Pyrite-lined shells as indicators of inefficient bioirrigation in the Holocene–Anthropocene stratigraphic record
- 1Earth Science Institute, Slovak Academy of Sciences, Bratislava, 84005, Slovakia
- 2Department of Palaeontology, University of Vienna, Althanstrasse 14, 1090 Vienna, Austria
Correspondence: Adam Tomašových (email@example.com)
Although the depth of bioturbation can be estimated on the basis of ichnofabric, the timescale of sediment mixing (reworking) and irrigation (ventilation) by burrowers that affects carbonate preservation and biogeochemical cycles is difficult to estimate in the stratigraphic record. However, pyrite linings on the interior of shells can be a signature of slow and shallow irrigation. They indicate that shells of molluscs initially inhabiting oxic sediment pockets were immediately and permanently sequestered in reduced, iron-rich microenvironments within the mixed layer. Molluscan biomass-stimulated sulfate reduction and pyrite precipitation was confined to the location of decay under such conditions. A high abundance of pyrite-lined shells in the stratigraphic record can thus be diagnostic of limited exposure of organic tissues to O2 even when the seafloor is inhabited by abundant infauna disrupting and age-homogenizing sedimentary fabric as in the present-day northern Adriatic Sea. Here, we reconstruct this sequestration pathway characterized by slow irrigation (1) by assessing preservation and postmortem ages of pyrite-lined shells of the shallow-infaunal and hypoxia-tolerant bivalve Varicorbula gibba in sediment cores and (2) by evaluating whether an independently documented decline in the depth of mixing, driven by high frequency of seasonal hypoxia during the 20th century, affected the frequency of pyrite-lined shells in the stratigraphic record of the northern Adriatic Sea. First, at prodelta sites with a high sedimentation rate, linings of pyrite framboids form rapidly in the upper 5–10 cm as they already appear in the interiors of shells younger than 10 years and occur preferentially in well-preserved and articulated shells with periostracum. Second, increments deposited in the early 20th century contain < 20 % of shells lined with pyrite at the Po prodelta and 30 %–40 % at the Isonzo prodelta, whereas the late 20th century increments possess 50 %–80 % of shells lined with pyrite at both locations. At sites with slow sedimentation rate, the frequency of pyrite linings is low (< 10 %–20 %). Surface sediments remained well mixed by deposit and detritus feeders even in the late 20th century, thus maintaining the suboxic zone with dissolved iron. The upcore increase in the frequency of pyrite-lined shells thus indicates that the oxycline depth was reduced and bioirrigation rates declined during the 20th century. We hypothesize that the permanent preservation of pyrite linings within the shells of V. gibba in the subsurface stratigraphic record was enabled by slow recovery of infaunal communities from seasonal hypoxic events, leading to the dominance of surficial sediment modifiers with low irrigation potential. The presence of very young and well-preserved pyrite-lined valves in the uppermost zones of the mixed layer indicates that rapid obrution by episodic sediment deposition is not needed for preservation of pyrite linings when sediment irrigation is transient and background sedimentation rates are not low (here, exceeding ∼ 0.1 cm yr−1) and infaunal organisms die at their living position within the sediment. Abundance of well-preserved shells lined by pyrite exceeding ∼ 10 % per assemblage in apparently well-mixed sediments in the deep-time stratigraphic record can be an indicator of inefficient bioirrigation. Fine-grained prodelta sediments in the northern Adriatic Sea deposited since the mid-20th century, with high preservation potential of reduced microenvironments formed within a mixed layer, can represent taphonomic and early diagenetic analogues of deep-time skeletal assemblages with pyrite linings.
