estuarine to lacustrine, and freshwater to terrestrial (Marshall and Pirrie, 2013; McCoy, 2014), but the majority appear to pertain to transitional environments, i.e., those at the interface between the marine and terrestrial realms (McCoy et al., 2015a). Whole or parts of organisms can be preserved via several processes, including entombment or primary cementation in concretions of calcite, silica, phosphate, siderite, pyrite or dolomite, with carbonate concretions being the most common (Baird et al., 1986; Allison and Pye, 1994; McCoy, 2014). Concretions are often hosted in fine-grained sedimentary rocks like shales and mudstones (McCoy, 2014). Their relatively low permeability can effectively implement a closed chemical system, isolating the remains of the organism from other organic matter and redox influences thereby inhibiting diagenetic reactions and supporting the preservation of fossilized soft tissue (s) and biosignatures (McCoy et al., 2015a,b). Although the size of the nucleating fossil within the concretion is often the controlling factor on concretion size, this is not always the case: for example, sub-centimeter ostracods form the nuclei of multi-meter concretions in the Devonian-aged Huron Member of the Ohio Shale (Clifton, 1957).
Recently, it has been hypothesized from fossil evidence that microbial metabolic processes are responsible for the preservation and mineralization of the organic tissues in the fossil record (Briggs, 1995b, 2003a,b; Sagemann et al., 1999; O'Brien et al., 2002; Briggs et al., 2005; Raff et al., 2008). Microorganisms live both on the surface of, and within, living organisms, and they can remain active on or in a carcass well after the time of death of an organism (Allison, 1988a; Briggs, 1995b; Sagemann et al., 1999; Janssen et al., 2022). Certain microbially-induced carbonate concretions have recently been recognized for their excellent potential to sequester OM, including organic compounds preserving a direct link to their biological origins (i.e., molecular fossils or biomarkers) and often also providing valuable information about past depositional environments (Melendez et al., 2013a,b; Plet et al., 2016). Initial heterotrophic decay by microorganisms leads to the release of high concentrations of ions ranging from H+, OH−, Na+, K+, Ca2+, Mg2+, Fe3+, NH4+, S2− into their immediate environment. This can facilitate the stabilization of the remaining tissues of a carcass and can influence mineralization; thus, microbial activity can lead to excellent preservation, provided that the rate of mineralization or stabilization exceeds that of tissue decomposition (Gehling, 1999; Sagemann et al., 1999; Petrovich, 2001; Carpenter, 2005; Janssen et al., 2022). Theoretical models and experimental observations that have highlighted the role of microbes in the fossilization process have also identified the physico-chemical conditions that can inhibit microbial mineral precipitation (Gehling, 1999; Briggs, 2003a; Martin et al., 2003; Bolhuis et al., 2013; Gäb et al., 2020). The influence of microbial activities on fossilization processes occurs in the early stages of eogenesis and diagenesis (Dupraz and Visscher, 2005; Raff et al., 2013; Dang and Lovell, 2016; Janssen et al., 2022). Detailed investigations into the role of intrinsic and extrinsic microbial metabolic activities, prevalence of sites/types of fossils, role of substrate, formation controls, bio-physico-chemical environments, type of organic matrix, governing reaction kinetics and comprehensive characterization of biomolecules from nano- to micro-scales are pivotal in understanding the fossilization story over geologic timeframes.
This review discusses the study of well-preserved OM in mineral concretions and how it can provide information on depositional and environmental conditions and the evolutionary history of life on Earth. Various concretion types and their formation modes are described, as well as the variety of methodologies employed in their characterization. The review also includes examples of organic geochemical (biomarker) and isotopic studies and the enormous potential for the molecular record to reveal insights about extinct organisms. Challenges and knowledge gaps in the field are presented, along with recent efforts to bridge them.
Exceptionally preserved fossils in concretions through space and time
Fossiliferous concretions have been identified in strata ranging in age from Mesoproterozoic to Holocene (Mozley and Burns, 1993; Marshall and Pirrie, 2013; McCoy, 2014; Wang et al., 2017; Mojarro et al., 2022) as seen in Figures 2, 3 and Table 1. The Mesoproterozoic Xiamaling Formation (~1.37 giga annum [Ga]), which preserves silicified bitumen concretions in black shale and green chert, antedates the evolution of multicellular organisms. Consequently, the nuclei for these concretions are bacterial and include microbial mats (Wang et al., 2017; Liu et al., 2019; Liu A. et al., 2020). Concretion-bearing deposits are far more common in Phanerozoic deposits than in Proterozoic or older strata. In lower Paleozoic deposits, the fossils dominantly preserved in concretions are invertebrates; examples of deposits where this is the case are the upper Cambrian Alum Shale Formation of Sweden (Dworatzek, 1987; Maeda et al., 2011) and the lower Ordovician Fezouata Formation of Morocco (Gaines et al., 2012; Van Roy et al., 2015; Saleh et al., 2021). The rocks hosting the concretions in each of these cases are shales, but the concretions in the former are calcareous, whereas those in the latter are siliceous. The middle Silurian Coalbrookdale Formation of the UK (Herefordshire Lagerstätte) also preserves invertebrates with soft tissue in calcareous concretions, but the host rock in this instance is bentonite (Siveter et al., 2020).
Figure 2
Figure 3
Table 1
| Locality | Formation | Age | Preservation | Fossils present | References |
|---|---|---|---|---|---|
| Norfolk, United Kingdom | - | Holocene | Siderite, calcite and iron monosulfide concretions | Plants, Invertebrates | Pye (1984), Pye et al. (1990), Allison and Pye (1994) |
| Kangerlussuaq, Greenland | - | Holocene | Carbonate concretions in clay | Fish (capelin: Mallotus villosus) | Mojarro et al. (2022) |
| Ottawa, Canada | - | Holocene | Carbonate concretions in clay | Fish (capelin: Mallotus villosus) | Mojarro et al. (2022) |
| Kent, United Kingdom | London Clay Formation | lower Eocene | Pyrite, apatite, phosphate, and calcite concretions in clay | Plants, Invertebrates, Fishes, Reptiles, Birds, Mammals | Allison (1988b), Huggett (1994), Huggett et al. (2000) |
| Magdalena Valley, Colombia | Cretaceous black shales | Lower Cretaceous | Carbonate concretions in shales | Invertebrates, Fishes | Weeks (1953, 1957) |
| Santana Group, Chapada do Araripe, Brazil | Romualdo Formation, Santana Group | Lower Cretaceous | Carbonate concretions in mudstones/shales with minor limestone | Plants, Invertebrates, Fishes, Amphibians, Reptiles, Birds | Mabesoone and Tinoco (1973), Martill (1988, 1989, 1990, 1993, 2007), Maisey (1991), Fara et al. (2005), Varejão et al. (2021) |
| Cerritos Bayos, Chile | Cordillera de Domeyko | Upper Jurassic | Calcareous concretions in black, sandy, gypsum-rich shales | Invertebrates, Fishes, Reptiles | Schultze (1989), Arratia and Schultze (1999) |
| Posidonia Shale, Germany | Sachrang Formation | Lower Jurassic | Pyritiferous calcite concretions in shale | Plants, Invertebrates, Fishes, Reptiles | Plet et al. (2016, 2017) |
| Mazon Creek, Ilinois, USA | Francis Creek Shale Member, Carbondale Formation | Upper Carboniferous | Siderite (iron carbonate) concretions in shale | Plants, Invertebrates, Fishes, Amphibians, Reptiles | Johnson and Richardson (1966), Woodland and Stenstrom (1979), Baird et al. (1985a, 1985b, 1986), Archer et al. (1995), Clements et al. (2018) |
| Gogo Station, Western Australia, Australia | Gogo Formation | Middle–Upper Devonian | Calcareous concretions hosted in shales and siltstones with lenses of limestone | Radiolarians, Invertebrates, Fishes | Melendez et al. (2013b), Lengger et al. (2017), Trinajstic et al. (2022a,b) |
| Herefordshire, United Kingdom | Coalbrookdale Formation | middle Silurian | Carbonate concretions hosted in bentonite | Invertebrates | Siveter et al. (2020) |
| Fezouata Biota, Morocco | Fezouata Formation | Lower Ordovician | Siliceous concretions in shale | Invertebrates (anomalocaridids) | Gaines et al. (2012), Van Roy et al. (2015), Saleh et al. (2021) |
| Västergötland, Sweden | Alum Shale Formation | upper Cambrian | Carbonate concretions in black shale (‘Orsten’-style concretions) | Invertebrates | Dworatzek (1987), Maeda et al. (2011) |
| North China | Xiamaling Formation | middle Mesoproterozoic (~1.39 Ga) | Silicified bitumen concretions in black shale, green chert | Bacteria; biofilms | Wang et al. (2017), Liu et al. (2019), Liu A. et al. (2020) |
A selection of sites preserving fossiliferous concretions.
Note the broad geographic and temporal ranges of these deposits. Whether or not the concretions at these sites (or others not included in this table) were formed as a consequence of microbial activity remains to be demonstrated.
One of the most famous concretion-bearing and soft-tissue preserving fossil deposits in the world is the Middle–Upper Devonian Gogo Formation of Western Australia (Long and Trinajstic, 2010; Melendez et al., 2013b; Lengger et al., 2017; Trinajstic et al., 2022a). Fossils from this unit have provided unprecedented insights into the soft tissue anatomy and ecology of early fishes (e.g., Trinajstic et al., 2007, 2013, 2022b; Long et al., 2008, 2009; Ahlberg et al., 2009). In addition, molecular and isotopic studies of a fossil crustacean from this unit revealed the oldest intact biolipids (i.e., cholesterol) in the fossil record, as well as the entire diagenetic continuum of steroids representing transformations that occurred in the water column and in the surface sediments (Melendez et al., 2013a,b). Biomarkers such as isorenieratane indicative of green-brown sulfur bacteria (GSB) indicated the pivotal role that anaerobic photosynthesis played in the exceptional soft tissue preservation of this ancient crustacean. δ13C of cholestane (−30.5 ‰), short-chain C17/C19n-alkanes (−34.8 ‰) and phytane (−34.0 ‰) support a source from phytoplankton consumed by the crustacean; the different values for these compounds reflect differences in biosynthetic pathways for different compound classes within phytoplankton cells (Schouten et al., 1998). Strongly 13C-depleted values of long chain n-alkanes (average-40 ‰) indicate a source from autolithified sulfate reducing bacteria (SRB) involved in concretion formation (Melendez et al., 2013b).
Another world-renowned concretion-bearing fossil site is the upper Carboniferous Mazon Creek site of Illinois, USA, hosted in the Francis Creek Shale Member of the Carbondale Formation (Johnson and Richardson, 1966; Woodland and Stenstrom, 1979; Baird et al., 1985a,b, 1986; Archer et al., 1995; Clements et al., 2018). The fossils preserved at this site include exquisitely and rarely preserved jellyfish, anemones, and shark-egg sacs, among a diverse deltaic and marine flora and fauna (Baird et al., 1985a, 1986; Clements et al., 2018; Plotnick et al., 2023). Recent geochemical studies on fossils from this site have informed the debate over the phylogenetic position of the enigmatic “Tully Monster” (McCoy et al., 2016, 2020). It has also been demonstrated that the encapsulation of coprolite fossils at this site was sufficiently rapid that intact dietary sterols were preserved (Tripp et al., 2022). An abundance of cholestane (86–99% of total steranes) alongside other cholesterol-derived compounds, including unaltered 5α-cholestan-3β-ol and coprostanol, were detected within the coprolite, whereas these compounds were comparatively low in abundance in the surrounding concretionary matrix (Tripp et al., 2022). This supports the interpretation that these compounds were derived from the original fecal material, and therefore could be treated as informative of the producer’s dietary habits. Whereas these compounds were determined to be derived from animals, supporting a primarily carnivorous diet for the coprolite producer, the n-alkanes were identified as of palaeoenvironmental origin. The cholestane was slightly 13C-depleted compared to n-alkanes, of palaeoenvironmental sources, and bulk OM (Tripp et al., 2022).
Moving into the Mesozoic, the Lower Jurassic Sachrang Formation of Holzmaden, Germany (often dubbed the Posidonia Shale) has produced countless exceptionally preserved fossils in concretions, including an ichthyosaur bone that preserves intact cholesterol (Plet et al., 2016, 2017). In addition, the well-preserved internal tissue of the bone included structures that resemble white- and red-blood cells (RBCs) (Plet et al., 2017). The cell-like structures interpreted as RBCs are ~20% the size of modern mammal RBCs, and their small size was explained as an evolutionary adaptation to low atmospheric oxygen levels during the Jurassic period. However, several arguments against the interpretation of these structures as ichthyosaur RBCs have been put forth: some have noted that extant reptile RBCs are considerably larger than those of mammals, and therefore much bigger than the supposed ichthyosaur RBCs (Eriksson et al., 2022; Senter, 2022); others have observed that reptilian RBCs are nucleated, unlike non-nucleated mammalian RBCs (Eriksson et al., 2022); and still others have posited that small RBCs could be inconsistent with the pelagic, deep-diving lifestyle inferred for ichthyosaurs, a lifestyle normally accompanied by an increase in RBC size (Sander, 2021; Sander and Wintrich, 2021). The cell-like structures described by Plet et al. (2017) have alternatively been linked to degraded, collagen-rich connective tissue (Senter, 2022), although their true identity remains an open question and therefore requires further research.
Several Mesozoic deposits in the Americas are known to host fossiliferous carbonate concretions in shales [e.g., the Upper Jurassic Cordillera de Domeyko Fromation in Chile (Schultze, 1989; Arratia and Schultze, 1999); the Lower Cretaceous black shales of Magdalena Valley, Colombia (Weeks, 1953, 1957)], although perhaps the most renowned is the famous Lower Cretaceous Santana Group of northeast Brazil (Mabesoone and Tinoco, 1973; Martill, 1988, 1989, 1990, 1993, 2007; Maisey, 1991; Fara et al., 2005; Varejão et al., 2021). The preservation quality of this site is sufficiently exceptional that even the hearts of fish are fossilized (Maldanis et al., 2016).
Among Cenozoic deposits with fossiliferous concretions, the Eocene London Clay Formation of the UK is perhaps one of the best known and studied (Allison, 1988b; Huggett, 1994; Huggett et al., 2000). Concretions with organismal nuclei are also known from deposits as young as Holocene in some regions, attesting to rapid encapsulation in certain modern environments. Examples of Holocene sites yielding fossiliferous concretions include North Norfolk, UK (Pye, 1984; Pye et al., 1990; Allison and Pye, 1994), Onondaga Lake, New York (Dence, 1956; Sondheimer et al., 1966; Wilcox and Effler, 1981), and Kangerlussuaq, Greenland and Ottawa, Canada (Mojarro et al., 2022). In the case of the carbonate concretions from Greenland and Canada, the capelin fish fossils conserved within were determined to have been preserved in different depositional settings from each other, providing a unique opportunity to analyze recently formed concretions for their biomarker and fatty acid compositions (Mojarro et al., 2022). Mojarro et al. (2022) demonstrated that concretions from both sites had similar organic carbon sources and environments of deposition, but that the degree and quality of organic preservation were highly divergent: one concretion exhibited exceptional soft tissue preservation, whereas the other only showed skeletal preservation. The free and bound organic fractions of the two concretions were similarly disparate: the fossil concretion with exceptionally preserved soft tissues also contained a diversity of lipids, whereas the skeletal fossil was largely overprinted by environmental lipid signals. The δ13C of n-alkanes and fatty acids (C19-30) varied between −28 ‰ to −32 ‰, which was attributed to input from C3 plants. Short-chain fatty acids, probably of a bacterial origin (C14-18) showed lower δ values (−24 ‰ to −30 ‰).
Concretion formation mechanisms
The formation of concretions has traditionally been explained by diffusion, carbonate inter-conversion reactions, and slow three-dimensional advection of water (Berner, 1968b; Wilkinson and Dampier, 1990). Microbial processes are becoming recognized as crucial in concretion formation as well (e.g., Curtis et al., 1972; Irwin et al., 1977; Hudson, 1978; Gautier, 1982; Coleman and Raiswell, 1995; Raiswell and Fisher, 2000; Yoshida et al., 2018), and factors such as the input and decay rate of OM, carbonate saturation, porewater velocity and rate of authigenic precipitation all contribute to the exceptional preservation seen in fossil concretions (Butts and Briggs, 2011; Gaines et al., 2012; Melendez et al., 2013b; Farrell, 2014; Wilmeth et al., 2018; Grice et al., 2019; Janssen et al., 2022). Recent research has shown that microbes and their associated metabolic activities play a crucial role in the destruction, preservation and mineralization of organic tissue (s) (Allison, 1988b; Briggs, 1995a, 2003a,b; Gehling, 1999; Sagemann et al., 1999; Krause and Jachau, 2002; O'Brien et al., 2002; Briggs et al., 2005; Raff et al., 2008; McNamara et al., 2009; Janssen et al., 2022). Raff et al. (2013) and Butler et al. (2015) demonstrated that the interactions of microbes play an important role in preservation by generation of pseudomorphs which can stabilize the carcass and protect it from destruction. In another study of Eagan et al. (2017)Bacillus strains isolated from decaying shrimp (Artemia sinica) larvae and sea urchin (Heliocidaris erythrogramma) embryos were recorded to destroy the soft tissue. Melendez et al. (2013b) also showed evidence for the anaerobic recycling of crustacean organic matter through microbial sulfate reduction and photosynthesis (e.g., performed by the green sulfur bacteria Chlorobi) via biomarker analysis. In some instances, initial, rapid heterotrophic decay leads to the release of high concentrations of cations (often calcium) to the immediate environment; this may result in the stabilization and preservation of the remaining tissues, provided that the rates of the mineralization or stabilization processes remain higher than tissue decomposition (Riley, 1997; Sagemann et al., 1999; Gupta et al., 2007; Janssen et al., 2022). So, the rate of OM decay governs the rate of destruction, preservation and mineralization of organic tissues in concretion formation. The occurrence of soft tissue fossils in carbonate concretions is therefore enigmatic, as concretions are proposed to form as a result of the balanced interactions between decaying OM, microbes and the local chemical environment (Weiner and Dove, 2003; Dupraz et al., 2009; Melendez et al., 2013b).
Role of microbes in concretion formation
Biologically induced mineralization (BIM) with organic matter (OM) is the most relevant process for fossilization and has been extensively studied by researchers over the last century (Weiner and Dove, 2003; Dupraz et al., 2009; Wilmeth et al., 2018; Dong et al., 2022). BIM is the process by which microbial metabolic activities promote mineral precipitation as a result of biochemical changes around the cell surface (Dhami et al., 2013b; Zhu and Dittrich, 2016; Murugan et al., 2021). For example, hydrolysis of urea by bacterial urease leads to an increase in pH, which supports the precipitation of calcium carbonate (Dhami et al., 2013b; Zhu and Dittrich, 2016). BIM can play a role in fossilization by interacting with decaying OM, including extracellular biopolymers or by-products of the microbial metabolic processes (Weiner and Dove, 2003; Dupraz et al., 2009; Zhu and Dittrich, 2016; Wilmeth et al., 2018). The surrounding environment of this decaying OM can act as a source of ions, influencing the chemical composition of precipitated minerals by development of appropriate conditions for free cation attachment to the nucleation sites, which are often degrading OM (Reitner, 2004; Li et al., 2015; Janssen et al., 2022).
The process of concretion formation is in essence a two-step process: (1) microbial communities adhere to the substrate, leading to the formation of a biofilm; and (2) the biofilms act as a nucleation site which, in the presence of soluble calcium ions under a high pH environment, results in biomineralization of calcium carbonate (Weiner and Dove, 2003; Dupraz et al., 2009; Melendez et al., 2013b).
During BIM, biofilm formation occurs with the adhesion of microbial communities on surfaces, which combine to form clusters or microcolonies. Microcolonies progress to a threshold density and form a biofilm, which then induces the expression of biosynthesis genes that control the synthesis of extracellular polymeric substances (EPS); these EPSs then become encapsulated within the biofilm (Costerton et al., 1995; Percival et al., 2011; Janssen et al., 2022). Biomineralization usually occurs on biofilms with heterogeneous structures because of cell aggregation (Li et al., 2015). With these differential structures, the microenvironment both within and external to the biofilm is modified to facilitate mineralization (Iniesto et al., 2015, 2016, 2018). For example, the biofilm formation of Pseudomonas aeruginosa accumulates minerals on the inside and outside of the biofilm by trapping fine abiotic calcite particles as well as granules of calcite through biomineralization (Bai et al., 2017). Biofilms are also known to exhibit diverse and highly structured microenvironments resulting from a combination of microbial metabolism and transport limitations (Stewart and Franklin, 2008). Li et al. (2015) demonstrated different patterns of biomineralization in situ with precipitation starting at the base of the biofilm and building upwards which impacts mineralization. Ex situ studies suggest that the extracellular polymeric substances (EPS) produced by biofilms influence precipitation and regulate patterns of mineralization (Ercole et al., 2007). Biofilm morphology also regulates the internal and external solute transport mechanisms, which determines the physiology of the biofilm-resident cells. Previous studies have demonstrated that microbial biofilms surrounding dead and decaying biomass also act as a template for carbonate precipitation and concretion formation (Iniesto et al., 2015, 2016).