Slow and shallow bioturbation (including biomixing and bioirrigation; Kristensen et al., 2012; Wrede et al., 2018) can reflect oxygen depletion, toxicity, or other environmental stresses that limit ecosystem functioning and nutrient recycling (Rhoads and Germano, 1986; Nilsson and Rosenberg, 2000; Rosenberg et al., 2001; Solan and Kennedy, 2002). It can also be conditioned by evolutionary factors such as the lack of innovations for deep burrowing (Thayer, 1983) or by extinction of burrowers after mass extinctions (Pruss et al., 2004; Buatois and Mangano, 2011). Although biomixing (reworking of sedimentary particles) and bioirrigation (exchanges of pore water and solutes by burrow ventilation) can be decoupled to some degree (Woodin et al., 2010), estimating the mixing rate and depth on the basis of the stratigraphic record can be used to assess the response and recovery of benthic ecosystems to stress and disturbances and to evaluate long-term trends in ecosystem functioning and biogeochemical cycling (Droser et al., 2002; Canfield and Farquhar, 2009; Tarhan et al., 2015; Gougeon et al., 2018; Buatois et al., 2020). The mixing rate, the mixing depth, and the sedimentation rate represent three parameters that determine the residence time of sedimentary and organic particles in the mixed layer (Meysman et al., 2003). Assuming that biomixing positively relates to bioirrigation, this residence time determines preservation, recycling, and burial efficiency of organic matter, carbonates, and redox-sensitive minerals because it also controls their exposure time to O2 in near-surface sediment zones (Aller, 1982, 1994; Hartnett et al., 1998; Meile and van Cappellen, 2005; Boyle et al., 2014; Aller and Cochran, 2019) and to borers, microbes, and undersaturated pore waters in the so-called taphonomic active zone (TAZ; Davies et al., 1989; Walker and Goldstein, 1999). If sedimentation rate does not change over a given duration of deposition, dividing the depth of the mixed layer by sedimentation rate can be used to estimate the residence time of particles in the mixed layer, and thus their potential exposure to bioirrigation (Wheatcroft, 1990; Tomašových et al., 2019a). However, first, exposure time of particles to O2 is not a simple function of their residence time in the mixed layer and also depends on the size and feeding mode of burrowers and on the persistence and magnitude of their pumping rate (Sandnes et al., 2000; Lohrer et al., 2004; Gingras et al., 2008; Volkenborn et al., 2012; Norkko et al., 2013; Kristensen et al., 2018; Renz et al., 2018; Wrede et al. 2018). For example, deposit feeders mainly promote mixing, whereas suspension feeders and chemosymbionts mainly induce irrigation (Christensen et al., 2000; Michaud et al., 2005). Second, long-term estimates of net sedimentation rate cannot be interpolated to shorter timescales (Jerolmack and Sadler, 2007), and the timescale of mixed-layer formation is similarly confounded by internal temporal variability in bioturbation over shorter timescales (Teal et al., 2008). For example, a 20 cm thick layer deposited under 1 cm yr−1 may be mixed (or irrigated) permanently over 20 years or may remain unmixed for 19 years and then instantaneously be mixed just in a single year. Both the instantaneous mixing and the slower mixing will generate an age-homogeneous distribution of sedimentary particles but will differ in the duration of mixing and in recycling and burial efficiency of redox-sensitive sedimentary particles. Therefore, although the depth of mixing in the stratigraphic record can be estimated on the basis of ichnofabric and trace fossils (Bromley and Ekdale, 1986; Droser and Bottjer, 1988; Savrda and Ozalas, 1993), it is unclear (i) whether mixing leading to age homogenization of sedimentary particles and to the loss of sedimentary fabric was also associated with efficient irrigation and (ii) whether the ichnofabric characterizing a mixed layer in the stratigraphic record developed over yearly, decadal, or longer timescales. This uncertainty differs from temporally explicit estimates of penetration of sediment by O2 and other solute tracers, from estimates of apparent redox potential discontinuity, or from the estimates of the mixed-layer thickness based on 234Th that can be measured in present-day environments (Andersson et al., 2006; Maire et al., 2008; Germano et al., 2011; Gerwing et al., 2018; Solan et al., 2019; Borger et al., 2020).
One criterion that can be used to constrain the exposure of particles to O2 in the mixed layer in the ancient stratigraphic record includes the detection of rapid authigenic mineralization associated with the decay of organic tissues in the absence of O2 (Allison, 1988; Briggs et al., 1991, 1996). The lack of bioturbation that limits O2 exposure and allows preservation of intact, articulated, multi-element skeletal remains under anaerobic degradation of organic matter can induce early pyritization, phosphatization, or silicification of organic tissues (Gabbott et al., 2004; Zhu et al., 2005; Cai et al., 2012; Saleh et al., 2019, 2020; Schiffbauer et al., 2014; Novek et al., 2016). Early pyritization or silicification induced by reactive organics may also generate death masks that stabilize and cement sediment and blanket benthic organisms (Gehling, 1999; Strang et al., 2016; Tarhan et al., 2016; Gibson et al., 2018; Liu et al., 2019; Slagter et al., 2021). Similar pathways stimulated by the decay of labile organics or further sustained by microbial and mucus-forming processes in anaerobic microenvironments (microniches or pockets; Emery and Rittenberg, 1952; Jørgensen, 1977; Borkow and Babcock, 2003; Stockdale et al., 2010; Anderson et al., 2011; Virtasalo et al., 2010, 2013; Lehto et al., 2014) can lead to distinctive clusters of authigenic minerals concentrated in intra-skeletal voids initially filled with organic tissues in otherwise well-preserved skeletal remains (Brett et al., 1991, 2012a, b). These authigenic minerals do not replace soft tissues but form linings or infills located at the sediment–skeletal boundaries in buried fossil assemblages (Gaines et al., 2008). For example, intraskeletal pores (initially containing organic tissues and microbes associated with their decay) lined by framboids or larger pyrite crystals preserved in the stratigraphic record, as observed in interiors of foraminifers, cephalopods, articulated brachiopods, or bivalves, indicate that reduced microenvironments within shells were not re-exposed to O2 by irrigation or exhumed to the sediment–water interface (Hudson, 1982; Schieber and Baird, 2001; Hunda et al., 2006; Schieber, 2012; Machain-Castillo et al., 2019). Such microenvironments thus remained permanently sequestered after their initial formation and can be indicative of spatially and temporally limited bioirrigation, and thus of a shallow depth of the oxycline. However, with the exception of seep environments (Powell et al., 2012) or studies focusing on pyrite infills in burrows (Virtasalo et al., 2010; Gingras et al., 2014; Harazim et al., 2015; Kędzierski et al., 2015; Baucon et al., 2020), pyrite-lined skeletal remains are rarely observed in actualistic studies assessing preservation of organisms with durable skeletal elements in Holocene or Anthropocene marine environments (Best and Kidwell, 2000). This rarity may not be surprising because the preservation of pyrite framboids nucleating at the sites of organic decay (initiated in reduced microenvironments) is limited in habitats with a well-irrigated mixed layer where most of the sulfide produced by sulfate reducers in microenvironments is rapidly reoxidized (Canfield et al., 1993; Wijsman et al., 2002; Canfield and Farquhar, 2009). However, taphonomic and early diagenetic pathways that affect skeletal remains remain poorly explored in environments affected by eutrophication, stratification, and oxygen depletion that tend to be characterized by limited bioirrigation and by high burial efficiency of iron (Carstensen et al., 2014; Kristensen et al., 2014; Lenstra et al., 2019).