Mineralization requires supersaturation of specific ions in the surrounding environment which can be governed by microbial activity in and around the cadaver immediately upon death. Depending upon the availability of organic substrates and cations, different mineralization reactions can occur, including silicification, phosphatization, pyritization or carbonate precipitation (Briggs et al., 1996; Grimes et al., 2001; Dornbos, 2011; Gaines et al., 2012; Farrell, 2014; Liu D. et al., 2020; Janssen et al., 2022). Among these, carbonates are the most commonly precipitated biominerals (Thompson et al., 1997; Grotzinger and Knoll, 1999; Zhu and Dittrich, 2016).
Microbial function and metabolic activity in biomineral precipitation (especially carbonates) can be grouped into three categories (Figure 4):
Precipitation of microbial metabolic pathway by-products. Metabolic pathways like photosynthesis, sulfate reduction, denitrification, anaerobic sulfide oxidation, ureolysis and methanogenesis might circumstantially lead to mineralization (Konhauser et al., 2005; Zhu and Dittrich, 2016; Zeng and Tice, 2018). The significance of SRB, iron reducing bacteria and methanogens has been widely recorded in calcite and siderite concretions (Coleman and Raiswell, 1981; Curtis et al., 1986; Coleman, 1993; Melendez et al., 2013a,b; Zeng and Tice, 2014; Cotroneo et al., 2016; Gaines and Vorhies, 2016; Plet et al., 2016; Lengger et al., 2017).
Interaction of the cell wall with the environment. Carbonate nucleation takes place either through the cell wall via ion exchange, or on the cell wall because of the presence of negatively charged functional groups like carboxyl, phosphate and amine, which can bind to divalent cations (e.g., Ca2+, Mg2+) when available (Warren et al., 2001; Dittrich and Sibler, 2005; Ercole et al., 2012). Following the increase in concentration of these metal ions in the surrounding microenvironment, and with sufficient availability of bicarbonates/carbonates, an oversaturation of carbonates is achieved, such as in calcite precipitation on cell walls of picocyanobacteria (Warren et al., 2001).
Entrapment by extracellular polymeric substances (EPS). EPS mainly comprise polysaccharides and proteins along with nucleic acids, lipids, uronic acids (Nichols and Mancuso Nichols, 2008; Ercole et al., 2012; Bains et al., 2015). As EPS contain various acidic residues and sugars, they can trap large divalent cations (e.g., Ca2+ and Mg2+) and remove free cations from solution. Once EPS degrade, the captured cations remain, and so the local concentration of cations increases and promotes calcium carbonate precipitation.
Figure 4
In the molecular fossil record, metabolic pathways influencing soft tissue preservation have been recorded via biomarker analysis. For example, (Melendez et al., 2013b) reported anaerobic recycling of invertebrate OM via microbial sulfate reduction and photosynthesis. Taphonomic experiments demonstrated the decay of arthropod brains in several Cambrian fossil sites, confirming the role of bacterial activity in mineralization (Parry et al., 2018; Purnell et al., 2018). Further evidence has been recorded in the taphonomic studies of Butler et al. (2015) and Bickel and Tang (2010) on bilaterians. It was found that, in order to counterbalance the rapid gut biota-driven internal decay of bilaterian tissues, gut biota rapidly escape the gut after death and form internal biofilms; these eventually provide a template for, and induce, mineralization, which facilitates concretion formation and the preservation of soft tissue (Bickel and Tang, 2010). The precipitation of siderite concretions has also been attributed to a complex array of sulfate and iron reducing bacteria (Farrell, 2014; McCoy, 2014; Janssen et al., 2022). Bone marrow and skin structures in frogs preserved on microbial mats for 3 years have been recorded in earlier studies (Iniesto et al., 2013, 2016, 2017). Previous studies have also demonstrated that microbes promote concretion formation via mineral precipitation on decaying carcass or within the sediment around decaying tissues (Pye et al., 1990; Briggs et al., 1993; McCoy et al., 2015b). All these investigations provide valuable evidence highlighting the role of microbes in several concretions and fossilization processes, but many other governing factors also play a crucial role.
Physicochemical factors influencing microbially mediated concretions
Numerous physicochemical parameters influence the formation and composition of microbially mediated concretions, a fact attested to by the variable size (both absolute and relative to the concretion nucleus) and geochemistry of concretions (and the fossils they host) in the fossil record. Several of these physicochemical factors are explored below.
Anoxic conditions
Successful fossilization typically correlates with anoxic conditions attributed to rapid burial, which concomitantly prevents scavenging of OM and inhibits aerobic decay processes (Allison, 1988a). Instead, OM decomposition proceeds via anaerobic metabolic pathways (Briggs, 2003b; Janssen et al., 2022). Moreover, under anaerobic conditions, denitrification (e.g., in Pseudomonas sp.), sulfate reduction to H2S, and anaerobic methane oxidation (coupled with sulfate reduction) are known to increase the alkalinity and change the chemistry around cells leading to carbonate precipitation (van Rijn et al., 2006; Zhu and Dittrich, 2016). In carbonate concretions, early diagenetic decay-induced mineralization is considered responsible for the co-occurrence of concretion formation with soft tissue fossils at their center. Some studies have suggested that anaerobically driven microbial processes, such as sulfate reduction and production of H2S, have been critical in facilitation of exceptional soft tissue fossil preservation (e.g., Melendez et al., 2013a,b; Schwark, 2013; Plet et al., 2016; Lengger et al., 2017).
pH
The chemistry of pore waters is a significant control in mineral precipitation, and consequently in carbonate concretion formation. Berner (1968a) reported that decaying tissue can increase pH as well as promote precipitation of calcium and magnesium from dissolved ions in solution. This rise in pH is related to the degradative release of bases such as ammonia (Berner, 1968a). However, further work by Berner (1969) showed that calcium carbonate precipitated only when the pH rise coincided with extensive bacterial sulfate reduction (BSR). pH also plays a vital role in the carbonate–phosphate switch that controls carbonate precipitation. Under low-pH conditions (<pH 6.38), and in the presence of free calcium ions and phosphate ions, calcium phosphate precipitates; by contrast, at higher pH (> pH 6.38), and in the presence of free calcium and carbonate ions, calcium carbonate precipitates (Briggs and Kear, 1993c; Briggs and Wilby, 1996; Janssen et al., 2022).
Other physico-chemical variables
Other factors including dissolved oxygen (DO), conductivity and temperature have been demonstrated to be contributing variables in concretion formation (e.g., Briggs, 1995b; Iniesto et al., 2017; Muramiya et al., 2022). Glendonite, a calcite pseudomorph after ikaite (CaCO3.6H2O), forms during early diagenesis in marine sediments and under relatively low temperatures ranging from-2°C to 10°C. This biomineral has been widely used as a low-temperature indicator to reconstruct paleoclimate (De Lurio and Frakes, 1999; Muramiya et al., 2022; Rogov et al., 2023). According to a study by Iniesto et al. (2017), DO exhibited a control similar to pH during laboratory based taphonomic experiments on frogs. The DO and pH were stabilized after seven weeks of incubation of a frog, and the drop in DO and pH implies the period of mineralization. This clearly demonstrated that DO and pH has a vital, but as yet unpredictable role in mineralization.
Microbiological controls on carbonate precipitation and concretion formation
Carbonate mineral precipitation is controlled by a number of complex, interrelated chemical processes. This includes alkalinity changes induced by microbiological processes, which can be dictated by the local environment and pore water chemistry (e.g., Berner, 1968b), or influenced by bicarbonate ions sourced from the surrounding pore waters or from decaying OM (Curtis et al., 1986). A source of cations within the substrate and/or porewaters is also required for concretion precipitation, most commonly calcium or iron forming calcite and siderite concretions, respectively (Curtis et al., 1986; Marshall and Pirrie, 2013; McCoy, 2014). Dolomitic concretions can also form in magnesium-rich environments (e.g., Grice et al., 2019; Scheller et al., 2021). Commonly initiated by decay of a central OM-rich nucleus, carbonate cement precipitates within unconsolidated sediment (Raiswell, 1971; Raiswell and Fisher, 2000; McCoy, 2014; Lengger et al., 2017). Carbonate concretions can form either via pervasive growth where nucleation is simultaneous across the concretion and cementation infills pore space later; concentric mineral growth outwards from a central nucleus; or by a combination of both processes (Raiswell and Fisher, 2000). The role of microbiological OM oxidation in concretion initiation and growth has been demonstrated by stable carbon isotope analyses (e.g., Curtis et al., 1972; Hudson, 1978; Coleman and Raiswell, 1981; Gautier, 1982; Raiswell and Fisher, 2000; Cotroneo et al., 2016), as well as biomarker studies (e.g., Melendez et al., 2013a,b; Plet et al., 2016; Lengger et al., 2017). Previous studies have also proven the role of bacterial EPS in mineral precipitation, for example absorbance of iron from iron-rich chlorides and oxides onto the surface of EPS during authigenic precipitation (Spicer, 1991; Dunn et al., 1997).
Calcium carbonate concretions
Calcium carbonate (calcite; CaCO3) precipitation is a consequence of BSR, wherein sulfate reducing bacteria oxidize OM to CO2 to obtain energy and reduce sulfate to H2S (Coleman and Raiswell, 1981; Coleman, 1993; Coleman and Raiswell, 1995; Kiriakoulakis et al., 2000; Melendez et al., 2013b; Plet et al., 2016). BSR is chemically represented by Equations 1, 2 (Raiswell, 1976). Subsequently, reduced sulfide reacts with dissolved iron to form pyrite via solid iron monosulfide (Equations 3, 4; e.g., Berner, 1985), while carbonate reacts to form calcite (e.g., Berner, 1968a; Pye et al., 1990).
Initial stages of calcite concretion formation typically occur within the earliest stages of diagenesis. Anoxic marine settings have abundant dissolved sulfate and therefore favor calcite precipitation (Berner, 1985). H2S at the photic zone of an anoxic water column promotes photic zone euxinia (PZE), which has been demonstrated to facilitate exceptional OM preservation (see Figure 5) (e.g., Summons and Powell, 1987; Schwark and Püttmann, 1990; Grice et al., 1996, 1997; Schaeffer et al., 1997; Figure 4). Notably, calcite concretions preserving soft tissue and biomolecules have been associated with PZE (e.g., Melendez et al., 2013a,b; Plet et al., 2016; Lengger et al., 2017).
Figure 5
Calcite concretions can display varying morphological and mineralogical properties with different crystalline phases. These include, but are not limited to, calcite, aragonite, vaterite, dolomite, CaCO3 monohydrate, CaCO3 hexahydrate and amorphous CaCO3 (Rodriguez-Navarro et al., 2012; Murugan et al., 2021). The shape and size of CaCO3 crystal changes during the precipitation process under different physico-chemical conditions and in association with different microbial communities (Wilby et al., 1996; O'Brien et al., 2002; Raff et al., 2008; Dhami et al., 2012; Raff and Raff, 2014; Plet et al., 2016; Zhu and Dittrich, 2016; Iniesto et al., 2018; Grice et al., 2019; Dubey et al., 2022; Murugan et al., 2022). The major factors responsible for microbially induced concretion precipitation include the concentration of calcium, concentration of DIC, pH, and the availability of nucleation sites (Hammes and Verstraete, 2002; Dhami et al., 2013b; Murugan et al., 2021).
Iron carbonate concretions
In contrast to calcite-forming environments, siderite precipitation is associated with sulfate-limited environments (Coleman, 1993), where dissolved sulfate is rapidly utilised forming pyrite (Equations 3, 4), and bacterial metabolic processes mainly occur via microbial iron reduction (Curtis et al., 1986) and methanogenesis (Maynard, 1982; Curtis et al., 1986; Coleman, 1993; Janssen et al., 2022), as per Equations 5, 6, respectively. This is observed in freshwater systems, such as lakes and swamps.
Pyrite formed as a product of early BSR is often identified in relation to siderite concretions; for example, in siderite concretions from Mazon Creek, pyrite can be observed either localized with fossils or in halos around them (e.g., Cotroneo et al., 2016). In the case of Mazon Creek siderite concretions, δ34S isotope data indicated initial bacterial sulfate reduction rapidly gave way to pervasive siderite growth via methanogenesis (Cotroneo et al., 2016).
Lipids released from decaying organisms might also play a potential role in promoting microbial processes (Kamran et al., 2020). Pure cultures of the iron-reducing bacteria Geobacter and Shewanella have precipitated siderite under laboratory conditions (Lin et al., 2020; Janssen et al., 2022). The reduction of the labile iron can raise the pH above optimal conditions (precipitation of calcite and aragonite is favored over pH ~7.2); however, when coupled with low levels of sulfate reduction, pH variation is limited within the range of siderite precipitation (Lin et al., 2020; Janssen et al., 2022). Here, iron (III) is used as an electron source for the oxidation of OM to CO2 instead of sulfate, by sulfate reducers such as Desulfovibrio (Kamran et al., 2020). A detailed model of iron carbonate concretion formation is shown in Figure 6.
Figure 6
Phosphatic concretions
Marine phosphatic concretions are formed under anoxic conditions near the sediment–water interface, during early diagenesis. Phosphate is sourced from the sediment pore waters with bacteria playing a crucial role in phosphate fixing, with a possible role for bacterial mats in concretion mineralization (Baturin, 1971; Bentor, 1980; Reimers et al., 1990). Large sulfur bacteria like Beggiatoa or Thiomargarita can store phosphate in the form of polyphosphate under oxic conditions (Brock and Schulz-Vogt, 2011). However, these bacteria produce sulfide, and if oxygen supply is insufficient for complete oxidation of the sulfides, the capacity for polyphosphate storage decreases. Increasing sulfide concentrations and anoxia leads to the decomposition of polyphosphate and iron hydroxides, causing the bacteria to release inorganic orthophosphate (Pi) into surrounding pore water (Brock and Schulz-Vogt, 2011). Pi is the precursor for the precipitation of phosphorite minerals and phosphatic replacement of soft tissues (Janssen et al., 2022). Once precipitation begins, the process is estimated to phosphatize soft tissues rapidly, in timescales of days to weeks (Föllmi, 1996).
Most of these phosphatized concretions are triggered by the decomposition of OM by subsurface microbial communities involved in bacterial sulfate reduction and anaerobic methane oxidation, EPS formation, photosynthesis, ureolysis, iron reduction (Equations 3, 4, 7; Plet et al., 2016; Zhu and Dittrich, 2016; Kamran et al., 2020).
The conditions of phosphatization involve phosphate ions (from the decay of animal remains or an allogenic source), Ca2+ ions from seawater and low pH from the production of volatile fatty acids and CO2 (Zoss et al., 2019). Phosphatized concretions are formed from carbonate fluorapatite (Ca5(PO4,CO3)3F) and occur most in deposits of Jurassic–Cretaceous age, when phosphogenic-favoring environments were particularly prevalent (Martill, 2007; Dornbos, 2011). Phosphatic concretions have been identified in deposits ranging in age from upper Mesoproterozoic [e.g., Diabaig Formation of the Torridon Group, Scotland, UK: Battison and Brasier (2012)] to Miocene, e.g., Riversleigh World Heritage Area, Queensland, Australia (Arena, 2008; Matzke-Karasz et al., 2013) and Funakawa Formation, Japan (Ogihara, 1999). Numerous modern phosphatic-rich deposits are found in organic-rich, offshore environments, e.g., Baja California (Schuffert et al., 1994; Ogihara, 1999), the Namibian coast (Zoss et al., 2019) and the Chilean-Peruvian coastline (Turnbull et al., 1996; Schulz and Schulz, 2005). A famous example from the fossil record is the Lower Cretaceous Santana Group Lagerstätte of Brazil, which preserves an array of fossils including abundant invertebrates, teleost fish, crocodyliforms, pterosaurs, and rare dinosaurs (Smith, 2000; Martill, 2007; Martill and Brito, 2017). Skin, gills, muscles, and collagen are the most frequently phosphatized soft tissues (Vincent et al., 2017; Parry et al., 2018). Phosphatization is also able to preserve cellular and subcellular structures (Bengtson and Budd, 2004; Bengtson et al., 2017; Sun et al., 2020). In bone tissues, the outer compact bone layers are more prone to replacement with fluorapatite, but the inner spongy bone is more prone to be replaced with calcite; however, the timing of phosphatization of bone tissues is still not fully understood (Zoss et al., 2019). The creation of phosphatized tissues and phosphatic concretions in microbial mats is also largely unknown, however there is extensive research on the role of organic-rich substrate in the precipitation of calcium phosphate (Onuma et al., 2000; Heinemann et al., 2011; Janssen et al., 2022). One location reported to contain microbial mat-preserved fossils is the Crato Formation Konservat-Lagerstätte of the Santana Group, Araripe Basin, Brazil (Varejão et al., 2019).
Analytical methods for concretion characterization
A range of sophisticated and multidisciplinary analytical approaches can be utilized in the robust interrogation of fossiliferous concretions and the fossils they contain (Figure 7; Table 2). These methods include: using powerful imaging tools to resolve the physical form and morphologies of concretions and fossils, sometimes at sub-microscopic levels; organic characterization of the nature and molecular speciation of the preserved organisms and the paleoenvironment in which they were formed; inorganic geochemical analysis for depositional information and evaluation of the redox conditions aiding preservation; and the use of microbiological and molecular techniques to study the structure and function of the microbes active in EPS and concretion formation (Figure 8: Approach 1).
Figure 7
Table 2
| Technique | Description | Advantages | Disadvantages |
|---|---|---|---|
| Morphological analyses | |||
| Scanning electron microscopy (SEM) | A focused beam of electrons is used to image the sample | High resolution (<20 nm) | Low electron penetration depth |
| SEM/EDS | SEM attached to EDS system, for spatial elemental analysis | Quantitative analysis of elements & mapping distribution | Low electron penetration depth |
| Focused ion beam (FIB)-SEM | Uses a focused beam of ions to form an image | Quantitative analysis of elements & mapping distribution | Destructive analysis |
| Optical (light) Microscopy | Visible light analysis of structures in fixed & living samples | Rapid results | Limited resolution, & not suitable for all samples |
| Confocal Scanning Laser Microscopy (CSLM) | Optical imaging technique using laser to increase contrast & resolution | Non-intrusive & non-destructive, minimal sample preparation | Highly limited depth of field, & slow process |
| Fluorescence Microscopy | Emission of luminescence to identify structures in fixed & living samples | Organic maceral identification | Limited resolution, & not suitable for all samples |
| Atomic Force Microscopy (AFM) | Optical imaging technique, does not use lenses or beam irradiation | Very- high resolution (~nm), no need to stain or place sample in vacuum | Small single scan image size, & slow process |
| X-Ray Fluorescence (XRF) | Characterization of the elemental composition of bulk sediment | Can analyze wide range of elements | Cannot identify different phases |
| X-Ray Diffraction (XRD) | Characterization of mineralogical composition | High precision & non-destructive | Requires a homogenous sample |
| Computed tomography (CT) | Imaging & quantification of 3D structures using X-ray microscopy | Non-destructive, can scan large samples | Lower resolution than other tomography-based methods |
| Micro-CT (μCT) | Imaging & quantification of 3D structures using X-ray microscopy | High resolution, non-destructive | Limited sample size (chamber), & long scanning times |
| Synchrotron propagation phase contrast micro-CT (PP-SRμCT) | 3D imaging technique | Non-destructive, rapid, high-spatial resolution | Complex process requiring multiple stages, samples require mounting |
| Neutron scattering | Imaging of 3D structures to see hydrogenous materials | Greater sample penetration than X-rays | Potential radioactive decay induced in samples |
| Organic geochemical (and related) analyses | |||
| Gas chromatography–mass spectrometry (GC–MS) | Identification & quantification of compounds in organic mixtures | Widely available, mature technology for light, non-polar compounds | Destructive analysis, often intricate sample preparations, analysis & data interpretation |
| Tandem mass spectroscopy (GC MS–MS)/Multiple Reaction Monitoring (MRM) | Targeted GC–MS analysis of known compounds | Increased sensitivity & selectivity of targeted compounds (e.g., biomarkers) | Requires advanced MS instrumentation & prior GC–MS analysis to identify targets |
| Multidimensional GC–MS (GC x GC) | GC separation using two different column types | Greatly improved separation of compounds, including those that coelute on one-dimensional GC–MS | As for GC–MS and GC MS–MS, & high data processing times |
| Time of Flight-Secondary Ion Mass Spectrometry (ToF-SIMS) | Elemental, chemical state, & molecular information from solid surfaces | High mass range, & high spatial resolution over wide cross-section of sample surface | Superimposed MS of complex organic mixture; not capable of resolving isomers |
| Liquid chromatography-mass spectrometry (LC–MS) | Separation & analysis of large, polar compounds | Mature technology, allows analysis of compounds not amenable to GC–MS | Destructive analysis, long preparation time needed for extraction of sample |
| Inductively Coupled Plasma Mass Spectrometry (ICP-MS) | Trace metal analysis | Can be coupled with laser probes to create high spatial resolution elemental maps | Destructive analysis, & wider field of ion energy resulting in noisy signals |
| Raman spectroscopy | Information about chemical structure, phase crystallinity & molecular interactions | Non-intrusive & non-destructive | Cannot analyze samples with high topography |
| Bulk isotope analysis | Distinguish OM source inputs, cycling of elements | Minimal sample preparation, rapid analysis | Gives an averaged value of complex organic samples, i.e., cannot distinguish multiple sources |
| Compound-specific isotope analysis (CSIA) | Stable isotope mass spectrometry coupled with gas or liquid chromatography | Stable isotope values of individual compounds in complex mixture | Requires prior GC–MS identification & rigorous sample preparation for typically required baseline peak separations, & incomplete separation of a compound in the mixture can lead to isotopic fractionation |
| Fourier-transform infrared spectroscopy (FT-IR) | Identification of organic, polymeric, & some inorganic materials via infra-red light | Highly sensitive & rapid analysis of organic bonding & functional groups | Qualitative analysis, variable chemical species response |
| Atomic absorption spectroscopy (AAS) | Detects elements using the absorption wavelengths of light | High accuracy | Can only measure one element at a time, destructive analysis |
Brief summary of the various analytical techniques applicable to concretion analysis, as discussed in this review.
Figure 8
Morphological, molecular, and microbiological characterization of concretions
An understanding of the metabolic activities that took place at the time of fossilization can be obtained through various analytical techniques, using either direct (microbial morphotypes, mineralized EPS, etc.) or indirect (microlaminations with OM or micropeloids) microscopic and elemental evidence (Iniesto et al., 2021; Dias and Carvalho, 2022). This understanding can be furthered via investigation of the influence of various metabolic pathways on decay and mineralization through taphonomic experiments in controlled environment (Pye et al., 1990; Briggs and Kear, 1993c; Butler et al., 2015; Wilson et al., 2016; Gäb et al., 2020; Janssen et al., 2022). In the previous taphonomic experiments, Pye et al. (1990) demonstrated at the Norfolk Marsh field setting that concretions form actively in reduced sediments in which sulphate-reducing bacteria are active. The source of carbonate in their study was found out to be partly driven from marine sources and partly from microbial degradation of organic matter. In another study of Briggs and Kear (1993c) on decay of modern shrimps, it was seen that partial mineralization occurred in amorphous calcium phosphate leading to preservation of cellular details of the muscle tissue under anaerobic conditions wherein microbial biofilms played an important role in the inhibition of tissue decomposition. The anaerobic conditions inhibit scavengers and degrading aerobic bacteria and promote various anaerobic metabolic pathways relevant for biologically induced mineralization (Wilson et al., 2016). Gäb et al. (2020) in their taphonomic experiments on fish found that the extreme environmental conditions in the Green River depositional environment could reduce decay and promote mineralization. Understanding the role of microbes and microbial by products in a range of fossilization conditions is therefore imperative and can be unpinned via a range of micrographical, mineralogical and molecular tools as discussed below.
Morphological analysis of real concretion samples
This analysis provides a useful first screening to assess microbial mineral interactions, investigate the role of microbes and biofilms in different fossiliferous concretions and the physical nature of fossils. A range of microscopic and other microanalytical techniques have been utilized in the field of paleomicrobiology, including scanning electron microscopy, optical microscopy, fluorescence and confocal microscopy, atomic force microscopy and various analysis using synchrotron radiation.
Scanning electron microscopy (SEM) and petrographic analysis with coupled X-ray spectroscopy (SEM/EDS) reveals morphological features along with the chemical constituents, thereby providing a comprehensive picture of microenvironments during fossilization (Iniesto et al., 2013, 2016, 2017; Raff and Raff, 2014; Mähler et al., 2020; Dias and Carvalho, 2022). To date, a number of experimental studies on the direct influence of bacteria on mineralization and preservation have been conducted (in marine and non-marine settings) using different scanning electron micrographical and other elemental analysis tools (Briggs and Kear, 1993a,b,c; Hof and Briggs, 1997; Sagemann et al., 1999; Martin et al., 2005; Raff et al., 2008, 2014; Peterson et al., 2010; Butler et al., 2015; Naimark et al., 2016, 2018; Eagan et al., 2017; Mähler et al., 2020). In a recent study of insect fossils from the Lower Cretaceous Crato Formation Lagerstätte (part of the Santana Group of Brazil), SEM imaging revealed direct evidence of microbial morphotypes and textural features of mineralized EPS, thereby providing strong evidence of the influence of microbial mats in the fossilization process (Dias and Carvalho, 2022).
Optical (light) Microscopy helps in visualizing the fine details of an object by creating a magnified image through a series of glass lenses. Optical microscopy has been widely used in the study of concretions (e.g., Iniesto et al., 2015; Dias and Carvalho, 2022; Downen et al., 2022; Lin et al., 2023).
Confocal Scanning laser Microscopy (CSLM) creates sharp and distinctive images of an exact plane of a specimen (Relucenti et al., 2021). It allows the quantitative evaluation of structural parameters, thickness, and roughness. This technique also permits non-destructive analysis of the 3D architecture and 4D visualization of microfossils (Relucenti et al., 2021). This technique is widely used for the identification of bacteria and EPS distribution within the live biofilm matrix (Wagner et al., 2009; Reichhardt and Parsek, 2019). CSLM, in concert with various fluorescent stains, helps in understanding the different classes of macromolecules by calculating their abundance and distribution on biofilms in a very short period of time (Zhang et al., 1998; Hille et al., 2005; Wagner et al., 2009). However, CSLM has been applied and reported sparingly in fossil studies. Studies by Wagner et al. (2009) and Schopf and Kudryavtsev (2009) demonstrated that CSLM, when combined with Raman spectroscopy, enables observation of biofilms in situ, thus providing supplementary information about chemical properties and the distribution of components of EPS.
Fluorescence Microscopy is based on the emission of luminescence because of absorption of photons, when the samples treated with special fluorescent reagents exhibit Stokes shift. This technique can be used to identify structures in fixed and living biological samples (Lichtman and Conchello, 2005; Sanderson et al., 2014), and helps in understanding the viability of living and dead bacterial cells, biofilms, EPS and calcium carbonate precipitates (McMullan, 1995; Vernon-Parry, 2000). This technique has been recently utilized for investigation of internal architecture in steinkern spider fossils from Oligocene Aix-en-Provence Lagerstätte in southern France (Downen et al., 2022), which identified prolific microbial mat communities as likely being responsible for the preservation of infilled spider molds.
Atomic Force Microscopy (AFM) is a form of scanning probe microscopy, which uses a probe or tip to map the contours of the sample (Braga and Ricci, 1998). AFM is the measurement of the variation of force between the probe tip and the sample surface (Braga and Ricci, 1998) and thus helps in achieving a quantitative assessment of various interactive forces on biofilms under ambient conditions, or even on liquid surfaces, without any pre-treatment. This helps in generating a 3D image of surface topography. In general, these advantages make this emerging imaging technique useful for analyzing bacterial morphology, as well as their adhesive and elastic properties (Chatterjee et al., 2014).
Itrax X-Ray Fluorescence (XRF) core scanning extends traditional XRF characterization of the elemental composition of bulk sediment material by providing high-resolution elemental distributions. These have important implications for understanding paleoenvironmental and geochemical records (e.g., Croudace et al., 2006; Rothwell et al., 2006; Thomson et al., 2006), and can enable better understanding of the complex geochemical, redox and microbial conditions controlling carbonate fossilization (Croudace et al., 2006; Hunt et al., 2015; Hussain et al., 2020). The Itrax XRF core scanner simultaneously collects micro-XRF spectrometry elemental profiles, and optical and microradiographic images (Croudace et al., 2006). This provides an opportunity to study the micro-spatial relationship of elemental distributions within sample material. For example, detailed analyses of elemental distributions across carbonate concretions showed steep profiles of important elements (e.g., calcium) that were subsequently used to construct a diffusion model for concretion growth (Yoshida et al., 2015, 2018).
Omic techniques
Omic techniques are a set of high-throughput methods used to study the structure, function, and interactions of microbial communities in different environments. These techniques include DNA metabarcoding, metagenomics, metatranscriptomics, proteomics, and metabolomics, which analyze the genetic material, RNA transcripts, proteins, and metabolites present in a microbial community, respectively (see green pathways in Figure 7; Zarraonaindia et al., 2013; Shaffer et al., 2022). By using these approaches, researchers can gain insights into the diversity and complexity of microbial ecosystems and understand the roles of different microorganisms in these environments, their metabolic pathways, and their interactions with other organisms and their environment. Omic techniques have broad applications in microbiology, ecology, and biotechnology, and are helping to drive discoveries in fields such as environmental science and bioremediation (Garnatje et al., 2017; Gutleben et al., 2018; Zhang et al., 2018; Laczi et al., 2020; McElhinney et al., 2022). In recent years, there has been increasing interest in applying omic techniques to the study of fossils and the processes involved in their formation and preservation (Dong et al., 2019; Janssen et al., 2022). By integrating multiple omic technologies, it is possible to gain a more complete picture of the constituents and functions of microbial communities within concretions, and potentially unravel the mechanisms underlying concretion formation. For example, microbial biofilms have been shown to play a crucial role in the nucleation and growth of concretions (Frankel and Bazylinski, 2003; Grice et al., 2019; Janssen et al., 2022). It is possible to identify the predominant microorganisms and metabolic pathways involved in the formation of concretions by examining the structure of microbial communities and gene expression patterns in biofilms through techniques such as DNA metabarcoding, metagenomics, and metatranscriptomics (Babilonia et al., 2018; Onstott et al., 2019; Campbell et al., 2021). In addition, these techniques can also provide insights into the preservation of fossils within concretions. For instance, proteomic analysis can reveal the proteins and enzymes involved in the preservation of soft tissues in fossils (Boatman et al., 2019), while metabolomic analysis can identify the biochemical pathways responsible for the preservation of organic compounds (Janssen et al., 2022). The use of omic techniques in paleontology and sedimentology is a relatively recent development, and there is still much to be discovered regarding their potential and limitations. However, as the technology continues to improve, these techniques have the potential to revolutionize our understanding of fossil and concretion formation in modern settings.
Ancient DNA
The analysis of ancient DNA (aDNA) provides researchers with innovative ways to study the past (Yang and Watt, 2005). The study of ancient organisms is rapidly growing owing to recent methodological and technological advancement. It is now possible to obtain vast quantities of DNA data from ancient samples in a high-throughput manner and use this information to investigate the dynamics and evolution of past communities (Eisenhofer and Weyrich, 2019). For instance, by analyzing the DNA of microbial communities preserved in sedimentary layers, it is possible to reconstruct the diversity and abundance of past microbial assemblages and identify the environmental factors that influenced their evolution, as well as shed light on their role in mineral formation and biogeochemical cycling over geological time scales (Capo et al., 2022; Dong et al., 2022). The use of aDNA could potentially provide a window into the microorganisms existing at the time of concretion formation and allow for the identification of the original source organism. However, there are several limitations and challenges associated with aDNA analysis, such as the degradation of DNA over time and the risk of contamination from modern sources. Despite these challenges, in the presence of favorable preservation conditions, the application of aDNA analysis holds great potential as a tool for investigating concretions.
Microbiology techniques
Microbial culturing, enzymatic analysis, physico-chemical parameters and viability analysis – Microbial culturing and enrichment is a simple and efficient method to enhance the multiplication of microbes (associated with fossil/sediment samples) by supplementation of nutrients under controlled laboratory conditions (Brock, 1999; Chapin and Lauderdale, 2007; Lewis et al., 2021). This aids in understanding the growth pattern, density, enumeration (colony forming units/ml) and metabolic properties of the enriched cultures along with their concretion/carbonate formation capability (Dhami et al., 2013a, 2017; Murugan et al., 2021). When trying to grow and study a specific microorganism under laboratory conditions (Figure 8, Approach 2), it is important to use a culture medium that closely mimics their natural environment. This helps the microbial colony to grow to its optimum, and enables better understanding of its specific needs and genetic makeup. Such minimal nutrient media have been designed and utilized in previous studies on enrichment of microbes from natural environments (Henson et al., 2016; Rahman et al., 2020; Ramachandran et al., 2020; Rodrigues and de Carvalho, 2022). Artificial sea water (ASW) media is generally used as a substitute for natural seawater to cultivate marine microbes as the latter often suffers from supply issues and seasonal variability and quality (Berges et al., 2001; Henson et al., 2016). Recently, halophilic archaea were cultivated from surface-sterilized middle–upper Eocene rock salt from the Yunying salt mine, China and the key feature that helped in the longevity of these microbes was their ability to keep their genomic DNA intact (Jaakkola et al., 2014).
Microbial community analysis is also conducted via omics tools (discussed above in omics section) followed by characterization of EPS, biofilm properties and any extracellular enzymes (as urease, carbonic anhydrase) produced by the grown cultures as demonstrated in prior studies (Dupraz et al., 2009; Li et al., 2015; Dhami et al., 2016; Al Disi et al., 2019; Murugan et al., 2021). Microbial culture supernatant is also investigated for change in physico-chemical parameters by microbial metabolic activities via a range of elemental analysis tools such as atomic absorption spectroscopy (AAS), Inductively coupled plasma mass spectroscopy (ICP-MS) and Fourier-transform infrared spectroscopy (FT-IR) (Li et al., 2015; Liu R. et al., 2021; Liu X. et al., 2021; Murugan et al., 2021).
In situ characterization of concretion sequestered microfossils
It is advantageous to screen concretion collections with in situ characterization techniques to identify those with the most promising impregnations (e.g., large, exceptional preservation) for more detailed analytical attention. Given the typically limited amounts of fossil sample available and their precious nature, a range of appropriate micro characterization methods are often applied prior to non-destructive chemical analysis.
Many of the micro-graphical techniques described in the previous concretion section (see: Morphological, molecular and microbiological characterization of concretions) can also be applied to the sequestered microfossils. Typically, concretions are opened so that the fossils can be accessed when exposed, but some techniques also allow in situ interrogation of the enclosed fossils. For instance, SEM imaging methods can provide ultrastructural information of fossilized tissues. However, SEM is limited by low electron penetration depth, meaning that it is often more effective on exposed structures, and especially on carefully prepared ultrathin (<100 nm) sections; one drawback, therefore is that these are representative of only a small fraction of the specimen. 3D images of embedded fossils can be achieved through focused ion beam (FIB)-SEM or by combining sequential milling with concurrent Energy Dispersive Spectroscopy (SEM EDS) where despite the destructive milling approach, nanoscale fossil structures can be successfully imaged to provide insights into their chemistry, ultrastructure, taphonomy and biogenicity (Wacey et al., 2012; Brasier et al., 2015).
CSLM and Raman Spectroscopy can also be used for non-intrusive and non-destructive study of the 3D structure and chemical composition of EPS and fossils (Schopf and Kudryavtsev, 2009; Wagner et al., 2009). Schopf et al. (2010) utilized optical microscopy in combination with CSLM and other interdisciplinary approaches to successfully distinguish between authentic microbial fossils and microscopic “look-alikes.”
Atomic Force Microscopy (AFM) is now widely used for fossil observations and imaging in paleontological research (Benítez et al., 2019). AFM studies by Kempe et al. (2002, 2005) on organic-walled fossils from the upper Neoproterozoic Chichkan Formation of Southern Kazakhstan revealed stacked arrays of 200 nm-sized angular platelets of polycyclic aromatic kerogen on their walls. On comparison with SEM, AFM images provided higher resolution and 3D information about the organization of carbon within the cell. AFM has also been used to measure biofilm thickness and the height and “roughness” of EPS (Relucenti et al., 2021), and to identify the crystal structures of biogenic marine calcite and aragonite from fossil corals (Coronado et al., 2015), echinoderms (Stolarski et al., 2009) and mollusks (Casella et al., 2018; Benítez et al., 2019).
Computed tomography (CT) extends the centuries long use of X-Rays to help visualization of geological fossils (Hohenstein, 2004). X-ray computed tomography (XCT) scanners can successfully visualize fossils in un- or partially prepared concretions and has revolutionized the science of paleontology [see Sutton et al. (2014) for an excellent overview]. Applications of XCT to fossils in concretions include the anatomical description of a Devonian shark from Morocco (Klug et al., 2023); the analysis of an ichthyosaur skull from the Triassic of Svalbard (Roberts et al., 2022); and the visualization of trace fossils in driftwood from the Cretaceous–Paleogene Boundary in the USA (Maisch and Becker, 2022). XCT does have its limitations, however, including digital separation of fossils or matrix – in which case other techniques might be more effective (e.g., neutron tomography; see below).
Micro-CT (μCT) scanning, or high resolution XCT, is also now being popularly applied in paleontology. Recent concretion fossil studies include the reinterpretation of a purported Cambrian jellyfish fossil as a pseudofossil (Nolan et al., 2023); the visualization of the musculature and reproductive, digestive, and circulatory systems of a Devonian arthropod (Laville et al., 2023); the revelation in exquisite detail of the anatomy of Carboniferous millipedes from France (Lheritier et al., 2023); and the characterization of a Jurassic pseudoplanktonic community on a fossilized log (Little et al., 2023).
Synchrotron exploration of the X-ray and matter interactions on a range of geological materials can provide insights on morphology, elemental composition, oxidation states, crystalline structure, magnetic properties, and others, which can measurably contribute to the investigation of biogenicity of putative biosignatures (Callefo et al., 2019). Gueriau et al. (2020) utilized synchrotron radiation to generate X-ray fluorescence elemental maps of fossils representative of different taxonomic groups (arthropods, sarcopterygians and actinopterygians), types of preservation (compressed and three-dimensional fossils, including the ones with extensive soft-tissue mineralization), geological ages and depositional environments. Mineralogical maps were also generated in transmission geometry using a two-dimensional area detector placed behind the fossil.
Synchrotron propagation phase contrast micro-CT (PP-SRμCT/PPC SRμCT) identifies and maps mineral phases and their distribution at the microscale over centimeter-sized areas. Elemental information can be collected synchronously, informing on texture (preferential orientation), crystallite size and local strain. The extremely high resolutions (<100 nm; Vorontsov et al., 2023) achievable with PP-SRμCT has possibly led to the greatest paleontological advances when applied to concretions (Sanchez et al., 2012). This sophisticated technique has been applied to a variety of concretion fossils in recent years, including Devonian placoderm fishes from Australia (Trinajstic et al., 2022b), Triassic coprolites from Poland (Qvarnström et al., 2019a,b) and Jurassic cephalopods from France (Rowe et al., 2022). The non-invasive extraction of 3D information from homogeneously dense specimens has proved critical to some paleobiological studies (Tafforeau et al., 2006; Cunningham et al., 2014; Maldanis et al., 2016), revealing even the preservation of soft tissues.
Neutron scattering
Neutron tomography (NT) is similar to CT in as much as it enables digital separation of fossils from rocks (Bevitt, 2018). Advantageously, the contrast and penetration that can be achieved with neutrons is greater than with X-rays: X-rays interact with electrons surrounding an atom, whereas neutrons interact with atomic nuclei (Bevitt, 2018). NT has been used to visualize a variety of fossils in concretions, including Devonian fishes from Australia (Trinajstic et al., 2022b), a Jurassic ammonite from the United Kingdom (Cherns et al., 2022), a Cretaceous fish from Brazil (Pugliesi et al., 2019), a Cretaceous crocodyliform (with part of an ornithopod dinosaur in its body cavity) from Australia (White et al., 2022), a Cretaceous seed cone from New Zealand (Mays et al., 2017), and an Eocene plant from Antarctica (Dawson et al., 2014).
Organic geochemical (and related) analysis of fossil OM
The isolation of the fossil from its concretion host is critical to the success of organic geochemical analysis of fossil OM. Separation is often achieved through physical methods, although these might not fully isolate the fossil and matrix. As a result, pure matrix is commonly analyzed separately from the fossil sample to avoid contamination and accurately determine the contributions of each component.
Sample screening with high throughput bulk analysis
Bulk geochemical and key elemental analysis are common preliminary methods used to chemically screen concretions and their organic fossils. These methods often involve measuring the total organic and inorganic carbon contents of sediments, along with other elements commonly found in organic compounds such as nitrogen, sulphur and oxygen. Elemental analyses can be used to measure these elements in decarbonated sediments treated with hydrochloric acid, providing a total for each element.
Rock-Eval pyrolysis is a widely used method in determining the thermal stability and quality of OM (Espitalié et al., 1977). It measures the thermal evolution of carbon compounds over laboratory applied temperatures (i.e., 300 to 650°C), and can also provide an indication of the carbon, hydrogen and oxygen content of sediments.
Molecular analysis by GC–MS
Natural OM (NOM) samples are typically subject to various wet chemistry and other preparation techniques to provide specific fractions appropriate for separate gas chromatography mass spectrometry (GC–MS) analysis. The most important technique for organic speciation – i.e., identification of organic compounds including biomarkers – in complex samples such as the NOM that can occur in concretions is GC–MS (see Grice and Eiserbeck, 2014 for a review).
Aliphatic and aromatic hydrocarbon speciation
The non-polar moiety of NOM is typically isolated in a solvent extractable or bitumen fraction which can be further resolved by liquid chromatography into saturate and aromatic fractions. These are then analyzed using GC–MS. The compounds detected in NOM samples can include biomarkers that act as molecular fossils of biological compounds like membrane lipids and pigments. After the deposition of organic matter, lipids and other compounds can be preserved and provide insights into past microbial activity (Brocks and Summons, 2014; Grice and Eiserbeck, 2014; Naeher et al., 2022). Molecular fossils can also include (metallo)porphyrins and proteins. These somewhat “functionalized” molecules are also relatively stable and often well-preserved in the rock record. Biomarkers when detected in NOM can provide a link to lipids and pigments of modern organisms (i.e., eukaryotes, bacteria, and archaea; Peters and Moldowan, 1992). In benign settings (e.g., concretions) hydrocarbon biomarkers may remain stable for hundreds of millions of years. Their detection in concretion fossils can therefore provide valuable taxonomic and environmental information about ancient ecosystems (see below).