The decline in the functioning of marine soft-bottom benthic ecosystems driven by eutrophication and deoxygenation over the past centuries (Schaffner et al., 1992; Valente and Cuomo, 2005; Petersen et al., 2008; Zillén et al., 2008) and affected by changes in biogeochemical cycling (Villnäs et al., 2012; Kristensen et al., 2014; Jokinen et al., 2018) thus represents a unique opportunity (1) to assess the nature of pathways that lead to the preservation of pyrite-lined shells (especially the steps associated with the initial formation of reducing, iron-rich microenvironments and with the subsequent lack of their reoxidation by irrigation and/or by exhumation to the sediment–water interface) and thus can provide taphonomic and early diagenetic analogues for pyrite-lined shells in the deep-time stratigraphic record and (2) to test whether the general decline in bioturbation and the associated shift in the composition of soft-bottom benthic communities detected in sediment cores over the past decades influenced the frequency of pyrite-lined shells in the stratigraphic record. On one hand, the decline in activities of infauna can limit bioirrigation, thus reducing the penetration of sediment by O2 (with more frequent formation of reducing microenvironments where pyrite framboids can precipitate) and decreasing the potential of pyrite framboids to be reoxidized. On the other hand, the decline in activities of infauna can lead to the decline in sediment mixing, thus reducing an iron-based redox shuttle and limiting the development of the suboxic zone rich in dissolved iron that is necessary for confinement of H2S to the location of carcass decay (Canfield et al., 1993; van de Velde and Meysman, 2016; Beam et al., 2018). Here, we focus on Holocene–Anthropocene sediment cores from the northern Adriatic Sea, which harbors diverse types of infaunal and epifaunal benthic communities (Fedra et al., 1976; Zuschin et al., 1999; Zuschin and Stachowitsch, 2009). This sea was affected by eutrophication and by an increase in frequency of seasonal hypoxia in the 20th century (Justić, 1991; Degobbis et al., 2000), with frequent mucilage events (Cozzi et al., 2004; Giani et al., 2005; Precali et al., 2005) and several spatially extensive seasonal anoxic events inducing mass mortality of benthic fauna in the 1970s–1990s (Stefanon and Boldrin, 1982; Faganeli et al., 1985; Stachowitsch, 1991). Oligotrophication has been detected in the northern Adriatic Sea since the 1990s (Mozetič et al. 2010; Djakovac et al., 2012, 2015), although habitats close to the Po prodelta were regularly affected by seasonal hypoxia during the 1977–2008 monitoring (Alvisi and Cozzi, 2016), and hypoxic events were also detected in the Gulf of Trieste in the early 21st century (Kralj et al., 2019). Paleoecological records in sediment cores collected in the Po prodelta and in the Gulf of Trieste showed that the effects of increasing frequency of seasonal oxygen depletion (and other changes related to pollution, sediment turbidity, and trawling) translated into a 20th century regime shift in the composition of soft-bottom molluscan communities (at 10–30 m water depths; Tomašových et al., 2020). Although this shift was characterized by a decline in the depth of the mixed layer during the 20th century, as indicated by an upcore increase in preservation of flood layers and in temporal resolution of molluscan assemblages in sediment cores (Tomašových et al., 2018), the uppermost centimeters of soft-bottom sediments remain relatively well-mixed by burrowers during the late 20th century.
Pyrite can precipitate rapidly at the location of decay of tissues of hosts or at the location of intra-skeletal organic matrices among crystals (we call such pyrite primary linings; Boekschoten, 1966; Brown, 1966) but can also form at the location of decay of secondary inhabitants of shells that were exposed to redox fluctuations in the TAZ for longer (coelobionts, encrusters, or borers – secondary linings; Kobluk and Risk, 1977) or can precipitate in skeletal pores as disseminated nanopyritic inclusions (Brand and Morrison, 1987), leading to darkened and stained valves (Tomašových et al., 2021). However, only primary linings represent unique evidence of limited postmortem exposure time of such shells to O2 from irrigation (with pyrite framboids confined to the location of carcass decay) prior to their transit below the mixed layer into the final stratigraphic record. Here, to assess whether abundant pyrite-lined shells of the hypoxia-tolerant bivalve Varicorbula gibba are informative about bioirrigation and to distinguish primary from secondary linings (and from other types of pyrite associated with skeletal remains that forms over longer timescales), we evaluate (1) the rate of formation of pyrite linings and the depth of their formation (in surface or subsurface sediment zones) on the basis of postmortem age–frequency and depth–frequency distributions of dated specimens of V. gibba in sediment cores, (2) whether pyrite-lined valves more frequently possess a periostracum and higher shell organic content than valves without pyrite (controlling for shell postmortem age), (3) whether the increment-level frequency of pyrite-lined valves correlates negatively with other types of alteration such as disarticulation or bioerosion, and (4) whether the frequencies of pyrite-lined valves change upcore within the Holocene–Anthropocene stratigraphic record and whether they track independently documented changes in community composition, using abundance and shell size of the hypoxia-tolerant bivalve V. gibba.