Analytical pyrolysis of kerogen
The non-solvent soluble or kerogen fraction of NOM can also be interrogated by GC–MS following appropriate thermal (or chemical) treatments. Thermal energy can be used to break macromolecular OM into smaller products which can pass through GC columns, in a process referred to as analytical pyrolysis. An important advantage of kerogen analyses is that its covalently bound lattice is less vulnerable to overprinting from migrating hydrocarbons or other autochthonous inputs than the free hydrocarbon fraction (i.e., bitumen Peters and Moldowan, 1992).
Various pyrolysis devices have been developed for NOM kerogen analysis, but hydropyrolysis (HyPy) is now widely considered the best practice method because of its high detection sensitivity including of ancient biochemical signatures sequestered in inorganic substrates (Reinhardt et al., 2019). This pyrolysis event is conducted in a hydrogen-rich atmosphere to provide hydrogen donors that quench the reactivity of unstable ion and radical pyrolysates. This helps to maintain primary pyrolysate integrity often including the preservation of biomarker stereochemistry (Meredith et al., 2015). The HyPy released fraction is operationally trapped on a bed of silica gel, allowing subsequent isolation of saturate and aromatic hydrocarbon fractions which can be separately analyzed by GC–MS (or GC-isotope ratio-MS for compound specific isotope analysis).
Polar compound speciation and S-biogeochemistry: The polar fraction of solvent extracted (or HyPy liberated) NOM can be isolated by LC elution with polar solvents. Labile biomolecules, like proteins, lipids and sugars, can be in part sequestered through oxidative cross-linking, yielding N-, O-, and S- containing heterocyclic polymers (e.g., Wiemann et al., 2018a, 2020; McCoy et al., 2020). In particular an abundance of sulfides from microbial sulfate reduction (i.e., in low reactive iron/pyrite settings) can aid organic sulfurization during diagenesis, producing organic sulfur-rich macromolecular aggregates which can stabilize and preserve lipid biomarkers (Sinninghe Damsté and de Leeuw, 1990; Schouten et al., 1993; Aizenshtat et al., 1995).
The three-dimensional macromolecules produced by organic sulfurization are not amenable to GC–MS without further treatment. Raney Nickel is commonly used to selectively cleave the carbon-sulfur bonds of polar fractions, releasing a sulfur-bound organic fraction that can be analyzed by GC–MS (Sinninghe Damsté and de Leeuw, 1990). This approach has been widely used to study sulfurized lipids of Phanerozoic sediments. Heteroatomic organic compounds released by this process (or present in other fractions) may not be directly detectable by GC–MS without derivatization of specific chemical functionalities, e.g., acylation or silylation of acid or hydroxyl groups, respectively (Drozd, 1981). Some functionalized and high MW organic species can be detected directly by LC–MS, which can be advantageous for the analysis of thermally unstable or non-volatile species but is limited by increased band broadening effects compared to gas chromatography (Skoog et al., 2018).
Multidimensional GC–MS
Thanks to continued development, optimization and sophistication, GC–MS is being applied at increasing sensitivity and resolution. Both MS and GC detection can now be extended to multiple dimensions to support very high-resolution product detection. Two-dimensional gas chromatography (GC × GC) uses two different columns to separate compounds that co-elute in one-dimensional separations, greatly expanding resolution of complex mixtures (Scarlett et al., 2019). This allows high resolution physical separation which can aid the characterization of particularly complex mixtures. Tandem mass spectrometry (e.g., MS–MS) or Multiple Reaction Monitoring (MRM) can provide particularly selective analysis of target compounds such as molecular biomarkers (Mei et al., 2018). This upward technological trajectory has helped advance our knowledge of the biogeochemical pathways involved in the formation of biomarkers from natural product precursors during eogenesis (in the water column) and diagenesis (sediments and sediment water interface) and the unique palaeoenvironmental conditions required for their exceptional preservation (Grice et al., 2019).
2D surface analysis of NOM by particle bombardment techniques
The ability to correlate organic molecules with spatial and mineralogical sample features is an important consideration when interpreting exceptionally preserved fossils. Detailed molecular biomarker analysis, which typically requires destruction of bulk sample material, would ideally be complemented by spatially informative surface sensitive analytical methods.
Inductively Coupled Plasma Mass Spectrometry (ICP-MS) analysis using a laser probe can be used to create detailed maps of the elements present on the surface of a given sample. For example, Fe and S biochemical gradients measured across in concretion hosting an ichthyosaur fossil (Lower Jurassic Sachrang Formation, Germany) identified much lower microbial activity in the inner part of the concretion, which likely contributed to the excellent fossil preservation (Plet et al., 2016).
Time of Flight-Secondary Ion Mass Spectrometry (ToF-SIMS) is a technique that can analyze organic and inorganic molecules simultaneously with high mass and lateral resolution. Cluster primary ion beams improve the identification of high MW organic compounds with less analyte fragmentation. This technology is useful in various fields such as material science, biology, and surface analysis (Kollmer, 2004; Touboul et al., 2005). Important organic ToF-SIMS studies have included multiple biomarker investigations (e.g., Steele et al., 2001; Toporski et al., 2002; Siljeström et al., 2009, 2010, 2013, 2017, 2022; Thiel and Sjövall, 2011; Greenwalt et al., 2013; Thiel et al., 2014; Gren et al., 2017; Schweitzer et al., 2018). Organic ToF-SIMS analysis of geological and paleontological samples can yield mass spectral data from rare and precious specimens, altering only the uppermost few nanometers of analysis areas (Greenwalt et al., 2013; Lindgren et al., 2018, 2019; Baumgartner et al., 2023). As it employs no analyte separation (such as that provided by GC), it is not capable of resolving stereoisomers, and the isotopic composition of large organic molecules can be difficult to interpret. ToF-SIMS can complement traditional biomarker techniques by spatially correlating trace biomarker detection with organic sources, mineral phases, and structural features.
Raman spectroscopy is a non-destructive analytical method which can be used for chemical characterization of a wide range of sample materials. The incident source is a laser with a wavelength significantly different from the absorption wavelengths of the target analytes. The spectra produced are characteristic to each molecule, representing the energy difference between excitation and emission wavelengths of Raman active bonds. Use of Raman spectroscopy for in situ analysis of fossil specimens can identify preserved molecular functional groups, alongside intermolecular and organo-mineral relationships (Pelletier, 1999), making it a powerful tool for studying preserved organic matter and methods of biomineralization. Recent developments have given rise to widespread applications of Raman spectroscopy for analysis of biomolecular fossilization products (e.g., Yang et al., 2018; Wiemann et al., 2018a,b, 2019, 2020; Boatman et al., 2019; Fabbri et al., 2020; Norell et al., 2020; Steele et al., 2020).
Stable isotope analysis
Analysis of the stable isotopic composition of sedimentary OM can help to distinguish a wide range of source inputs (Hedges and Keil, 1995; Grice and Brocks, 2011). In the case of fossiliferous concretions, these inputs include bacteria involved in concretion formation, the surrounding depositional environment, and the fossilized organism itself (Melendez et al., 2013b; Plet et al., 2017). Stable isotopic composition is controlled by three major factors: the isotopic composition of source elements, the isotopic fractionation during biosynthesis, and isotopic fractionations during burial and diagenesis (Hayes, 2001; Sessions, 2016).
Stable carbon and oxygen measurements of carbonate have helped to classify the source of concretion carbon, e.g., sulfate (or iron) reduction vs. methanogenic CO2 (Mozley and Burns, 1993; Pearson and Nelson, 2005; Cotroneo et al., 2016), or biogenic vs. abiogenic carbonate (Yoshida et al., 2015). The δ34S of pyrite gives information on the sulfur cycle during concretion formation. Enriched δ34S measurements of pyrite from Mazon Creek concretions suggest formation in sulfate-limited conditions and near total depletion of local dissolved sulfate by SRB during concretion formation (Cotroneo et al., 2016), whereas strongly depleted pyrite in Oligocene Boom Clay concretions (Belgium) indicates abundant dissolved sulfate (De Craen et al., 1999). Stable carbon isotope ratios of bulk organic matter (δ13Corg) can be measured after removal of carbonate by reaction with dilute acid. Similarities in δ13Corg of Upper Cretaceous Holz Shale concretions (California) and host sediment was interpreted as evidence that OM was not strongly degraded during concretion formation (Loyd, 2017). Tripp et al. (2022) compared δ13Corg with compound-specific δ13C values of organic compounds from a Mazon Creek concretion (Illinois) preserving a coprolite (see below).
Compound-specific isotope analysis (CSIA) allows the stable isotope analysis of individual compounds in complex mixtures of sedimentary OM (Grice and Brocks, 2011). The technique was first developed for carbon (δ13C) and nitrogen (δ15N) (Matthews and Hayes, 1978), and has since been applied to hydrogen (δ2H, commonly written as δD) (Burgoyne and Hayes, 1998) and sulfur (δ34S) (Amrani et al., 2009). The technical requirements for reliable and reproducible measurements are sufficient peak height for accurate measurement of the minor isotopes, and typically also baseline separation of peaks to allow the entire peak to be integrated without interference (Sessions, 2006; N.B. not necessary for δ34S CSIA).
Challenges and future directions
The investigation of mineral concretions and their capacity to sequester the organic remains of extant organisms is still a relatively new and immature science. The information that concretions can convey about ancient organisms and ecosystems is primarily derived from the detection of molecular biomarkers (or distinctive morphological features) from the well-preserved fossils sequestered within them (Figure 8, Approach 1). Prior to the end goal of biomarker analysis, however, a large number and variety of other analytical approaches can assist the selection and interrogation of concretions with promising fossil targets. Different analytical approaches that can help to exploit this largely untapped biochemical record range from (i) fundamental evaluation of concretion formation controls for a better understanding of the propensity and distribution of those likely to sequester and preserve ancient organisms (Figure 8, Approach 1); to (ii) in situ characterization and imaging techniques able to identify concretions with promising fossil targets for more detailed geochemical analyses; and (iii) detailed geochemical characterization of the microfossils themselves.
This review has outlined promising methodologies utilized in preliminary studies exploring the chemistry of concretion-encapsulated fossils. Despite early advances in the development and application of techniques that have helped define concretion formation processes and characterize their OM record — including at submicroscopic morphologies and biochemical composition levels — this research area is best considered to be at a developmental stage. There is still much to learn about the mechanisms and controls on microbially mediated concretions and their preservation of NOM under different paleoenvironmental conditions. To better exploit the biological and geological information that fossiliferous concretions present, a number of research challenges will need to be addressed:
More effective literary, analytical and application integration of complementary Earth Science disciplines involved in concretion research, including microbiology, molecular biology, organic and inorganic geochemistry, paleontology and mineralogy. For instance, the role of various biogeochemical factors in the fossilization process (including those that have previously been implicated) can be further elucidated through studies of modern mineralogy, microbes, genes, and surface physicochemistry. Detailed observation and understanding of these parameters and processes will enable a better understanding of the environmental settings that led to concretion formation in deep time.
Design and develop laboratory simulations and modeling technology to evaluate field-based inferences of fossilization formation mechanisms (Figure 8, Approach 2). These microbial–mineral related processes are complex and often difficult to unravel directly from microbial, mineral and fossil data from the field, but can be systematically evaluated in artificially controlled situations or predicted from intelligent system models. Wide field data collection, including samples from different locations and timescales, will be important to guide the direction of laboratory experiments (Figure 8). The integration of large field, simulated and modeled data sets will provide new insights about microbe–mineral interactions in different concretion-forming environments (e.g., marine and non-marine settings).
Successful identification and selection of concretions that host the most promising fossils (i.e., the largest and most morphologically intact) will require the development and application of new field tools. Current evaluations of impregnated fossils with traditional imaging and other methods remain challenging. Development of new and accessible methods able to support in situ interrogation of organismic fossils, both in the field and laboratory would be highly beneficial. Appropriate field application will conveniently help to lessen downstream analytical loads.
Molecular speciation of organic sediments involves sophisticated, time-consuming procedures, restricting timely analytical processing of samples. The analytical challenges are intensified when conducted on trace amounts of organic analyses (well-preserved fossils are often very small) where particularly meticulous protocols need to be implemented to distinguish sample from background signals. This can be exacerbated when baseline organic signals are high (NB. biologically rich paleo-environments can result in highly dispersed organic content), which is the case at several famous sites with fossiliferous concretions, including the Carboniferous deposits at Mazon Creek, Illinois (coincident with a Pennsylvanian coal seam), the Eocene Green River Formation, Utah (oil shale formation); and the Cambrian Alum Shale, Sweden (shale rich; also high uranium concentration contributing to the radiological alteration of OM). New physical separation techniques able to better isolate fossils will be highly beneficial.
Research scientists are not always the most effective communicators, either within or beyond their direct research communities. Various logistics (e.g., time, lack of training) can challenge the public communication of research outcomes and the engagement of scientists in outreach initiatives. Nevertheless, scientists have an obligation (especially if backed by public funding) to openly communicate and share the results of their work, particularly those which tangibly impact society. The analysis of ancient organisms that are exceptionally preserved within mineral concretions will provide new information about evolutionary processes on Earth. A higher resolution of environmental and biological paleo-dynamics will add valuable context to understanding contemporary environmental and Earth science (ESS) issues, including modern climate change. Paleoenvironmental reconstructions help climate scientists assess the resilience of our planet’s biosphere, as well as its capacity to cope with and regulate widely fluctuating climate conditions. They also enable climate scientists to more accurately predict the environmental and ecological consequences of present-day climate trajectories – some of which are at close to historical highs (e.g., atmospheric temperature and CO2 rises over the last 200 years). An intensifying community focus on climate change presents an opportunity to improve societal understanding, attitudes, and behavior toward the environment (Bradley et al., 1999; Ballantyne et al., 2001). Effective communication and educational leverage of Earth Science (e.g., concretionary fossil) and climate change research will help to raise the EES literacy of the general public, including students (the next generation of Earth Scientists) who often have soft subject perceptions about ESS due to greater curricula focus on traditional science and mathematics subjects (Burg, 2003; Dawson and Carson, 2013). A basic EES learning will help to balance climate change perceptions, avoiding unwarranted alarm, but also encourage support for the phasing out of harmful industrial activities as societies transition to more environmentally sustainable practices. Effective science outreach programs should incorporate a variety of approaches, including but not limited to digital content, in-person events, workshops, media appearances, school visits, partnered programs and citizen science.
Statements
Author contributions
ND, PG, SP, and KG wrote the manuscript as the leading authors. KG provided Figures 1, 8. MT and KG prepared Figures 5, 6 with input from other co-authors. AE prepared Figures 2, 7 with input from co-authors. AE and SP prepared Figure 3 and Table 1 with input from co-authors. HV and ND provided Figure 4 with input from co-authors. Table 2 was prepared by AE, PG, AH and KG along with other co-authors. All authors contributed to the article and approved the submitted version.
Funding
This research was funded by Australian Research Council (ARC) for an ARC-Laureate Fellowship grant (FL210100103) to KG.
Acknowledgments
The authors acknowledge Victor Leshyk for providing concept figures for ARC Laureate proposal included here.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
References
1
AhlbergP.TrinajsticK.JohansonZ.LongJ. (2009). Pelvic claspers confirm chondrichthyan-like internal fertilization in arthrodires. Nature460, 888–889. doi: 10.1038/nature08176
2
AizenshtatZ.KreinE. B.VairavamurthyM. A.GoldsteinT. P. (1995). “Role of sulfur in the transformations of sedimentary organic matter: a mechanistic overview” in Geochemical transformations of sedimentary sulfur. eds. VairavamurthyM. A.SchoonenM. A. A. (Washington, D.C.: American Chemical Society), 16–37.
3
Al DisiZ. A.ZouariN.DittrichM.JaouaS.Al-KuwariH. A. S.BontognaliT. R. R. (2019). Characterization of the extracellular polymeric substances (EPS) of Virgibacillus strains capable of mediating the formation of high mg-calcite and protodolomite. Mar. Chem.216:103693. doi: 10.1016/j.marchem.2019.103693
4
AllisonP. A. (1988a). The role of anoxia in the decay and mineralization of proteinaceous macro- fossils. Paleobiology14, 139–154. doi: 10.1017/S009483730001188X
5
AllisonP. A. (1988b). Taphonomy of the Eocene London clay biota. Palaeontology31, 1079–1100.
6
AllisonP. A.BottjerD. J. (eds.). (2011). Taphonomy: Process and Bias through time. Dordrecht: Springer.
7
AllisonP. A.PyeK. (1994). Early diagenetic mineralization and fossil preservation in modern carbonate concretions. PALAIOS9, 561–575. doi: 10.2307/3515128
8
AmraniA.SessionsA. L.AdkinsJ. F. (2009). Compound-specific δ34S analysis of volatile organics by coupled GC/multicollector-ICPMS. Anal. Chem.81, 9027–9034. doi: 10.1021/ac9016538
9
ArcherA. W.KuecherG. J.KvaleE. P. (1995). The role of tidal-velocity asymmetries in the deposition of silty tidal rhythmites (carboniferous, eastern interior Coal Basin, U.S.a.). J. Sediment. Res.65, 408–416. doi: 10.1306/d42680d6-2b26-11d7-8648000102c1865d
10
ArenaD. A. (2008). Exceptional preservation of plants and invertebrates by phosphatization, Riversleigh, Australia. PALAIOS23, 495–502. doi: 10.2110/palo.2006.p06-142r
11
ArratiaG.SchultzeH.-P. (1999). “Mesozoic fishes from Chile” in Mesozoic fishes 2 – systematics and fossil record. eds. ArratiaG.SchultzeH.-P. (Munich: Verlag Dr. Friedrich Pfeil), 565–593.
12
BabiloniaJ.ConesaA.CasaburiG.PereiraC.LouyakisA. S.ReidR. P.et al. (2018). Comparative metagenomics provides insight into the ecosystem functioning of the Shark Bay stromatolites, Western Australia. Front. Microbiol.9:1359. doi: 10.3389/fmicb.2018.01359
13
BaiY.GuoX.-J.LiY.-Z.HuangT. (2017). Experimental and visual research on the microbial induced carbonate precipitation by Pseudomonas aeruginosa. AMB Express7:57. doi: 10.1186/s13568-017-0358-5
14
BainsA.DhamiN. K.MukherjeeA.ReddyM. S. (2015). Influence of exopolymeric materials on bacterially induced mineralization of carbonates. Appl. Biochem. Biotech.175, 3531–3541. doi: 10.1007/s12010-015-1524-3
15
BairdG. C.ShabicaC. W.AndersonJ. L.RichardsonE. S. (1985a). Biota of a Pennsylvanian muddy coast: habitats within the Mazonian delta complex, Northeast Illinois. J. Paleontol.59, 253–281.
16
BairdG. C.SrokaS. D.ShabicaC. W.BeardT. L.ScottA. C.BroadhurstF. M.et al. (1985b). Mazon Creek-type fossil assemblages in the U.S. midcontinent Pennsylvanian: their recurrent character and palaeoenvironmental significance. Philos. T. R. Soc. Lon. B311, 87–99. doi: 10.1098/rstb.1985.0141
17
BairdG. C.SrokaS. D.ShabicaC. W.KuecherG. J. (1986). Taphonomy of middle Pennsylvanian Mazon Creek area fossil localities, Northeast Illinois: significance of exceptional fossil preservation in syngenetic concretions. PALAIOS1, 271–285. doi: 10.2307/3514690
18
BallantyneR.FienJ.PackerJ. (2001). School environmental education programme impacts upon student and family learning: a case study analysis. Environ. Educ. Res.7, 23–37. doi: 10.1080/13504620124123
19
BattisonL.BrasierM. D. (2012). Remarkably preserved prokaryote and eukaryote microfossils within 1Ga-old lake phosphates of the Torridon group. NW Scotland. Precambrian Res.196-197, 204–217. doi: 10.1016/j.precamres.2011.12.012
20
BaturinG. N. (1971). Stages of phosphorite formation on the ocean floor. Nat. Phys. Sci.232, 61–62. doi: 10.1038/physci232061a0
21
BaumgartnerR. J.TeeceB. L.RasmussenB.MuhlingJ.RickardW. D. A.PejcicB.et al. (2023). Exceptional preservation of organic matter and iron-organic colloidal mineralization in hydrothermal black smoker-type sulfide mineralization from the Paleoarchean seafloor. Chem. Geol.618:121296. doi: 10.1016/j.chemgeo.2022.121296
22
BengtsonS.BuddG. (2004). Comment on small bilaterian fossils from 40 to 55 million years before the Cambrian. Science306:1291. doi: 10.1126/science.1101338
23
BengtsonS.SallstedtT.BelivanovaV.WhitehouseM. (2017). Three-dimensional preservation of cellular and subcellular structures suggests 1.6 billion-year-old crown-group red algae. PLoS Biol.15:e2000735. doi: 10.1371/journal.pbio.2000735
24
BenítezJ. J.Guzman-PuyolS.DomínguezE.HerediaA.Heredia-GuerreroJ. A. (2019). Applications and potentialities of atomic force microscopy in fossil and extant plant cuticle characterization. Rev. Palaeobot. Palyno.268, 125–132. doi: 10.1016/j.revpalbo.2019.06.015
25
BentorY. K. (1980). “Phosphorites—the unsolved problems” in Marine Phosphorites—Geochemistry, occurrence, genesis. ed. BentorY. K. (Tulsa, Oklahoma: SEPM Society for Sedimentary Geology), 3–19.
26
BergesJ. A.FranklinD. J.HarrisonP. J. (2001). Evolution of an artificial seawater medium: improvements in enriched seawater, artificial water over the last two decades. J. Phycol.37, 1138–1145. doi: 10.1046/j.1529-8817.2001.01052.x
27
BernerR. A. (1968a). Calcium carbonate concretions formed by the decomposition of organic matter. Science159, 195–197. doi: 10.1126/science.159.3811.195
28
BernerR. A. (1968b). Rate of concretion growth. Geochim. Cosmochim. Ac.32, 477–483. doi: 10.1016/0016-7037(68)90040-9
29
BernerR. A. (1969). Chemical changes affecting dissolved calcium during the bacterial decomposition of fish and clams in sea water. Mar. Geol.7, 253–274. doi: 10.1016/0025-3227(69)90011-5
30
BernerR. A. (1985). Sulphate reduction, organic matter decomposition and pyrite formation. Philos. T. R. Soc. Lon. A315, 25–38. doi: 10.1098/rsta.1985.0027
31
BevittJ. J. (2018). Discovering dinosaurs with neutrons. Nat. Rev. Mater.3, 296–298. doi: 10.1038/s41578-018-0049-0
32
BickelS. L.TangK. W. (2010). Microbial decomposition of proteins and lipids in copepod versus rotifer carcasses. Mar. Biol.157, 1613–1624. doi: 10.1007/s00227-010-1434-4
33
BoatmanE. M.GoodwinM. B.HolmanH.-Y. N.FakraS.ZhengW.GronskyR.et al. (2019). Mechanisms of soft tissue and protein preservation in tyrannosaurus rex. Sci. Rep.9:15678. doi: 10.1038/s41598-019-51680-1
34
BojanowskiM. J.ClarksonE. N. K. (2012). Origin of siderite concretions in microenvironments of methanogenesis developed in a sulfate reduction zone: an exception or a rule?J. Sediment. Res.82, 585–598. doi: 10.2110/jsr.2012.50
35
BolhuisH.FillingerL.StalL. J. (2013). Coastal microbial mat diversity along a natural salinity gradient. PLoS One8:e63166. doi: 10.1371/journal.pone.0063166
36
BradleyJ. C.WaliczekT. M.ZajicekJ. M. (1999). Relationship between environmental knowledge and environmental attitude of high school students. J. Environ. Educ.30, 17–21. doi: 10.1080/00958969909601873
37
BragaP. C.RicciD. (1998). Atomic force microscopy: application to investigation of Escherichia coli morphology before and after exposure to cefodizime. Antimicrob. Agents Ch.42, 18–22. doi: 10.1128/AAC.42.1.18
38
BrasierM. D.AntcliffeJ.SaundersM.WaceyD. (2015). Changing the picture of Earth's earliest fossils (3.5-1.9 Ga) with new approaches and new discoveries. P. Natl. Acad. Sci. USA112, 4859–4864. doi: 10.1073/pnas.1405338111
39
BriggsD. E. G. (1995a). Experimental taphonomy. PALAIOS10, 539–550. doi: 10.2307/3515093
40
BriggsD. E. G. (1995b). Preservation of soft tissues in the fossil record. Eclogae Geol. Helv.88, 623–626.
41
BriggsD. E. G. (2003a). “The role of biofilms in the fossilization of non-biomineralized tissues” in Fossil and recent biofilms: A natural history of life on earth. eds. KrumbeinW. E.PatersonD. M.ZavarzinG. A. (Dordrecht: Springer Netherlands), 281–290.
42
BriggsD. E. G. (2003b). The role of decay and mineralization in the preservation of soft-bodied fossils. Annu. Rev. Earth Pl. Sc.31, 275–301. doi: 10.1146/annurev.earth.31.100901.144746
43
BriggsD. E. G.KearA. J. (1993a). Decay and preservation of polychaetes: taphonomic thresholds in soft-bodied organisms. Paleobiology19, 107–135. doi: 10.1017/S0094837300012343
44
BriggsD. E. G.KearA. J. (1993b). Decay of Branchiostoma: implications for soft-tissue preservation in conodonts and other primitive chordates. Lethaia26, 275–287. doi: 10.1111/j.1502-3931.1993.tb01532.x
45
BriggsD. E. G.KearA. J. (1993c). Fossilization of soft tissue in the laboratory. Science259, 1439–1442. doi: 10.1126/science.259.5100.1439
46
BriggsD. E. G.KearA. J.MartillD. M.WilbyP. R. (1993). Phosphatization of soft-tissue in experiments and fossils. J. Geol. Soc.150, 1035–1038. doi: 10.1144/gsjgs.150.6.1035
47
BriggsD. E. G.MooreR. A.ShultzJ. W.SchweigertG. (2005). Mineralization of soft-part anatomy and invading microbes in the horseshoe crab Mesolimulus from the upper Jurassic Lagerstätte of Nusplingen, Germany. P. Roy. Soc. B-Biol. Sci.272, 627–632. doi: 10.1098/rspb.2004.3006
48
BriggsD. E. G.RaiswellR.BottrellS. H.HatfieldD.BartelsC. (1996). Controls on the pyritization of exceptionally preserved fossils; an analysis of the lower Devonian Hunsrueck slate of Germany. Am. J. Sci.296, 633–663. doi: 10.2475/ajs.296.6.633
49
BriggsD. E. G.WilbyP. R. (1996). The role of the calcium carbonate-calcium phosphate switch in the mineralization of soft-bodied fossils. J. Geol. Soc.153, 665–668. doi: 10.1144/gsjgs.153.5.0665
50
BrockT. D. (1999). Robert Koch: A life in medicine and bacteriology. Washington, DC: American Society of Microbiology Press.
51
BrockJ.Schulz-VogtH. N. (2011). Sulfide induces phosphate release from polyphosphate in cultures of a marine Beggiatoa strain. ISME J.5, 497–506. doi: 10.1038/ismej.2010.135
52
BrocksJ. J.SummonsR. E. (2014). “Sedimentary hydrocarbons, biomarkers for early life” in Treatise on geochemistry (second edition) volume 10: Biogeochemistry. eds. KarlD. M.SchlesingerW. H. (Oxford: Elsevier), 61–103.
53
BurgK. (2003). Earth and environmental science: where to from here?Sci. Educ. News52, 61–66. doi: 10.3316/aeipt.129850
54
BurgoyneT. W.HayesJ. M. (1998). Quantitative production of H2 by pyrolysis of gas chromatographic effluents. Anal. Chem.70, 5136–5141. doi: 10.1021/ac980248v
55
ButlerA. D.CunninghamJ. A.BuddG. E.DonoghueP. C. J. (2015). Experimental taphonomy of Artemia reveals the role of endogenous microbes in mediating decay and fossilization. P. Roy. Soc. B-Biol. Sci.282:20150476. doi: 10.1098/rspb.2015.0476
56
ButtsS. H.BriggsD. E. G. (2011). “Silicification through time” in Taphonomy: Process and Bias through time. eds. AllisonP. A.BottjerD. J. (Dordrecht: Springer Netherlands), 411–434.
57
CallefoF.MaldanisL.TeixeiraV. C.AbansR. A. D. O.MonfrediniT.RodriguesF.et al. (2019). Evaluating biogenicity on the geological record with synchrotron-based techniques. Front. Microbiol.10:2358. doi: 10.3389/fmicb.2019.02358
58
CampbellM. A.CoolenM. J. L.VisscherP. T.MorrisT.GriceK. (2021). Structure and function of Shark Bay microbial communities following tropical cyclone Olwyn: a metatranscriptomic and organic geochemical perspective. Geobiology19, 642–664. doi: 10.1111/gbi.12461
59
CapoE.MonchampM.-E.CoolenM. J. L.DomaizonI.ArmbrechtL.BertilssonS. (2022). Environmental paleomicrobiology: using DNA preserved in aquatic sediments to its full potential. Environ. Microbiol.24, 2201–2209. doi: 10.1111/1462-2920.15913
60
CarpenterK. (2005). Experimental investigation of the role of bacteria in bone fossilization. Neues. Jahrb. Geol. P. M.2005, 83–94. doi: 10.1127/njgpm/2005/2005/83
61
CasellaL. A.Simonet RodaM. D. M.AngioliniL.ZieglerA.SchmahlW. W.BrandU.et al. (2018). Archival biogenic micro- and nanostructure data analysis: signatures of diagenetic systems. Data Brief19, 299–311. doi: 10.1016/j.dib.2018.05.041
62
ChapinK. C.LauderdaleT. L. (2007). “Reagents, stains, and media: bacteriology” in Manual of clinical microbiology. eds. MurrayP. R.BaronE. J.JorgensenJ. H.LandryM. L.PfallerM. A.. 9th ed (Washington, D.C.: ASM Press), 334–364.
63
ChatterjeeS.BiswasN.DattaA.DeyR.MaitiP. (2014). Atomic force microscopy in biofilm study. Microscopy63, 269–278. doi: 10.1093/jmicro/dfu013
64
ChernsL.SpencerA. R. T.RahmanI. A.GarwoodR. J.ReedmanC.BurcaG.et al. (2022). Correlative tomography of an exceptionally preserved Jurassic ammonite implies hyponome-propelled swimming. Geology50, 397–401. doi: 10.1130/g49551.1
65
ClementsT.PurnellM.GabbottS. (2018). The Mazon Creek Lagerstätte: a diverse late Paleozoic ecosystem entombed within siderite concretions. J. Geol. Soc.176, 1–11. doi: 10.1144/jgs2018-088
66
CliftonH. E. (1957). The carbonate concretions of the Ohio shale. Ohio J. Sci.57, 114–124.
67
ColemanM. L. (1993). Microbial processes: controls on the shape and composition of carbonate concretions. Mar. Geol.113, 127–140. doi: 10.1016/0025-3227(93)90154-N
68
ColemanM. L.RaiswellR. (1981). Carbon, oxygen and Sulphur isotope variations in concretions from the upper Lias of N.E. England. Geochim. Cosmochim. Acta45, 329–340. doi: 10.1016/0016-7037(81)90243-X
69
ColemanM. L.RaiswellR. (1995). Source of carbonate and origin of zonation in pyritiferous carbonate concretions; evaluation of a dynamic model. Am. J. Sci.295, 282–308. doi: 10.2475/ajs.295.3.282
70
CoronadoI.Fernández-MartínezE.RodríguezS.TourneurF. (2015). Reconstructing a carboniferous inferred coral–alcyonarian association using a biomineralogical approach. Geobiology13, 340–356. doi: 10.1111/gbi.12133
71
CostertonJ. W.LewandowskiZ.CaldwellD. E.KorberD. R.Lappin-ScottH. M. (1995). Microbial biofilms. Annu. Rev. Microbiol.49, 711–745. doi: 10.1146/annurev.mi.49.100195.003431
72
CotroneoS.SchiffbauerJ. D.McCoyV. E.WortmannU. G.DarrochS. A. F.PengY.et al. (2016). A new model of the formation of Pennsylvanian iron carbonate concretions hosting exceptional soft-bodied fossils in Mazon Creek, Illinois. Geobiology14, 543–555. doi: 10.1111/gbi.12197
73
CroudaceI. W.RindbyA.RothwellR. G. (2006). “ITRAX: description and evaluation of a new multi-function X-ray core scanner” in New techniques in sediment Core analysis. ed. RothwellR. G., vol. 267 (London: Geological Society, London, Special Publications), 51–63.
74
CunninghamJ. A.DonoghueP. C. J.BengtsonS. (2014). Distinguishing biology from geology in soft-tissue preservation. Paleontol. Soc. Papers20, 275–288. doi: 10.1017/S1089332600002898
75
CurtisC. D.ColemanM. L.LoveL. G. (1986). Pore water evolution during sediment burial from isotopic and mineral chemistry of calcite, dolomite and siderite concretions. Geochim. Cosmochim. Ac.50, 2321–2334. doi: 10.1016/0016-7037(86)90085-2
76
CurtisC. D.PetrowskiC.OertelG. (1972). Stable carbon isotope ratios within carbonate concretions: a clue to place and time of formation. Nature235, 98–100. doi: 10.1038/235098a0
77
DangH.LovellC. R. (2016). Microbial surface colonization and biofilm development in marine environments. Microbiol. Mol. Biol. R.80, 91–138. doi: 10.1128/MMBR.00037-15
78
DawsonV.CarsonK. (2013). Science teachers’ and senior secondary schools students’ perceptions of earth and environmental science topics. Aust. J. Environ. Edu.29, 202–220. doi: 10.1017/aee.2014.6
79
DawsonM.FrancisJ.CarpenterR. (2014). New views of plant fossils from Antarctica: a comparison of X-ray and neutron imaging techniques. J. Paleontol.88, 702–707. doi: 10.1666/13-124
80
De CraenM.SwennenR.KeppensE. M.MacaulayC. I.KiriakoulakisK. (1999). Bacterially mediated formation of carbonate concretions in the Oligocene boom clay of northern Belgium. J. Sediment. Res.69, 1098–1106. doi: 10.2110/jsr.69.1098
81
De LurioJ. L.FrakesL. A. (1999). Glendonites as a paleoenvironmental tool: implications for early cretaceous high latitude climates in Australia. Geochim. Cosmochim. Acta63, 1039–1048. doi: 10.1016/S0016-7037(99)00019-8
82
DenceW. A. (1956). Concretions of the alewife, Pomolobus pseudoharengus (Wilson), at Onondaga Lake, New York. Copeia1956, 155–158. doi: 10.2307/1439629
83
DhamiN. K.AlsubhiW. R.WatkinE.MukherjeeA. (2017). Bacterial community dynamics and biocement formation during stimulation and augmentation: implications for soil consolidation. Front. Microbiol.8:1267. doi: 10.3389/fmicb.2017.01267
84
DhamiN. K.ReddyM. S.MukherjeeA. (2012). Improvement in strength properties of ash bricks by bacterial calcite. Ecol. Eng.39, 31–35. doi: 10.1016/j.ecoleng.2011.11.011
85
DhamiN. K.ReddyM. S.MukherjeeA. (2013a). Biomineralization of calcium carbonate polymorphs by the bacterial strains isolated from calcareous sites. J. Microbiol. Biotechnol.23, 707–714. doi: 10.4014/jmb.1212.11087
86
DhamiN. K.ReddyM. S.MukherjeeA. (2013b). Biomineralization of calcium carbonates and their engineered applications: a review. Front. Microbiol.4:314. doi: 10.3389/fmicb.2013.00314
87
DhamiN. K.ReddyM. S.MukherjeeA. (2016). Significant indicators for biomineralisation in sand of varying grain sizes. Constr. Build. Mater.104, 198–207. doi: 10.1016/j.conbuildmat.2015.12.023
88
DiasJ. J.CarvalhoI. d. S. (2022). The role of microbial mats in the exquisite preservation of Aptian insect fossils from the Crato Lagerstätte, Brazil. Cretaceous Res.130:105068. doi: 10.1016/j.cretres.2021.105068
89
DittrichM.SiblerS. (2005). Cell surface groups of two picocyanobacteria strains studied by zeta potential investigations, potentiometric titration, and infrared spectroscopy. J. Colloid Interf. Sci.286, 487–495. doi: 10.1016/j.jcis.2005.01.029
90
DongH.HuangL.ZhaoL.ZengQ.LiuX.ShengY.et al. (2022). A critical review of mineral–microbe interaction and co-evolution: mechanisms and applications. Natl. Sci. Rev.9:128. doi: 10.1093/nsr/nwac128
91
DongY.SanfordR. A.InskeepW. P.SrivastavaV.BuloneV.FieldsC. J.et al. (2019). Physiology, metabolism, and fossilization of hot-spring filamentous microbial mats. Astrobiology19, 1442–1458. doi: 10.1089/ast.2018.1965
92
DornbosS. Q. (2011). “Phosphatization through the Phanerozoic” in Taphonomy: Process and Bias through time. eds. AllisonP. A.BottjerD. J. (Dordrecht: Springer Netherlands), 435–456.
93
DownenM. R.SchiffbauerJ. D.SeldenP. A.OlcottA. N. (2022). Steinkern spiders: a microbial mat-controlled taphonomic pathway in the Oligocene Aix-En-Provence Lagerstätte, France. Palaeoentomology5, 524–536. doi: 10.11646/palaeoentomology.5.6.4
94
DrozdJ. (1981). Chemical derivatization in gas chromatography – journal of chromatography library, 19. Amsterdam: Elsevier.
95
DubeyA. A.MuruganR.RaviK.MukherjeeA.DhamiN. K. (2022). Investigation on the impact of cementation media concentration on properties of biocement under stimulation and augmentation approaches. J. Hazard. Tox. Radioact. Waste26:04021050. doi: 10.1061/(ASCE)HZ.2153-5515.0000662
96
DunnK. A.McLeanR. J. C.UpchurchG. R.Jr.FolkR. L. (1997). Enhancement of leaf fossilization potential by bacterial biofilms. Geology25, 1119–1122. doi: 10.1130/0091-7613(1997)025<1119:EOLFPB>2.3.CO;2
97
DuprazC.ReidR. P.BraissantO.DechoA. W.NormanR. S.VisscherP. T. (2009). Processes of carbonate precipitation in modern microbial mats. Earth-Sci. Rev.96, 141–162. doi: 10.1016/j.earscirev.2008.10.005
98
DuprazC.VisscherP. T. (2005). Microbial lithification in marine stromatolites and hypersaline mats. Trends Microbiol.13, 429–438. doi: 10.1016/j.tim.2005.07.008
99
DworatzekM. (1987). "Sedimentology and petrology of carbonate intercalations in the upper Cambrian Olenid shale facies of southern Sweden". (Uppsala: Sveriges Geologiska Undersökning).
100
EaganJ. L.AndrewsM. E.PearsonR. L.TurnerF. R.RaffE. C.RaffR. A. (2017). Identification and modes of action of endogenous bacteria in taphonomy of embryos and larvae. PALAIOS32, 206–217. doi: 10.2110/palo.2016.071
101
EisenhoferR.WeyrichL. S. (2019). Assessing alignment-based taxonomic classification of ancient microbial DNA. PeerJ7:e6594. doi: 10.7717/peerj.6594
102
ErcoleC.BozzelliP.AltieriF.CacchioP.Del GalloM. (2012). Calcium carbonate mineralization: involvement of extracellular polymeric materials isolated from calcifying bacteria. Microsc. Microanal.18, 829–839. doi: 10.1017/S1431927612000426
103
ErcoleC.CacchioP.BottaA. L.CentiV.LepidiA. (2007). Bacterially induced mineralization of calcium carbonate: the role of exopolysaccharides and capsular polysaccharides. Microsc. Microanal.13, 42–50. doi: 10.1017/S1431927607070122
104
ErikssonM. E.De La GarzaR.HornE.LindgrenJ. (2022). A review of ichthyosaur (Reptilia, Ichthyopterygia) soft tissues with implications for life reconstructions. Earth-Sci. Rev.226:103965. doi: 10.1016/j.earscirev.2022.103965
105
EspitaliéJ.LaporteJ. L.MadecM.MarquisF.LeplatP.PauletJ.et al. (1977). Méthode rapide de caractérisation des roches mètres, de leur potentiel pétrolier et de leur degré d'évolution. Rev. Inst. Fr. Pét.32, 23–42. doi: 10.2516/ogst:1977002
106
FabbriM.WiemannJ.ManucciF.BriggsD. E. G. (2020). Three-dimensional soft tissue preservation revealed in the skin of a non-avian dinosaur. Palaeontology63, 185–193. doi: 10.1111/pala.12470
107
FaraE.SaraivaA. Á. F.de Almeida CamposD.MoreiraJ. K. R.de Carvalho SiebraD.KellnerA. W. A. (2005). Controlled excavations in the Romualdo member of the Santana formation (early cretaceous, Araripe Basin, northeastern Brazil): stratigraphic, palaeoenvironmental and palaeoecological implications. Palaeogeogr. Palaeocl.218, 145–160. doi: 10.1016/j.palaeo.2004.12.012
108
FarmerJ. D.Des MaraisD. J. (1999). Exploring for a record of ancient Martian life. J. Geophys. Res.-Planet.104, 26977–26995. doi: 10.1029/1998JE000540
109
FarrellÚ. C. (2014). Pyritization of soft tissues in the fossil record: an overview. Paleontol. Soc. Papers20, 35–58. doi: 10.1017/S1089332600002795
110
FöllmiK. B. (1996). The phosphorus cycle, phosphogenesis and marine phosphate-rich deposits. Earth-Sci. Rev.40, 55–124. doi: 10.1016/0012-8252(95)00049-6
111
FrankelR. B.BazylinskiD. A. (2003). Biologically induced mineralization by bacteria. Rev. Mineral. Geochem.54, 95–114. doi: 10.2113/0540095
112
GäbF.BallhausC.StinnesbeckE.KralA. G.JanssenK.BierbaumG. (2020). Experimental taphonomy of fish – role of elevated pressure, salinity and pH. Sci. Rep.10:7839. doi: 10.1038/s41598-020-64651-8
113
GainesR. R.BriggsD. E. G.OrrP. J.Van RoyP. (2012). Preservation of giant anomalocaridids in silica-chlorite concretions from the early Ordovician of Morocco. PALAIOS27, 317–325. doi: 10.2110/palo.2011.p11-093r
114
GainesR. R.VorhiesJ. S. (2016). Growth mechanisms and geochemistry of carbonate concretions from the Cambrian wheeler formation (Utah, USA). Sedimentology63, 662–698. doi: 10.1111/sed.12234
115
GarnatjeT.PeñuelasJ.VallèsJ. (2017). Ethnobotany, phylogeny, and ‘omics’ for human health and food security. Trends Plant Sci.22, 187–191. doi: 10.1016/j.tplants.2017.01.001
116
GautierD. L. (1982). Siderite concretions; indicators of early diagenesis in the gammon shale (cretaceous). J. Sediment. Res.52, 859–871. doi: 10.1306/212f8076-2b24-11d7-8648000102c1865d
117
GehlingJ. G. (1999). Microbial mats in terminal Proterozoic siliciclastics; Ediacaran death masks. PALAIOS14, 40–57. doi: 10.2307/3515360
118
GelinF.de LeeuwJ. W.Sinninghe DamstéJ. S.DerenneS.LargeauC.MetzgerP. (1994). The similarity of chemical structures of soluble aliphatic polyaldehyde and insoluble algaenan in the green microalga Botryococcus braunii race a as revealed by analytical pyrolysis. Org. Geochem.21, 423–435. doi: 10.1016/0146-6380(94)90094-9
119
GothK.de LeeuwJ. W.PüttmannW.TegelaarE. W. (1988). Origin of Messel oil shale kerogen. Nature336, 759–761. doi: 10.1038/336759a0
120
GreenwaltD. E.GorevaY. S.SiljeströmS. M.RoseT.HarbachR. E. (2013). Hemoglobin-derived porphyrins preserved in a middle Eocene blood-engorged mosquito. P. Natl. Acad. Sci. USA110, 18496–18500. doi: 10.1073/pnas.1310885110
121
GrenJ. A.SjövallP.ErikssonM. E.SylvestersenR. L.MaroneF.Sigfridsson ClaussK. G. V.et al. (2017). Molecular and microstructural inventory of an isolated fossil bird feather from the Eocene Fur formation of Denmark. Palaeontology60, 73–90. doi: 10.1111/pala.12271
122
GriceK.AudinoM.BorehamC. J.AlexanderR.KagiR. I. (2001). Distributions and stable carbon isotopic compositions of biomarkers in torbanites from different palaeogeographical locations. Org. Geochem.32, 1195–1210. doi: 10.1016/S0146-6380(01)00087-0
123
GriceK.BrocksJ. J. (2011). “Biomarkers (organic, compound-specific isotopes)” in Encyclopedia of Geobiology. eds. ReitnerJ.ThielV. (Dordrecht: The Netherlands Springer), 167–182.