The northern Adriatic Sea is a relatively low-energy and low-relief, ramp-like shelf environment with a narrow tidal range, with counterclockwise surface circulation, mainly driven by the freshwater input of the Po River (Kemp et al., 1999; Boldrin et al., 2009; Brush et al., 2021). The cyclonic circulation normally deflects nutrient-rich water masses off the Po Delta southwards. However, this circulation slows down during the summer when a local cyclonic gyre can also spread such eutrophic waters towards the eastern Adriatic shelf normally characterized by oligotrophic surface conditions. The decline in circulation leads to the development of a pycnocline and, in combination with high phytoplankton production, to the accumulation of marine snow and mucilages and to bottom-water oxygen depletion in some years across large parts of the northern Adriatic Sea (Stachowitsch, 1991; Penna et al., 1993; Manini et al., 2000; Cozzi et al., 2004; Precali et al., 2005). Sediments associated with silt and clay-rich sediments are relatively rich in iron in deltaic environments (3 %–4 %; Spagnoli et al., 2014) and less so in carbonate sediments off Istria (> 1.5 %–3 % in the Gulf of Trieste; Faganeli et al., 1991, 1994; Dolenec et al., 1998). Iron is bound mainly by iron oxides or by pyrite (as framboids or foram infillings). Pyrite forms 2 %–5 % of the sediments in the Gulf of Trieste (Faganeli and Ogrinc, 2009) and typically less than 1 % in Holocene cores on the Po Plain (Amorosi et al., 2002). Biogeochemical studies performed in the 1990s showed that anaerobic decomposition of organics (mainly sulfate reduction) is a dominant pathway in organic-rich sediments at the Po prodelta (Barbanti et al., 1995). In contrast, less organic-rich sites in the NW Adriatic Sea with slower sedimentation display a higher importance of aerobic respiration and iron reduction (Barbanti et al., 1995; Hammond et al., 1999). This gradient in sedimentation rate leads to lower recycling of organic carbon at the Po prodelta and higher recycling at sites distal relative to river-borne sediments. A similar situation was also observed in the Gulf of Trieste, with higher burial efficiency of organic carbon and nitrogen at muddy sites with a high sedimentation rate at the Isonzo prodelta and with higher recycling at sandy sites with a slow sedimentation rate in the central and southern parts of the Gulf of Trieste (with iron bound with oxides rather than with sulfides; Hines et al., 1997; Arcon et al., 1999; Faganeli and Ogrinc, 2009).
3.1 Sediment cores
Sediment cores collected at five sites in the northern Adriatic Sea (Fig. 1) described and geochronologically dated in our former papers were used to assess stratigraphic changes in the proportion of specimens lined with pyrite. Two sites are located at the Po prodelta (Po 3 and Po 4 at 21 m; Tomašových et al., 2018); one site in the northern Gulf of Trieste, in the Bay of Panzano at 12 m at the Isonzo prodelta (Gallmetzer et al., 2017; Tomašových et al., 2017); one site in the southern Gulf of Trieste off Piran at 23 m (Mautner et al., 2018; Tomašových et al., 2019b); and one site on the southern tip of Istria at Brijuni at 44 m (Schnedl et al., 2018). Sediment cores collected in 2013 are ∼ 1.5 m long (Gallmetzer et al., 2016) and were initially split into 2 cm thick increments in the upper 20 cm and into 5 cm thick increments below. The core diameter was 9 cm at the site Brijuni and 16 cm at the sites Po, Panzano, and Piran. All increments were sieved with 1 mm, and, with some exceptions (at Piran), all individuals of Varicorbula gibba were picked from residues. At Piran, the increments between 10 and 35 cm were split into quarters, and increments between 35 and 45 cm were split to half owing to high shell abundance (Gallmetzer et al., 2019). Van Veen grabs with surface death assemblages were collected in 2014 (Haselmair et al., 2021). Core geochronology, the estimates of sedimentation rates, and the depth of the mixed layer are based (i) on the profiles in the excess activity of 210Pb and (ii) on the stratigraphic distribution of median bivalve shell ages based on amino acid racemization (AAR) calibrated by 14C formerly published in studies devoted to individual sites (at Panzano in Tomašových et al., 2017; at Po in Tomašových et al., 2018; at Piran in Mautner et al., 2018, and Tomašových et al., 2019b; and at Brijuni in Schnedl et al., 2018, and Gallmetzer et al., 2019).
Although these sites are located at similar water depths, they differ in their proximity to clastic input from rivers, grain size, net sedimentation rate, sediment organic enrichment, and iron content. Stratigraphic profiles in grain size and in concentrations of CaCO3, TOC and TN, and Fe concentrations (in 63 µm sediment fraction, documented in Gallmetzer et al., 2017; Mautner et al., 2018; Schnedl et al., 2018) show that the three prodelta sites are exclusively muddy and rich in iron (∼ 3 %), whereas the two locations off Istria are sandy, iron-poor (1 %–2 %), and rich in carbonate skeletal material (molluscs, echinoderms, bryozoans, coralline algae) (Fig. 2). The two Po cores are characterized by high sedimentation rate (∼ 1–2 cm yr−1), the Panzano core was deposited under an intermediate sedimentation rate (∼ 0.2–0.5 cm yr−1, occasionally up to 1 cm yr−1), and the Piran and Brijuni sites are sediment-starved (∼ 0.01–0.03 cm yr−1). At Piran a 25 cm thick skeletal shell bed occurs at 8 cm below the seafloor (Tomašových et al., 2019b), and at Brijuni a 20 cm thick sandy mud in the core top overlies a coarse bryozoan-rich molluscan muddy sand (Tomašových et al., 2021). Upcore changes in median shell age show that sedimentation rates moderately oscillated through time and do not show any increase in the uppermost levels that correspond to the late 20th century. The within-site variability in sedimentation rates is smaller than the marked variability among sites. Sedimentation rates fluctuated between ∼ 1 and 2.4 cm yr−1 during the 20th century at the Po sites (Tomašových et al., 2018) and between ∼ 0.2–1 cm yr−1 over the past 500 years at Panzano (Gallmetzer et al., 2017; Tomašových et al., 2017). Sedimentation rates at Piran and Brijuni were persistently 1 or 2 orders of magnitude lower during both the transgressive and highstand phases (∼ 0.01–0.03 cm yr−1) than at Po and Panzano (Tomašových et al., 2019b, 2021), and we thus refer to Po and Panzano as sites with a high sedimentation rate and to Piran and Brijuni as sites with a low sedimentation rate. The estimates of sedimentation rates based on the slope of the 210Pb profiles below the mixed layer are similar to those based on downcore changes in median shell ages at both Po sites and at Panzano (Fig. 3). However, the 210Pb segments located below the fully mixed layer at Piran and Brijuni are still steepened by biomixing (and thus overestimate sedimentation rates), as is typical of conditions when the rate of biomixing exceeds the rate of sedimentation (Johannessen and Macdonald, 2012). The thickness of the well-mixed surface layer, based on homogeneity of median per-increment shell ages (amino acid racemization calibrated by 14C, Fig. 3a), is 20 cm at Po and at Brijuni, 5 cm at Panzano, and 8 cm at Piran (where a coarse skeletal shell bed occurs at 8–35 cm below the seafloor). The cores at Piran and Brijuni can be subdivided into units deposited during the transgressive phase characterized by rapid increase in accommodation space (transgressive system tract, TST), during the time of maximum ingression (maximum flooding zone, MFZ), and during the highstand phase characterized by a very slow increase in accommodation space (highstand system tract, HST, prior to the 20th century). The uppermost zones contain a mixture of late-highstand and 20th century sediments (Fig. 2, Mautner et al., 2018; Schnedl et al., 2018). The net sedimentation rates at Piran and Brijuni (affected by negligible clastic sediment input and by significant contribution of in situ heterozoan carbonate production) were very slow during the highstand phase and did not increase relative to the condition during the transgressive phase (i.e., prograding sediment bodies did not form during the highstand phase). The core at Panzano captures about 500 years, and 20th century sediments occur in the upper 35 cm. The cores at Po consist of sediments deposited during the early and the late 20th century (and the earliest 21st century), as described by Gallmetzer et al. (2017) and Tomašových et al. (2018, 2019b).