124
GriceK.EiserbeckC. (2014). “The analysis and application of biomarkers” in Treatise on geochemistry (second edition) volume 12: Organic geochemistry. eds. FalkowskiP. G.FreemanK. H. (Oxford: Elsevier), 47–78.
125
GriceK.HolmanA. I.PletC.TrippM. (2019). Fossilised biomolecules and biomarkers in carbonate concretions from Konservat-Lagerstätten. Fortschr. Mineral.9:158. doi: 10.3390/min9030158
126
GriceK.SchaefferP.SchwarkL.MaxwellJ. R. (1996). Molecular indicators of palaeoenvironmental conditions in an immature Permian shale (Kupferschiefer, lower Rhine Basin, north-West Germany) from free and S-bound lipids. Org. Geochem.25, 131–147. doi: 10.1016/S0146-6380(96)00130-1
127
GriceK.SchaefferP.SchwarkL.MaxwellJ. R. (1997). Changes in palaeoenvironmental conditions during deposition of the Permian Kupferschiefer (lower Rhine Basin, Northwest Germany) inferred from molecular and isotopic compositions of biomarker components. Org. Geochem.26, 677–690. doi: 10.1016/S0146-6380(97)00036-3
128
GriceK.SchoutenS.BlokkerP.DerenneS.LargeauC.NissenbaumA.et al. (2003). Structural and isotopic analysis of kerogens in sediments rich in free sulfurised Botryococcus braunii biomarkers. Org. Geochem.34, 471–482. doi: 10.1016/S0146-6380(02)00187-0
129
GrimesS. T.BrockF.RickardD.DaviesK. L.EdwardsD.BriggsD. E. G.et al. (2001). Understanding fossilization: experimental pyritization of plants. Geology29, 123–126. doi: 10.1130/0091-7613(2001)029<0123:UFEPOP>2.0.CO;2
130
GrotzingerJ. P.KnollA. H. (1999). Stromatolites in Precambrian carbonates: evolutionary mileposts or environmental dipsticks?Annu. Rev. Earth Pl. Sc.27, 313–358. doi: 10.1146/annurev.earth.27.1.313
131
GueriauP.RéguerS.LeclercqN.CupelloC.BritoP. M.JauvionC.et al. (2020). Visualizing mineralization processes and fossil anatomy using synchronous synchrotron X-ray fluorescence and X-ray diffraction mapping. J. R. Soc. Interface17:20200216. doi: 10.1098/rsif.2020.0216
132
GuptaN. S.BriggsD. E. G.CollinsonM. E.EvershedR. P.MichelsR.JackK. S.et al. (2007). Evidence for the in situ polymerisation of labile aliphatic organic compounds during the preservation of fossil leaves: implications for organic matter preservation. Org. Geochem.38, 499–522. doi: 10.1016/j.orggeochem.2006.06.011
133
GutlebenJ.Chaib De MaresM.van ElsasJ. D.SmidtH.OvermannJ.SipkemaD. (2018). The multi-omics promise in context: from sequence to microbial isolate. Crit. Rev. Microb.44, 212–229. doi: 10.1080/1040841X.2017.1332003
134
HammesF.VerstraeteW. (2002). Key roles of pH and calcium metabolism in microbial carbonate precipitation. Rev. Environ. Sci. Bio.1, 3–7. doi: 10.1023/A:1015135629155
135
HayesJ. M. (2001). Fractionation of carbon and hydrogen isotopes in biosynthetic processes. Rev. Mineral. Geochem.43, 225–277. doi: 10.2138/gsrmg.43.1.225
136
HedgesJ. I.KeilR. G. (1995). Sedimentary organic matter preservation: an assessment and speculative synthesis. Mar. Chem.49, 81–115. doi: 10.1016/0304-4203(95)00008-F
137
HeinemannS.HeinemannC.JägerM.NeunzehnJ.WiesmannH. P.HankeT. (2011). Effect of silica and hydroxyapatite mineralization on the mechanical properties and the biocompatibility of nanocomposite collagen scaffolds. ACS Appl. Mater. Inter.3, 4323–4331. doi: 10.1021/am200993q
138
HensonM. W.PitreD. M.WeckhorstJ. L.LanclosV. C.WebberA. T.ThrashJ. C. (2016). Artificial seawater media facilitate cultivating members of the microbial majority from the Gulf of Mexico. mSphere1, e00028–e00016. doi: 10.1128/mSphere.00028-16
139
HilleA.NeuT. R.HempelD. C.HornH. (2005). Oxygen profiles and biomass distribution in biopellets of aspergillus Niger. Biotechnol. Bioeng.92, 614–623. doi: 10.1002/bit.20628
140
HofC. H. J.BriggsD. E. G. (1997). Decay and mineralization of mantis shrimps (Stomatopoda; Crustacea); a key to their fossil record. PALAIOS12, 420–438. doi: 10.2307/3515381
141
HohensteinP. (2004). X-ray imaging for palaeontology. Brit. J. Radiol.77, 420–425. doi: 10.1259/bjr/27832269
142
HudsonJ. D. (1978). Concretions, isotopes, and the diagenetic history of the Oxford clay (Jurassic) of Central England. Sedimentology25, 339–370. doi: 10.1111/j.1365-3091.1978.tb00317.x
143
HuggettJ. M. (1994). Diagenesis of mudrocks and concretions from the London clay formation in the London Basin. Clay Miner.29, 693–707. doi: 10.1180/claymin.1994.029.4.22
144
HuggettJ. M.GaleA. S.EvansS. (2000). Carbonate concretions from the London clay (Ypresian, Eocene) of southern England and the exceptional preservation of wood-boring communities. J. Geol. Soc.157, 187–200. doi: 10.1144/jgs.157.1.187
145
HuntJ. E.CroudaceI. W.MacLachlanS. E. (2015). “Use of calibrated ITRAX XRF data in determining turbidite geochemistry and provenance in Agadir Basin, northwest African passive margin” in Micro-XRF studies of sediment cores: Applications of a non-destructive tool for the environmental sciences. eds. CroudaceI. W.RothwellR. G. (Dordrecht: Springer Netherlands), 127–146.
146
HussainA.HaughtonP. D. W.ShannonP. M.TurnerJ. N.PierceC. S.Obradors-LatreA.et al. (2020). High-resolution X-ray fluorescence profiling of hybrid event beds: implications for sediment gravity flow behaviour and deposit structure. Sedimentology67, 2850–2882. doi: 10.1111/sed.12722
147
IniestoM.Blanco-MorenoC.VillalbaA.BuscalioniÁ. D.GuerreroM. C.López-ArchillaA. I. (2018). Plant tissue decay in long-term experiments with microbial mats. Geosciences8:387. doi: 10.3390/geosciences8110387
148
IniestoM.BuscalioniÁ. D.Carmen GuerreroM.BenzeraraK.MoreiraD.López-ArchillaA. I. (2016). Involvement of microbial mats in early fossilization by decay delay and formation of impressions and replicas of vertebrates and invertebrates. Sci. Rep.6:25716. doi: 10.1038/srep25716
149
IniestoM.Gutiérrez-SilvaP.DiasJ. J.CarvalhoI. S.BuscalioniA. D.López-ArchillaA. I. (2021). Soft tissue histology of insect larvae decayed in laboratory experiments using microbial mats: Taphonomic comparison with cretaceous fossil insects from the exceptionally preserved biota of Araripe, Brazil. Palaeogeogr, Palaeocl.564:110156. doi: 10.1016/j.palaeo.2020.110156
150
IniestoM.LagunaC.FlorínM.GuerreroM. C.ChicoteA.BuscalioniA. D.et al. (2015). The impact of microbial mats and their microenvironmental conditions in early decay of fish. PALAIOS30, 792–801. doi: 10.2110/palo.2014.086
151
IniestoM.Lopez-ArchillaA. I.Fregenal-MartínezM.BuscalioniA. D.GuerreroM. C. (2013). Involvement of microbial mats in delayed decay: an experimental essay on fish preservation. PALAIOS28, 56–66. doi: 10.2110/palo.2011.p11-099r
152
IniestoM.VillalbaI.BuscalioniA. D.GuerreroM. C.López-ArchillaA. I. (2017). The effect of microbial mats in the decay of anurans with implications for understanding taphonomic processes in the fossil record. Sci. Rep.7:45160. doi: 10.1038/srep45160
153
IrwinH.CurtisC.ColemanM. (1977). Isotopic evidence for source of diagenetic carbonates formed during burial of organic-rich sediments. Nature269, 209–213. doi: 10.1038/269209a0
154
JaakkolaS. T.ZerullaK.GuoQ.LiuY.MaH.YangC.et al. (2014). Halophilic archaea cultivated from surface sterilized middle-late Eocene rock salt are polyploid. PLoS One9:e110533. doi: 10.1371/journal.pone.0110533
155
JanssenK.MählerB.RustJ.BierbaumG.McCoyV. E. (2022). The complex role of microbial metabolic activity in fossilization. Biol. Rev.97, 449–465. doi: 10.1111/brv.12806
156
JohnsonR. G.RichardsonE. S. (1966). A remarkable Pennsylvanian Fauna from the Mazon Creek area, Illinois. J. Geol.74, 626–631.
157
KamranA.SchneiderD.RoddatisV.ThielV.HoppertM. (2020). Formation of siderite in microbial microcosms derived from a marine sediment. Geomicrobiol J.37, 475–485. doi: 10.1080/01490451.2020.1725186
158
KempeA.SchopfJ. W.AltermannW.KudryavtsevA. B.HecklW. M. (2002). Atomic force microscopy of Precambrian microscopic fossils. P. Natl. Acad. Sci. USA99, 9117–9120. doi: 10.1073/pnas.142310299
159
KempeA.WirthR.AltermannW.StarkR. W.SchopfJ. W.HecklW. M. (2005). Focussed ion beam preparation and in situ nanoscopic study of Precambrian acritarchs. Precambrian Res.140, 36–54. doi: 10.1016/j.precamres.2005.07.002
160
KiriakoulakisK.MarshallJ. D.WolffG. A. (2000). Biomarkers in a lower Jurassic concretion from Dorset (UK). J. Geol. Soc.157, 207–220. doi: 10.1144/jgs.157.1.207
161
KlugC.CoatesM.FreyL.GreifM.JobbinsM.PohleA.et al. (2023). Broad snouted cladoselachian with sensory specialization at the base of modern chondrichthyans. Swiss J. Palaeo.142:2. doi: 10.1186/s13358-023-00266-6
162
KollmerF. (2004). Cluster primary ion bombardment of organic materials. Appl. Surf. Sci.231-232, 153–158. doi: 10.1016/j.apsusc.2004.03.101
163
KonhauserK. O.NewmanD. K.KapplerA. (2005). The potential significance of microbial Fe(III) reduction during deposition of Precambrian banded iron formations. Geobiology3, 167–177. doi: 10.1111/j.1472-4669.2005.00055.x
164
KrauseD.JachauK. (2002). Späte leichenveränderungen. Rechtsmedizin12, 175–186. doi: 10.1007/s00194-002-0144-8
165
LacziK.Erdeiné KisÁ.SzilágyiÁ.BounedjoumN.BodorA.VinczeG. E.et al. (2020). New frontiers of anaerobic hydrocarbon biodegradation in the multi-omics era. Front. Microbiol.11:590049. doi: 10.3389/fmicb.2020.590049
166
LavilleT.HegnaT. A.ForelM.-B.DarrochS.CharbonnierS. (2023). New look at Concavicaris woodfordi (Euarthropoda: Pancrustacea?) using micro-computed tomography. Palaeontol. Electron.26:26.21.a21. doi: 10.26879/1218
167
LenggerS. K.MelendezI. M.SummonsR. E.GriceK. (2017). Mudstones and embedded concretions show differences in lithology-related, but not source-related biomarker distributions. Org. Geochem.113, 67–74. doi: 10.1016/j.orggeochem.2017.08.003
168
LewisW. H.TahonG.GeesinkP.SousaD. Z.EttemaT. J. G. (2021). Innovations to culturing the uncultured microbial majority. Nat. Rev. Microbiol.19, 225–240. doi: 10.1038/s41579-020-00458-8
169
LheritierM.PerrouxM.VannierJ.EscarguelG.WesenerT.MoritzL.et al. (2023). Fossils from the Montceau-les-mines Lagerstätte (305 Ma) shed light on the anatomy, ecology and phylogeny of carboniferous millipedes. J. Syst. Palaeontol.21:2169891. doi: 10.1080/14772019.2023.2169891
170
LiX.ChoppD. L.RussinW. A.BrannonP. T.ParsekM. R.PackmanA. I. (2015). Spatial patterns of carbonate biomineralization in biofilms. Appl. Environ. Microb.81, 7403–7410. doi: 10.1128/AEM.01585-15
171
LichtmanJ. W.ConchelloJ.-A. (2005). Fluorescence microscopy. Nat. Methods2, 910–919. doi: 10.1038/nmeth817
172
LinL.ChengF.XuJ. (2023). Preservation of molecular fossils in carbonate concretions in cretaceous shales in the songliao basin, Northeast China. Front. Earth Sci.10:1074178. doi: 10.3389/feart.2022.1074178
173
LinC. Y.TurchynA. V.KrylovA.AntlerG. (2020). The microbially driven formation of siderite in salt marsh sediments. Geobiology18, 207–224. doi: 10.1111/gbi.12371
174
LindgrenJ.NilssonD.-E.SjövallP.JarenmarkM.ItoS.WakamatsuK.et al. (2019). Fossil insect eyes shed light on trilobite optics and the arthropod pigment screen. Nature573, 122–125. doi: 10.1038/s41586-019-1473-z
175
LindgrenJ.SjövallP.ThielV.ZhengW.ItoS.WakamatsuK.et al. (2018). Soft-tissue evidence for homeothermy and crypsis in a Jurassic ichthyosaur. Nature564, 359–365. doi: 10.1038/s41586-018-0775-x
176
LittleC. T. S.GaleA.WilliamsM.HammerØ.FernandezV. (2023). Bivalve-barnacle pseudoplanktonic colonisation of wood from the Toarcian, lower Jurassic, strawberry Bank Lagerstätte, Somerset, UK. Acta Palaeontol. Pol.68, 133–142. doi: 10.4202/app.01018.2022
177
LiuD.FanQ.PapineauD.YuN.ChuY.WangH.et al. (2020). Precipitation of protodolomite facilitated by sulfate-reducing bacteria: the role of capsule extracellular polymeric substances. Chem. Geol.533:119415. doi: 10.1016/j.chemgeo.2019.119415
178
LiuR.HuangS.ZhangX.SongY.HeG.WangZ.et al. (2021). Bio-mineralisation, characterization, and stability of calcium carbonate containing organic matter. RCS Adv.11, 14415–14425. doi: 10.1039/D1RA00615K
179
LiuA.-Q.TangD.-J.ShiX.-Y.ZhouL.-M.ZhouX.-Q.ShangM.-H.et al. (2019). Growth mechanisms and environmental implications of carbonate concretions from the ~ 1.4 Ga Xiamaling formation, North China. J. Palaeogeogr.8:20. doi: 10.1186/s42501-019-0036-4
180
LiuA.TangD.ShiX.ZhouX.ZhouL.ShangM.et al. (2020). Mesoproterozoic oxygenated deep seawater recorded by early diagenetic carbonate concretions from the member IV of the Xiamaling formation, North China. Precambrian Res.341:105667. doi: 10.1016/j.precamres.2020.105667
181
LiuX.ZarfelG.van der WeijdenR.LoiskandlW.BitschnauB.DinklaI. J. T.et al. (2021). Density-dependent microbial calcium carbonate precipitation by drinking water bacteria via amino acid metabolism and biosorption. Water Res.202:117444. doi: 10.1016/j.watres.2021.117444
182
LongJ. A.TrinajsticK. (2010). The late Devonian Gogo formation Lägerstatte of Western Australia: exceptional early vertebrate preservation and diversity. Annu. Rev. Earth Pl. Sc.38, 255–279. doi: 10.1146/annurev-earth-040809-152416
183
LongJ. A.TrinajsticK.JohansonZ. (2009). Devonian arthrodire embryos and the origin of internal fertilization in vertebrates. Nature457, 1124–1127. doi: 10.1038/nature07732
184
LongJ. A.TrinajsticK.YoungG. C.SendenT. (2008). Live birth in the Devonian period. Nature453, 650–652. doi: 10.1038/nature06966
185
LoydS. J. (2017). Preservation of overmature, ancient, sedimentary organic matter in carbonate concretions during outcrop weathering. Geobiology15, 146–157. doi: 10.1111/gbi.12194
186
MabesooneJ. M.TinocoI. M. (1973). Palaeoecology of the Aptian Santana formation (northeastern Brazil). Palaeogeogr. Palaeocl.14, 97–118. doi: 10.1016/0031-0182(73)90006-0
187
MackenzieA. S.BrassellS. C.EglintonG.MaxwellJ. R. (1982). Chemical fossils: the geological fate of steroids. Science217, 491–504. doi: 10.1126/science.217.4559.491
188
MaedaH.TanakaG.ShimobayashiN.OhnoT.MatsuokaH. (2011). Cambrian Orsten Lagerstätte from the alum shale formation: fecal pellets as a probable source of phosphorus preservation. PALAIOS26, 225–231. doi: 10.2110/palo.2010.p10-042r
189
MählerB.JanssenK.MennekenM.TahounM.LagosM.BierbaumG.et al. (2020). Calcite precipitation forms crystal clusters and muscle mineralization during the decomposition of Cambarellus diminutus (Decapoda: Cambaridae) in freshwater. Palaeontol. Electron.23:a55. doi: 10.26879/992
190
MaischH. M.BeckerM. A. (2022). Teredolites driftwood from the Arkadelphia formation–midway group contact (K–Pg), Malvern, Arkansas, USA. Ichnos29, 117–136. doi: 10.1080/10420940.2023.2182298
191
MaiseyJ. G. (1991). Santana fossils: An illustrated atlas. New Jersey: T.F.H. Publications.
192
MaldanisL.CarvalhoM.AlmeidaM. R.FreitasF. I.de AndradeJ. A. F. G.NunesR. S.et al. (2016). Heart fossilization is possible and informs the evolution of cardiac outflow tract in vertebrates. elife5:e14698. doi: 10.7554/eLife.14698
193
MarshallJ. D.PirrieD. (2013). Carbonate concretions—explained. Geol. Today29, 53–62. doi: 10.1111/gto.12002
194
MartillD. M. (1988). Preservation of fish in the cretaceous Santana formation of Brazil. Palaeontology31, 1–18.
195
MartillD. M. (1989). The medusa effect: instantaneous fossilization. Geol. Today5, 201–205. doi: 10.1111/j.1365-2451.1989.tb00671.x
196
MartillD. M. (1990). Macromolecular resolution of fossilized muscle tissue from an elopomorph fish. Nature346, 171–172. doi: 10.1038/346171a0
197
MartillD. M. (1993). Fossils of the Santana and Crato formations, Brazil. London: The Palaeontological Association.
198
MartillD. M. (2007). The age of the cretaceous Santana formation fossil Konservat Lagerstätte of north-East Brazil: a historical review and an appraisal of the biochronostratigraphic utility of its palaeobiota. Cretac. Res.28, 895–920. doi: 10.1016/j.cretres.2007.01.002
199
MartillD. M.BritoP. M. (2017). “The Santana formation” in Terrestrial conservation Lagerstatten: Windows into the evolution of life on land. eds. FraserN. C.SuesH. D. (Dunedin: Dunedin Academic Press), 215–256.