The thickness of the well-mixed surface layer, based on the vertical extent of uniform or irregular segments of profiles in 210Pb excess, is ∼ 16 cm at Po and 6 cm at Panzano, Piran, and Brijuni (Fig. 3b). With the exception of Brijuni, the estimates of the mixed-layer depths based on the 210Pb profiles and the 14C-based shell age profiles are thus similar. At Brijuni, the 6 cm thick mixed layer based on the 210Pb profiles relative to the 20 cm thick mixed layer based on 14C probably reflects the shorter (multi-decadal) half-life of 210Pb relative to the longer time needed to mix the upper 20 cm of sediment and their bioclasts. Downcore increase in the mottling of sedimentary fabric and in time averaging of V. gibba assemblages in 5 cm increments further indicate that the mixed layer extended to more than ∼ 20 cm at Po and Panzano prior to the late 20th century (Tomašových et al., 2018). These estimates of the depth of the mixed layer do not necessarily correspond to depths of instantaneous mixing. They apply to the depths that are fully mixed at yearly and decadal scales at Po and Panzano but at millennial scales at Piran and Brijuni. Some incomplete mixing by burrowers also occurs below these depths, as suggested by the presence of very young shells at 100 cm at the Po sites (Tomašových et al., 2018).
We target specimens of the bivalve V. gibba because this species is common in all cores. V. gibba is a small-sized (< 15 mm), shallow-infaunal, poorly mobile bivalve that has short siphons and thus lives in the upper 3 cm of sediment (Faresi et al., 2012), with the posterior margin located at or slightly below the sediment–water interface. It feeds on suspended phytoplankton but also exploits benthic diatoms, bacteria, and organic detritus at the sediment–water interface (Yonge, 1946). This species has a higher tolerance to reduced oxygen levels relative to other molluscs and invertebrate groups (Holmes and Miller, 2006; Riedel et al., 2012) and can survive for several days and even weeks in anoxic conditions (Christensen, 1970). In the northern Adriatic Sea, it increases in abundance in the wake of short-term, seasonal anoxic or hypoxic events to more than 1000 individuals m−2 (Hrs-Brenko 2006; Nerlović et al., 2011) and grows to 7–8 mm during the first year, achieving the maximum size of ∼ 15 mm in 2 years (Hrs-Brenko 2003). It is classified as an opportunistic species in the assessments of benthic ecosystem health in the Mediterranean Sea (Simboura and Zenetos, 2002; Borja et al., 2000; Moraitis et al., 2018). Soft-bottom molluscan assemblages at water depths below the seasonal thermocline in the northern Adriatic became dominated by this species during the late 20th century sea (Tomašových et al., 2018). The shells of this species consist of two unequally sized valves that are formed by an outer (with a cross-lamellar structure) and an inner (with a cross-lamellar and complex cross-lamellar structure) layer (Fig. 4a). Both valves possess one or more conspicuous internal, 10–100 µm thick conchiolin layers (Fig. 4b–c), with embedded aragonite nodules (< 5 µm) (Lewy and Samtleben, 1979; Kardon, 1998). The internal conchiolin layer in the right valve terminates on the internal surface in a groove between the pallial line and the ventral margin (Fig. 4). The margin of the left valve is pressed against this groove so that the left valve is almost perpendicular relative to the right valve, and the external periostracum of the left valve overlaps with the ventral external margin of the right valve. These traits allow a tight closure of articulated valves. The conchiolin in the internal layers is more refractory and insoluble (Krampitz et al., 1983) than labile organics initially lining the interior of valves. Its intrinsic attributes with (1) tightly closed valves with overlapping periostracum and a small internal ligament (Yonge, 1946), reducing the potential for postmortem disarticulation, and (2) a conchiolin layer located within valves can favor the formation of reduced microenvironments both within shells and within individual valves (Fig. 4).