200
MartinD.BriggsD. E. G.ParkesR. J. (2003). Experimental mineralization of invertebrate eggs and the preservation of Neoproterozoic embryos. Geology31, 39–42. doi: 10.1130/0091-7613(2003)031<0039:EMOIEA>2.0.CO;2
201
MartinD.BriggsD. E. G.ParkesR. J. (2005). Decay and mineralization of invertebrate eggs. PALAIOS20, 562–572. doi: 10.2110/palo.2004.p04-67
202
MatthewsD. E.HayesJ. M. (1978). Isotope-ratio-monitoring gas chromatography-mass spectrometry. Anal. Chem.50, 1465–1473. doi: 10.1021/ac50033a022
203
Matzke-KaraszR.NeilJ. V.SmithR. J.GodthelpH.ArcherM.HandS. J. (2013). Ostracods (Crustacea) with soft part preservation from Miocene cave deposits of the Riversleigh world heritage area, NW Queensland, Australia. J. Syst. Palaeontol.11, 789–819. doi: 10.1080/14772019.2012.760007
204
MaynardJ. B. (1982). Extension of Berner's "new geochemical classification of sedimentary environments" to ancient sediments. J. Sediment. Res.52, 1325–1331. doi: 10.1306/212F812F-2B24-11D7-8648000102C1865D
205
MaysC.BevittJ. J.StilwellJ. D. (2017). Pushing the limits of neutron tomography in palaeontology: three-dimensional modeling of in situ resin within fossil plants. Palaeontol. Electron.20:20.23.57A. doi: 10.26879/808
206
McCoyV. E. (2014). Concretions as agents of soft-tissue preservation: a review. Paleontol. Soc. Papers20, 147–162. doi: 10.1017/S1089332600002849
207
McCoyV. E.SaupeE. E.LamsdellJ. C.TarhanL. G.McMahonS.LidgardS.et al. (2016). The ‘Tully monster’ is a vertebrate. Nature532, 496–499. doi: 10.1038/nature16992
208
McCoyV. E.WiemannJ.LamsdellJ. C.WhalenC. D.LidgardS.MayerP.et al. (2020). Chemical signatures of soft tissues distinguish between vertebrates and invertebrates from the carboniferous Mazon Creek Lagerstätte of Illinois. Geobiology18, 560–565. doi: 10.1111/gbi.12397
209
McCoyV. E.YoungR. T.BriggsD. E. G. (2015a). Factors controlling exceptional preservation in concretions. PALAIOS30, 272–280. doi: 10.2110/palo.2014.081
210
McCoyV. E.YoungR. T.BriggsD. E. G. (2015b). Sediment permeability and the preservation of soft-tissues in concretions: an experimental study. PALAIOS30, 608–612. doi: 10.2110/palo.2015.002
211
McElhinneyJ. M. W. R.CatacutanM. K.MawartA.HasanA.DiasJ. (2022). Interfacing machine learning and microbial omics: a promising means to address environmental challenges. Front. Microbiol.13:851450. doi: 10.3389/fmicb.2022.851450
212
McMullanD. (1995). Scanning electron microscopy 1928–1965. Scanning17, 175–185. doi: 10.1002/sca.4950170309
213
McNamaraM. E.OrrP. J.KearnsS. L.AlcaláL.AnadónP.Peñalver MolláE. (2009). Soft-tissue preservation in Miocene frogs from Libros, Spain: insights into the genesis of decay microenvironments. PALAIOS24, 104–117. doi: 10.2110/palo.2008.p08-017r
214
MeiM.BissadaK. K.MalloyT. B.DarnellL. M.SzymcykE. B. (2018). Improved method for simultaneous determination of saturated and aromatic biomarkers, organosulfur compounds and diamondoids in crude oils by GC–MS/MS. Org. Geochem.116, 35–50. doi: 10.1016/j.orggeochem.2017.09.010
215
MelendezI.GriceK.SchwarkL. (2013a). Exceptional preservation of Palaeozoic steroids in a diagenetic continuum. Sci. Rep.3:2768. doi: 10.1038/srep02768
216
MelendezI.GriceK.TrinajsticK.LadjavardiM.GreenwoodP.ThompsonK. (2013b). Biomarkers reveal the role of photic zone euxinia in exceptional fossil preservation: an organic geochemical perspective. Geology41, 123–126. doi: 10.1130/g33492.1
217
MeredithW.SnapeC. E.LoveG. D. (2015). “Development and use of catalytic hydropyrolysis (HyPy) as an analytical tool for organic geochemical applications” in Principles and practice of analytical techniques in geosciences. ed. GriceK. (Oxford: Royal Society of Chemistry), 171–208.
218
MojarroA.CuiX.ZhangX.JostA. B.BergmannK. D.VintherJ.et al. (2022). Comparative soft-tissue preservation in Holocene-age capelin concretions. Geobiology20, 377–398. doi: 10.1111/gbi.12480
219
MozleyP. S.BurnsS. J. (1993). Oxygen and carbon isotopic composition of marine carbonate concretions; an overview. J. Sediment. Res.63, 73–83. doi: 10.1306/d4267a91-2b26-11d7-8648000102c1865d
220
MuramiyaY.YoshidaH.MinamiM.MikamiT.KobayashiT.SekiuchiK.et al. (2022). Glendonite concretion formation due to dead organism decomposition. Sediment. Geol.429:106075. doi: 10.1016/j.sedgeo.2021.106075
221
MuruganR.SundararaghavanA.DhamiN. K.MukherjeeA.SuraishkumarG. K. (2022). Importance of carbon to nitrogen ratio in microbial cement production: insights through experiments and genome-scale metabolic modelling. Biochem. Eng. J.186:108573. doi: 10.1016/j.bej.2022.108573
222
MuruganR.SuraishkumarG. K.MukherjeeA.DhamiN. K. (2021). Insights into the influence of cell concentration in design and development of microbially induced calcium carbonate precipitation (MICP) process. PLoS One16:e0254536. doi: 10.1371/journal.pone.0254536
223
NaeherS.CuiX.SummonsR. E. (2022). Biomarkers: molecular tools to study life, environment, and climate. Elements18, 79–85. doi: 10.2138/gselements.18.2.79
224
NaimarkE. B.BoevaN. M.KalininaM. A.ZaytsevaL. V. (2018). Complementary transformations of buried organic residues and the ambient sediment: results of long-term taphonomic experiments. Paleontol. J.52, 109–122. doi: 10.1134/S0031030118020053
225
NaimarkE.KalininaM.ShokurovA.BoevaN.MarkovA.ZaytsevaL. (2016). Decaying in different clays: implications for soft-tissue preservation. Palaeontology59, 583–595. doi: 10.1111/pala.12246
226
NicholsP. D.Mancuso NicholsC. A. (2008). Microbial signature lipid profiling and exopolysaccharides: experiences initiated with Professor David C White and transported to Tasmania, Australia. J. Microbiol. Meth.74, 33–46. doi: 10.1016/j.mimet.2007.06.017
227
NipM.TegelaarE. W.BrinkhuisH.De LeeuwJ. W.SchenckP. A.HollowayP. J. (1986). Analysis of modern and fossil plant cuticles by curie point Py-GC and curie point Py-GC-MS: recognition of a new, highly aliphatic and resistant biopolymer. Org. Geochem.10, 769–778. doi: 10.1016/S0146-6380(86)80014-6
228
NolanM. R.WalkerS. E.SellyT.SchiffbauerJ. (2023). Is the middle Cambrian Brooksella a hexactinellid sponge, trace fossil or pseudofossil?PeerJ11:e14796. doi: 10.7717/peerj.14796
229
NorellM. A.WiemannJ.FabbriM.YuC.MarsicanoC. A.Moore-NallA.et al. (2020). The first dinosaur egg was soft. Nature583, 406–410. doi: 10.1038/s41586-020-2412-8
230
O'BrienN. R.MeyerH. W.ReillyK.RossA. M.MaguireS. (2002). Microbial taphonomic processes in the fossilization of insects and plants in the late Eocene Florissant formation, Colorado. Rocky Mt. Geol.37, 1–11. doi: 10.2113/gsrocky.37.1.1
231
OgiharaS. (1999). Geochemical characteristics of phosphorite and carbonate nodules from the Miocene Funakawa formation, western margin of the Yokote Basin, Northeast Japan. Sediment. Geol.125, 69–82. doi: 10.1016/S0037-0738(98)00136-5
232
OnstottT. C.EhlmannB. L.SapersH.ColemanM.IvarssonM.MarlowJ. J.et al. (2019). Paleo-rock-hosted life on earth and the search on Mars: a review and strategy for exploration. Astrobiology19, 1230–1262. doi: 10.1089/ast.2018.1960
233
OnumaK.OyaneA.KokuboT.TrebouxG.KanzakiN.ItoA. (2000). Nucleation of calcium phosphate on 11-mercaptoundecanoic acid self-assembled monolayer in a pseudophysiological solution. J. Phys. Chem. B104, 11950–11956. doi: 10.1021/jp002015p
234
ParryL. A.SmithwickF.NordénK. K.SaittaE. T.Lozano-FernandezJ.TannerA. R.et al. (2018). Soft-bodied fossils are not simply rotten carcasses – toward a holistic understanding of exceptional fossil preservation. BioEssays40:1700167. doi: 10.1002/bies.201700167
235
PearsonM. J.NelsonC. S. (2005). Organic geochemistry and stable isotope composition of New Zealand carbonate concretions and calcite fracture fills. New Zeal. J. Geol. Geop.48, 395–414. doi: 10.1080/00288306.2005.9515122
236
PelletierM. J. (1999). Analytical applications of Raman spectroscopy. Oxford: Wiley-Blackwell.
237
PercivalS. L.MalicS.CruzH.WilliamsD. W. (2011). “Introduction to biofilms” in Biofilms and veterinary medicine. eds. PercivalS.KnottenbeltD.CochraneC. (Berlin, Heidelberg: Springer Berlin Heidelberg), 41–68.
238
PetersK. E.MoldowanJ. M. (1992). The biomarker guide. New Jersey: Prentice-Hall.
239
PetersonJ. E.LenczewskiM. E.SchererR. P. (2010). Influence of microbial biofilms on the preservation of primary soft tissue in fossil and extant archosaurs. PLoS One5:e13334. doi: 10.1371/journal.pone.0013334
240
PetrovichR. (2001). Mechanisms of fossilization of the soft-bodied and lightly armored faunas of the burgess shale and of some other classical localities. Am. J. Sci.301, 683–726. doi: 10.2475/ajs.301.8.683
241
PletC.GriceK.PagèsA.RuebsamW.CoolenM. J. L.SchwarkL. (2016). Microbially-mediated fossil-bearing carbonate concretions and their significance for palaeoenvironmental reconstructions: a multi-proxy organic and inorganic geochemical appraisal. Chem. Geol.426, 95–108. doi: 10.1016/j.chemgeo.2016.01.026
242
PletC.GriceK.PagèsA.VerrallM.CoolenM. J. L.RuebsamW.et al. (2017). Palaeobiology of red and white blood cell-like structures, collagen and cholesterol in an ichthyosaur bone. Sci. Rep.7:13776. doi: 10.1038/s41598-017-13873-4
243
PlotnickR. E.YoungG. A.HagadornJ. W. (2023). An abundant sea anemone from the carboniferous Mazon Creek Lagerstӓtte, USA. Pap. Palaeontol.9:e1479. doi: 10.1002/spp2.1479
244
PugliesiR.PereiraM. A. S.AndradeM. L. G.BassoJ. M. L.VoltaniC. G.GonzalesI. C. (2019). Study of the fish fossil Notelops brama from Araripe-Basin Brazil by neutron tomography. Nucl. Instrum. Meth. A919, 68–72. doi: 10.1016/j.nima.2018.12.001
245
PurnellM. A.DonoghueP. J. C.GabbottS. E.McNamaraM. E.MurdockD. J. E.SansomR. S. (2018). Experimental analysis of soft-tissue fossilization: opening the black box. Palaeontology61, 317–323. doi: 10.1111/pala.12360
246
PyeK. (1984). SEM analysis of siderite cements in intertidal marsh sediments, Norfolk, England. Mar. Geol.56, 1–12. doi: 10.1016/0025-3227(84)90002-1
247
PyeK.DicksonJ. A. D.SchiavonN.ColemanM. L.CoxM. (1990). Formation of siderite-mg-calcite-iron sulphide concretions in intertidal marsh and sandflat sediments, North Norfolk, England. Sedimentology37, 325–343. doi: 10.1111/j.1365-3091.1990.tb00962.x
248
QvarnströmM.AhlbergP. E.NiedźwiedzkiG. (2019a). Tyrannosaurid-like osteophagy by a Triassic archosaur. Sci. Rep.9:925. doi: 10.1038/s41598-018-37540-4
249
QvarnströmM.WernströmJ. V.PiechowskiR.TałandaM.AhlbergP. E.NiedźwiedzkiG. (2019b). Beetle-bearing coprolites possibly reveal the diet of a late Triassic dinosauriform. Roy. Soc. Open Sci.6:181042. doi: 10.1098/rsos.181042
250
RaffR. A.AndrewsM. E.PearsonR. L.TurnerF. R.SaurS. T.ThomasD. C.et al. (2014). Microbial ecology and biofilms in the taphonomy of soft tissues. PALAIOS29, 560–569. doi: 10.2110/palo.2014.043
251
RaffE. C.AndrewsM. E.TurnerF. R.TohE.NelsonD. E.RaffR. A. (2013). Contingent interactions among biofilm-forming bacteria determine preservation or decay in the first steps toward fossilization of marine embryos. Evol. Dev.15, 243–256. doi: 10.1111/ede.12028
252
RaffR. A.RaffE. C. (2014). The role of biology in the fossilization of embryos and other soft-bodied organisms: microbial biofilms and Lagerstätten. Paleontol. Soc. Papers20, 83–100. doi: 10.1017/S1089332600002813
253
RaffE. C.SchollaertK. L.NelsonD. E.DonoghueP. C. J.ThomasC.-W.TurnerF. R.et al. (2008). Embryo fossilization is a biological process mediated by microbial biofilms. P. Natl. Acad. Sci. USA105, 19360–19365. doi: 10.1073/pnas.0810106105
254
RahmanF. U.AndreeK. B.Salas-MassóN.Fernandez-TejedorM.SanjuanA.FiguerasM. J.et al. (2020). Improved culture enrichment broth for isolation of Arcobacter-like species from the marine environment. Sci. Rep.10:14547. doi: 10.1038/s41598-020-71442-8
255
RaiswellR. (1971). The growth of Cambrian and Liassic concretions. Sedimentology17, 147–171. doi: 10.1111/j.1365-3091.1971.tb01773.x
256
RaiswellR. (1976). The microbiological formation of carbonate concretions in the upper Lias of NE England. Chem. Geol.18, 227–244. doi: 10.1016/0009-2541(76)90006-1
257
RaiswellR.FisherQ. J. (2000). Mudrock-hosted carbonate concretions: a review of growth mechanisms and their influence on chemical and isotopic composition. J. Geol. Soc.157, 239–251. doi: 10.1144/jgs.157.1.239
258
RamachandranA. L.PolatP.MukherjeeA.DhamiN. K. (2020). Understanding and creating biocementing beachrocks via biostimulation of indigenous microbial communities. Appl. Microbiol. Biot.104, 3655–3673. doi: 10.1007/s00253-020-10474-6
259
ReichhardtC.ParsekM. R. (2019). Confocal laser scanning microscopy for analysis of Pseudomonas aeruginosa biofilm architecture and matrix localization. Front. Microbiol.10:677. doi: 10.3389/fmicb.2019.00677
260
ReimersC. E.KastnerM.GarissonR. E. (1990). “The role of bacterial mats in phosphate mineralization with particular reference to the Monterey formation” in Phosphate deposits of the world Vol. 3: Neogene to modern Phosphorites. eds. BurnettW. C.RiggsS. R. (Cambridge: Cambridge University Press)
261
ReinhardtM.GoetzW.DudaJ. P.HeimC.ReitnerJ.ThielV. (2019). Organic signatures in Pleistocene cherts from Lake Magadi (Kenya) – implications for early earth hydrothermal deposits. Biogeosciences16, 2443–2465. doi: 10.5194/bg-16-2443-2019
262
ReitnerJ. (2004). “Organomineralization” in Origins: Genesis, evolution and diversity of life. ed. SeckbachJ. (Dordrecht: Springer Netherlands), 195–212.
263
RelucentiM.FamiliariG.DonfrancescoO.TaurinoM.LiX.ChenR.et al. (2021). Microscopy methods for biofilm imaging: focus on SEM and VP-SEM pros and cons. Biology10:51. doi: 10.3390/biology10010051
264
RileyP. A. (1997). Molecules in focus: melanin. Int. J. Biochem. Cell. B.29, 1235–1239. doi: 10.1016/S1357-2725(97)00013-7
265
RobertsA. J.EngelschiønV. S.HurumJ. H. (2022). First three-dimensional skull of the middle Triassic mixosaurid ichthyosaur Phalarodon fraasi from Svalbard, Norway. Acta Palaeontol. Pol.67, 51–62. doi: 10.4202/app.00915.2021
266
RodriguesC. J. C.de CarvalhoC. C. C. R. (2022). Cultivating marine bacteria under laboratory conditions: overcoming the “unculturable” dogma. Front. Bioeng. Biotechnol.10:964589. doi: 10.3389/fbioe.2022.964589
267
Rodriguez-NavarroC.JroundiF.SchiroM.Ruiz-AgudoE.González-MuñozM. T. (2012). Influence of substrate mineralogy on bacterial mineralization of calcium carbonate: implications for stone conservation. Appl. Environ. Microbiol.78, 4017–4029. doi: 10.1128/AEM.07044-11
268
RogovM.ErshovaV.GainaC.VereshchaginO.VasilevaK.MikhailovaK.et al. (2023). Glendonites throughout the Phanerozoic. Earth-Sci. Rev241:104430. doi: 10.1016/j.earscirev.2023.104430
269
RothwellR. G.HoogakkerB.ThomsonJ.CroudaceI. W.FrenzM. (2006). “Turbidite emplacement on the southern Balearic abyssal plain (western Mediterranean Sea) during marine isotope stages 1–3: an application of ITRAX XRF scanning of sediment cores to lithostratigraphic analysis” in New techniques in sediment Core analysis. ed. RothwellR. G. (London: Geological Society of London), 79–98.
270
RoweA. J.KrutaI.LandmanN. H.VillierL.FernandezV.RougetI. (2022). Exceptional soft-tissue preservation of Jurassic Vampyronassa rhodanica provides new insights on the evolution and palaeoecology of vampyroteuthids. Sci. Rep.12:8292. doi: 10.1038/s41598-022-12269-3
271
SagemannJ.BaleS. J.BriggsD. E. G.ParkesR. J. (1999). Controls on the formation of authigenic minerals in association with decaying organic matter: an experimental approach. Geochim. Cosmochim. Ac.63, 1083–1095. doi: 10.1016/S0016-7037(99)00087-3
272
SalehF.VaucherR.AntcliffeJ. B.DaleyA. C.El HaririK.KouraissK.et al. (2021). Insights into soft-part preservation from the early Ordovician Fezouata biota. Earth-Sci. Rev.213:103464. doi: 10.1016/j.earscirev.2020.103464
273
SanchezS.AhlbergP. E.TrinajsticK. M.MironeA.TafforeauP. (2012). Three-dimensional synchrotron virtual paleohistology: a new insight into the world of fossil bone microstructures. Microsc. Microanal.18, 1095–1105. doi: 10.1017/S1431927612001079
274
SanderP. M. (2021). "Ichthyosauria," in Vertebrate skeletal histology and Paleohistology, eds. BuffrénilV.deRicqlèsA. J.deZylberbergL.PadianK. (Boca Raton: CRC Press), 458–466.
275
SanderP. M.WintrichT. (2021). "Sauropterygia: histology of plesiosauria," in Vertebrate skeletal histology and Paleohistology, eds. BuffrénilV.deRicqlèsA. J.deZylberbergL.PadianK. (Boca Raton: CRC Press), 444–457.
276
SandersonM. J.SmithI.ParkerI.BootmanM. D. (2014). Fluorescence microscopy. Cold Spring Harbor Protoc:pdb.top071795. doi: 10.1101/pdb.top071795
277
ScarlettA. G.Despaigne-DiazA. I.WildeS. A.GriceK. (2019). An examination by GC×GC-TOFMS of organic molecules present in highly degraded oils emerging from Caribbean terrestrial seeps of cretaceous age. Geosci. Front.10, 5–15. doi: 10.1016/j.gsf.2018.03.011
278
SchaefferP.AdamP.WehrungP.AlbrechtP. (1997). Novel aromatic carotenoid derivatives from sulfur photosynthetic bacteria in sediments. Tetrahedron Lett.38, 8413–8416. doi: 10.1016/S0040-4039(97)10235-0
279
SchellerE. L.SwindleC.GrotzingerJ.BarnhartH.BhattacharjeeS.EhlmannB. L.et al. (2021). Formation of magnesium carbonates on earth and implications for Mars. J. Geophys. Res.-Planet.126:e2021JE006828. doi: 10.1029/2021je006828
280
SchopfJ. W.KudryavtsevA. B. (2009). Confocal laser scanning microscopy and Raman imagery of ancient microscopic fossils. Precambrian Res.173, 39–49. doi: 10.1016/j.precamres.2009.02.007
281
SchopfJ. W.KudryavtsevA. B.SergeevV. N. (2010). Confocal laser scanning microscopy and Raman imagery of the late Neoproterozoic Chichkan microbiota of South Kazakhstan. J. Paleontol.84, 402–416. doi: 10.1666/09-134.1
282
SchoutenS.Klein BretelerW. C. M.BlokkerP.SchogtN.RijpstraW. I. C.GriceK.et al. (1998). Biosynthetic effects on the stable carbon isotopic compositions of algal lipids: implications for deciphering the carbon isotopic biomarker record. Geochim. Cosmochim. Ac.62, 1397–1406. doi: 10.1016/S0016-7037(98)00076-3
283
SchoutenS.van DrielG. B.Sinninghe DamstéJ. S.de LeeuwJ. W. (1993). Natural sulphurization of ketones and aldehydes: a key reaction in the formation of organic Sulphur compounds. Geochim. Cosmochim. Ac.57, 5111–5116. doi: 10.1016/0016-7037(93)90613-2
284
SchuffertJ. D.JahnkeR. A.KastnerM.LeatherJ.SturzA.WingM. R. (1994). Rates of formation of modern phosphorite off western Mexico. Geochim. Cosmochim. Ac.58, 5001–5010. doi: 10.1016/0016-7037(94)90227-5
285
SchultzeH.-P. (1989). Three-dimensional muscle preservation in Jurassic fishes of Chile. Rev. Geol. Chile16, 183–215.
286
SchulzH. N.SchulzH. D. (2005). Large sulfur bacteria and the formation of phosphorite. Science307, 416–418. doi: 10.1126/science.1103096
287
SchwarkL. (2013). Exceptional preservation of microbial lipids in Paleozoic to Mesoproterozoic sediments. Geology41, 287–288. doi: 10.1130/focus022013.1
288
SchwarkL.PüttmannW. (1990). Aromatic hydrocarbon composition of the Permian Kupferschiefer in the lower Rhine Basin, NW Germany. Org. Geochem.16, 749–761. doi: 10.1016/0146-6380(90)90114-f
289
SchweitzerM. H.ZhengW.MoyerA. E.SjövallP.LindgrenJ. (2018). Preservation potential of keratin in deep time. PLoS One13:e0206569. doi: 10.1371/journal.pone.0206569
290
SenterP. J. (2022). Cells and soft tissues in fossil bone: a review of preservation mechanisms, with corrections of misconceptions. Palaeontol. Electron.25:a34. doi: 10.26879/1248
291
SessionsA. L. (2006). Isotope-ratio detection for gas chromatography. J. Sep. Sci.29, 1946–1961. doi: 10.1002/jssc.200600002
292
SessionsA. L. (2016). Factors controlling the deuterium contents of sedimentary hydrocarbons. Org. Geochem.96, 43–64. doi: 10.1016/j.orggeochem.2016.02.012
293
ShafferJ. P.NothiasL.-F.ThompsonL. R.SandersJ. G.SalidoR. A.CouvillionS. P.et al. (2022). Standardized multi-omics of Earth’s microbiomes reveals microbial and metabolite diversity. Nat. Microbiol.7, 2128–2150. doi: 10.1038/s41564-022-01266-x
294
SiljeströmS.HodeT.LausmaaJ.SjövallP.ToporskiJ.ThielV. (2009). Detection of organic biomarkers in crude oils using ToF-SIMS. Org. Geochem.40, 135–143. doi: 10.1016/j.orggeochem.2008.08.010
295
SiljeströmS.LausmaaJ.SjövallP.BromanC.ThielV.HodeT. (2010). Analysis of hopanes and steranes in single oil-bearing fluid inclusions using time-of-flight secondary ion mass spectrometry (ToF-SIMS). Geobiology8, 37–44. doi: 10.1111/j.1472-4669.2009.00223.x
296
SiljeströmS.NeubeckA.SteeleA. (2022). Detection of porphyrins in vertebrate fossils from the Messel and implications for organic preservation in the fossil record. PLoS One17:e0269568. doi: 10.1371/journal.pone.0269568
297
SiljeströmS.ParenteauM. N.JahnkeL. L.CadyS. L. (2017). A comparative ToF-SIMS and GC–MS analysis of phototrophic communities collected from an alkaline silica-depositing hot spring. Org. Geochem.109, 14–30. doi: 10.1016/j.orggeochem.2017.03.009
298
SiljeströmS.VolkH.GeorgeS. C.LausmaaJ.SjövallP.DutkiewiczA.et al. (2013). Analysis of single oil-bearing fluid inclusions in mid-Proterozoic sandstones (roper group, Australia). Geochim. Cosmochim. Ac.122, 448–463. doi: 10.1016/j.gca.2013.08.010
299
Sinninghe DamstéJ. S.de LeeuwJ. W. (1990). Analysis, structure and geochemical significance of organically-bound Sulphur in the geosphere: state of the art and future research. Org. Geochem.16, 1077–1101. doi: 10.1016/0146-6380(90)90145-P
300
SiveterD. J.BriggsD. E. G.SiveterD. J.SuttonM. D. (2020). The Herefordshire Lagerstätte: fleshing out Silurian marine life. J. Geol. Soc.177, 1–13. doi: 10.1144/jgs2019-110
301
SkoogD. A.HollerF. J.CrouchS. R. (2018). Principles of instrumental analysis7th Edn. Boston: Cengage Learning.
302
SmithR. J. (2000). Morphology and ontogeny of Cretaceous ostracods with preserved appendages from Brazil. Palaeontology43, 63–98. doi: 10.1111/1475-4983.00119
303
SondheimerE.DenceW. A.MattickL. R.SilvermanS. R. (1966). Composition of combustible concretions of the alewife, Alosa pseudoharengus. Science152, 221–223. doi: 10.1126/science.152.3719.221
304
SpicerR. (1991). “Plant taphonomic processes” in Taphonomy: Releasing the data locked in the fossil record. eds. AllisonP. A.BriggsD. E. G. (New York: Plenum Press), 71–113.
305
SteeleA.FriesM. D.PasterisJ. D. (2020). Geoscience meets biology: Raman spectroscopy in geobiology and biomineralization. Elements16, 111–116. doi: 10.2138/gselements.16.2.111
306
SteeleA.ToporskiJ. K. W.AvciR.GuidryS.McKayD. S. (2001). Time of flight secondary ion mass spectrometry (ToFSIMS) of a number of hopanoids. Org. Geochem.32, 905–911. doi: 10.1016/S0146-6380(01)00048-1
307
StewartP. S.FranklinM. J. (2008). Physiological heterogeneity in biofilms. Nat. Rev. Microbiol.6, 199–210. doi: 10.1038/nrmicro1838
308
StolarskiJ.GorzelakP.MazurM.MarrocchiY.MeibomA. (2009). Nanostructural and geochemical features of the Jurassic isocrinid columnal ossicles. Acta Palaeontol. Pol.54, 69–75. doi: 10.4202/app.2009.0108
309
SummonsR. E.PowellT. G. (1987). Identification of aryl isoprenoids in source rocks and crude oils: biological markers for the green Sulphur bacteria. Geochim. Cosmochim. Acta51, 557–566. doi: 10.1016/0016-7037(87)90069-X
310
SunW.YinZ.CunninghamJ. A.LiuP.ZhuM.DonoghueP. C. J. (2020). Nucleus preservation in early Ediacaran Weng'an embryo-like fossils, experimental taphonomy of nuclei and implications for reading the eukaryote fossil record. Interface Focus10:20200015. doi: 10.1098/rsfs.2020.0015
311
SuttonM. D.RahmanI. A.GarwoodR. J. (2014). Techniques for virtual Palaeontology. Chichester, UK: John Wiley & Sons.
312
TafforeauP.BoistelR.BollerE.BravinA.BrunetM.ChaimaneeY.et al. (2006). Applications of X-ray synchrotron microtomography for non-destructive 3D studies of paleontological specimens. Appl. Phys. A Mater. Sci. Process.83, 195–202. doi: 10.1007/s00339-006-3507-2
313
ThielV.BlumenbergM.KielS.LeefmannT.LiebenauK.LindgrenJ.et al. (2014). Occurrence and fate of fatty acyl biomarkers in an ancient whale bone (Oligocene, El Cien formation, Mexico). Org. Geochem.68, 71–81. doi: 10.1016/j.orggeochem.2013.12.006
314
ThielV.SjövallP. (2011). Using time-of-flight secondary ion mass spectrometry to study biomarkers. Annu. Rev. Earth Pl. Sc.39, 125–156. doi: 10.1146/annurev-earth-040610-133525
315
ThompsonJ. B.Schultze-LamS.BeveridgeT. J.Des MaraisD. J. (1997). Whiting events: biogenic origin due to the photosynthetic activity of cyanobacterial picoplankton. Limnol. Oceanogr.42, 133–141. doi: 10.4319/lo.1997.42.1.0133
316
ThomsonJ.CroudaceI. W.RothwellR. G. (2006). “A geochemical application of the ITRAX scanner to a sediment core containing eastern Mediterranean sapropel units” in New techniques in sediment Core analysis. ed. RothwellR. G. (London: Geological Society of London), 65–78.
317
TissotB. P.WelteD. H. (1984). Petroleum formation and Occurence. Berlin: Springer-Verlag.
318
ToporskiJ. K. W.SteeleA.WestallF.AvciR.MartillD. M.McKayD. S. (2002). Morphologic and spectral investigation of exceptionally well-preserved bacterial biofilms from the Oligocene Enspel formation, Germany. Geochim. Cosmochim. Acta66, 1773–1791. doi: 10.1016/S0016-7037(01)00870-5
319
TouboulD.KollmerF.NiehuisE.BrunelleA.LaprévoteO. (2005). Improvement of biological time-of-flight-secondary ion mass spectrometry imaging with a bismuth cluster ion source. J. Am. Soc. Mass Spectr.16, 1608–1618. doi: 10.1016/j.jasms.2005.06.005
320
TrinajsticK.BriggsD. E. G.LongJ. A. (2022a). The Gogo formation Lagerstätte: a view of Australia's first great barrier reef. J. Geol. Soc.179:jgs2021-2105. doi: 10.1144/jgs2021-105
321
TrinajsticK.LongJ. A.SanchezS.BoisvertC. A.SnittingD.TafforeauP.et al. (2022b). Exceptional preservation of organs in Devonian placoderms from the Gogo lagerstätte. Science377, 1311–1314. doi: 10.1126/science.abf3289
322
TrinajsticK.MarshallC.LongJ.BifieldK. (2007). Exceptional preservation of nerve and muscle tissues in late Devonian placoderm fish and their evolutionary implications. Biol. Lett.3, 197–200. doi: 10.1098/rsbl.2006.0604
323
TrinajsticK.SanchezS.DupretV.TafforeauP.LongJ.YoungG.et al. (2013). Fossil musculature of the most primitive jawed vertebrates. Science341, 160–164. doi: 10.1126/science.1237275
324
TrippM.WiemannJ.BrocksJ.MayerP.SchwarkL.GriceK. (2022). Fossil biomarkers and biosignatures preserved in coprolites reveal carnivorous diets in the carboniferous Mazon Creek ecosystem. Biology11:1289. doi: 10.3390/biology11091289
325
TurnbullM. J. M.WhitehouseM. J.MoorbathS. (1996). New isotopic age determinations for the Torridonian, NW Scotland. J. Geol. Soc.153, 955–964. doi: 10.1144/gsjgs.153.6.0955
326
van RijnJ.TalY.SchreierH. J. (2006). Denitrification in recirculating systems: theory and applications. Aquac. Eng.34, 364–376. doi: 10.1016/j.aquaeng.2005.04.004
327
Van RoyP.BriggsD. E. G.GainesR. R. (2015). The Fezouata fossils of Morocco; an extraordinary record of marine life in the early Ordovician. J. Geol. Soc.172, 541–549. doi: 10.1144/jgs2015-017
328
VarejãoF. G.WarrenL. V.SimõesM. G.BuatoisL. A.MánganoM. G.Bahniuk RumbelspergerA. M.et al. (2021). Mixed siliciclastic–carbonate sedimentation in an evolving epicontinental sea: Aptian record of marginal marine settings in the interior basins of North-Eastern Brazil. Sedimentology68, 2125–2164. doi: 10.1111/sed.12846
329
VarejãoF. G.WarrenL. V.SimõesM. G.FürsichF. T.MatosS. A.AssineM. L. (2019). Exceptional preservation of soft tissues by microbial entombment: insights into the taphonomy of the Crato Konservat-Lagerstätte. PALAIOS34, 331–348. doi: 10.2110/palo.2019.041
330
Vernon-ParryK. D. (2000). Scanning electron microscopy: an introduction. III-Vs Rev.13, 40–44. doi: 10.1016/S0961-1290(00)80006-X
331
VincentP.AllemandR.TaylorP. D.SuanG.MaxwellE. E. (2017). New insights on the systematics, palaeoecology and palaeobiology of a plesiosaurian with soft tissue preservation from the Toarcian of Holzmaden. Germany. Sci. Nat.104:51. doi: 10.1007/s00114-017-1472-6
332
VorontsovD. D.KolesnikovV. B.VoronezhskayaE. E.PerkovskyE. E.BertoM. M.MoweryJ.et al. (2023). Beyond the limits of light: an application of super-resolution confocal microscopy (sCLSM) to investigate Eocene amber microfossils. Life13:865. doi: 10.3390/life13040865
333
WaceyD.MenonS.GreenL.GerstmannD.KongC.McLoughlinN.et al. (2012). Taphonomy of very ancient microfossils from the ∼3400Ma Strelley Pool formation and ∼1900Ma gunflint formation: new insights using a focused ion beam. Precambrian Res.220-221, 234–250. doi: 10.1016/j.precamres.2012.08.005
334
WagnerM.IvlevaN. P.HaischC.NiessnerR.HornH. (2009). Combined use of confocal laser scanning microscopy (CLSM) and Raman microscopy (RM): investigations on EPS – matrix. Water Res.43, 63–76. doi: 10.1016/j.watres.2008.10.034
335
WangX.ZhangS.WangH.CanfieldD. E.SuJ.HammarlundE. U.et al. (2017). Remarkable preservation of microfossils and biofilms in Mesoproterozoic silicified bitumen concretions from northern China. Geofluids2017:4818207. doi: 10.1155/2017/4818207
336
WarrenL. A.MauriceP. A.ParmarN.FerrisF. G. (2001). Microbially mediated calcium carbonate precipitation: implications for interpreting calcite precipitation and for solid-phase capture of inorganic contaminants. Geomicrobiol J.18, 93–115. doi: 10.1080/01490450151079833
337
WeeksL. G. (1953). Environment and mode of origin and facies relationships of carbonate concretions in shales. J. Sediment. Res.23, 162–173. doi: 10.1306/d42695f8-2b26-11d7-8648000102c1865d
338
WeeksL. G. (1957). Origin of carbonate concretions in shales, Magdalena Valley. Colombia. GSA Bull.68, 95–102. doi: 10.1130/0016-7606(1957)68[95:Ooccis]2.0.Co;2
339
WeinerS.DoveP. M. (2003). An overview of biomineralization processes and the problem of the vital effect. Rev. Mineral. Geochem.54, 1–29. doi: 10.2113/0540001
340
WhiteM. A.BellP. R.CampioneN. E.SansaloneG.BroughamT.BevittJ. J.et al. (2022). Abdominal contents reveal cretaceous crocodyliforms ate dinosaurs. Gondwana Res.106, 281–302. doi: 10.1016/j.gr.2022.01.016
341
WiemannJ.CrawfordJ. M.BriggsD. E. G. (2020). Phylogenetic and physiological signals in metazoan fossil biomolecules. Sci. Adv.6:eaba6883. doi: 10.1126/sciadv.aba6883
342
WiemannJ.FabbriM.YangT.-R.SteinK.SanderP. M.NorellM. A.et al. (2018a). Fossilization transforms vertebrate hard tissue proteins into N-heterocyclic polymers. Nat. Commun.9:4741. doi: 10.1038/s41467-018-07013-3
343
WiemannJ.YangT.-R.NorellM. A. (2018b). Dinosaur egg colour had a single evolutionary origin. Nature563, 555–558. doi: 10.1038/s41586-018-0646-5
344
WiemannJ.YangT.-R.NorellM. A. (2019). Reply to: egg pigmentation probably has an Archosaurian origin. Nature570, E46–E50. doi: 10.1038/s41586-019-1283-3
345
WilbyP. R.BriggsD. E. G.BernierP.GaillardC. (1996). Role of microbial mats in the fossilization of soft tissues. Geology24, 787–790. doi: 10.1130/0091-7613(1996)024<0787:Rommit>2.3.Co;2
346
WilcoxD. A.EfflerS. W. (1981). Formation of alewife concretions in polluted Onondaga Lake. Environ. Pollut. B.2, 203–215. doi: 10.1016/0143-148X(81)90018-5
347
WilkinsonM.DampierM. D. (1990). The rate of growth of sandstone-hosted calcite concretions. Geochim. Cosmochim. Ac.54, 3391–3399. doi: 10.1016/0016-7037(90)90293-T
348
WilmethD. T.JohnsonH. A.StampsB. W.BerelsonW. M.StevensonB. S.NunnH. S.et al. (2018). Environmental and biological influences on carbonate precipitation within hot spring microbial mats in Little Hot Creek, CA. Front. Microbiol.9:1464. doi: 10.3389/fmicb.2018.01464
349
WilsonP.ParryL. A.VintherJ.EdgecombeG. D. (2016). Unveiling biases in soft-tissue phosphatization: extensive preservation of musculature in the cretaceous (Cenomanian) polychaete Rollinschaeta myoplena (Annelida: Amphinomidae). Palaeontology59, 463–479. doi: 10.1111/pala.12237
350
WoodlandB. G.StenstromR. C. (1979). “The occurrence and origin of siderite concretions in the Francis Creek shale (Pennsylvanian) of northeastern Illinois” in Mazon Creek fossils (M.H. Nitecki: Academic Press), 69–103.
351
YangT.-R.ChenY.-H.WiemannJ.SpieringB.SanderP. M. (2018). Fossil eggshell cuticle elucidates dinosaur nesting ecology. PeerJ6:e5144. doi: 10.7717/peerj.5144
352
YangD. Y.WattK. (2005). Contamination controls when preparing archaeological remains for ancient DNA analysis. J. Archaeol. Sci.32, 331–336. doi: 10.1016/j.jas.2004.09.008
353
YoshidaH.UjiharaA.MinamiM.AsaharaY.KatsutaN.YamamotoK.et al. (2015). Early post-mortem formation of carbonate concretions around tusk-shells over week-month timescales. Sci. Rep.5:14123. doi: 10.1038/srep14123
354
YoshidaH.YamamotoK.MinamiM.KatsutaN.Sin-ichiS.MetcalfeR. (2018). Generalized conditions of spherical carbonate concretion formation around decaying organic matter in early diagenesis. Sci. Rep.8:6308. doi: 10.1038/s41598-018-24205-5
355
ZarraonaindiaI.SmithD. P.GilbertJ. A. (2013). Beyond the genome: community-level analysis of the microbial world. Biol. Philos.28, 261–282. doi: 10.1007/s10539-012-9357-8
356
ZengZ.TiceM. M. (2014). Promotion and nucleation of carbonate precipitation during microbial iron reduction. Geobiology12, 362–371. doi: 10.1111/gbi.12090
357
ZengZ.TiceM. M. (2018). Electron transfer strategies regulate carbonate mineral and micropore formation. Astrobiology18, 28–36. doi: 10.1089/ast.2016.1560
358
ZhangX.BishopP. L.KupferleM. J. (1998). Measurement of polysaccharides and proteins in biofilm extracellular polymers. Water Sci. Technol.37, 345–348. doi: 10.2166/wst.1998.0661
359
ZhangX.XiaP.WangP.YangJ.BairdD. J. (2018). Omics advances in ecotoxicology. Envir. Sci. Tech.52, 3842–3851. doi: 10.1021/acs.est.7b06494
360
ZhuT.DittrichM. (2016). Carbonate precipitation through microbial activities in natural environment, and their potential in biotechnology: a review. Front. Bioeng. Biotechnol.4:4. doi: 10.3389/fbioe.2016.00004
361
ZossR.Medina FerrerF.FloodB. E.JonesD. S.LouwD. C.BaileyJ. (2019). Microbial communities associated with phosphogenic sediments and phosphoclast-associated DNA of the Benguela upwelling system. Geobiology17, 76–90. doi: 10.1111/gbi.12318
Summary
Keywords
concretion, fossil, microbes, organic geochemistry, paleontology, biomarkers, biomolecules, biominerals
Citation
Dhami NK, Greenwood PF, Poropat SF, Tripp M, Elson A, Vijay H, Brosnan L, Holman AI, Campbell M, Hopper P, Smith L, Jian A and Grice K (2023) Microbially mediated fossil concretions and their characterization by the latest methodologies: a review. Front. Microbiol. 14:1225411. doi: 10.3389/fmicb.2023.1225411
Received
19 May 2023
Accepted
14 August 2023
Published
29 September 2023
Volume
14 - 2023
Edited by
Yizhi Sheng, China University of Geosciences, China
Reviewed by
Zhifei Zhang, Northwest University, China; Dongyi Guo, Miami University, United States
Updates
Copyright
© 2023 Dhami, Greenwood, Poropat, Tripp, Elson, Vijay, Brosnan, Holman, Campbell, Hopper, Smith, Jian and Grice.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Kliti Grice, K.Grice@curtin.edu.au
†These authors have contributed equally to this work
Disclaimer
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.