3.2 Age distributions of pyrite-lined valves
Ratios of D- and L-isomers () of eight amino acids (aspartic, glutamic, serine, alanine, valine, phenylalanine, isoleucine, and leucine) and their concentrations in valves of V. gibba were measured at Northern Arizona University using reverse-phase high-pressure liquid chromatography (RP-HPLC) and the procedures of Kaufman and Manley (1998). ratios measure the extent of razemization and thus represent a geochronological tool (Kosnik et al., 2008; Allen et al., 2013). These data were measured in 252 valves from Po 3, in 243 valves from Po 4, in 311 valves from Panzano, and in 232 valves from Piran, and they were presented with age calibrations of aspartic acid by 14C-dated valves by Tomašových et al. (2017, 2018) and Mautner et al. (2018). To constrain the rate and the location of pyrite formation on the basis of postmortem age data, we evaluated (1) whether valves of the same postmortem age (binned to 10 years at Po and to 50 years at Panzano), with and without pyrite linings, differ in their mean stratigraphic depth or whether pyrite-lined valves are located deeper; (2) whether the valves with and without pyrite linings differ in their burial rate below the present-day mixed layer (with pyrite-lined valves expected to be buried earlier to deeper zones with reducing conditions); and (3) whether valves of the same age with and without pyrite linings differ in their total content of amino acids. We assess the differences in depth and age between valves with and without pyrite by comparing their mean values and 95 % bootstrapped confidence intervals. We estimate burial rates of valves below the mixed layer by fitting age distributions of valves with and without pyrite linings from Po and Panzano to two models that assume that the input of dead shells to the death assemblage is constant during their residence in the mixed layer (and thus over the duration of time averaging). The parameters estimated by these models are related to the burial rate and depend on the steepness of age distributions in the mixed layer. However, they are also determined by the disintegration rate within the mixed layer (Tomašových et al., 2014). First, a simple model with a temporally constant loss rate of valves (λ) from the mixed layer (with loss occurring by disintegration and/or burial) predicts that age distributions can be well-fitted by the exponential distribution (disintegration–burial model). Second, a more complex (sequestration) model where disintegration rate declines from λ1 to λ2 at some sequestration rate τ predicts that the resulting age distributions are heavy-tailed, typically owing to exhumation of older valves to the sediment surface, with λ1 corresponding to the disintegration rate of young valves, λ2 corresponding to the reduced disintegration rate of older valves, and τ to the sequestration rate that can correspond to the burial rate (Tomašových et al., 2014). The Akaike information criterion corrected for small sample size shows similar support for these two models at Po and Panzano in valves both with and without pyrite linings, with either a lower Akaike information criterion (AIC) for the simple model or a slightly higher support for the sequestration model that does not exceed 2–3 units and small differences between λ1 and λ2 in the sequestration model (Table A1). The λ parameter estimated by the simple model at Po and at Panzano is similar both to 210Pb-based estimates and to 14C shell-based estimates of the sedimentation rate (1–2 cm yr−1 at Po and 0.2 cm at Panzano). Therefore, we infer that this λ parameter at Po and Panzano corresponds to burial rates and can be used to compare burial rates of valves with and without pyrite linings.
3.3 Taphonomic scoring
To assess the nature and types of pyrite linings, we evaluated preservation of all specimens of V. gibba at light-microscope scale at 10–20× magnification. We investigated several specimens with a scanning electron microscope (SEM) and with backscattered electrons (BSEs), using an electron probe microanalyzer at 100–1000× magnification. The chemical composition of pyrite and iron oxides was validated with energy-dispersive X-ray spectroscopy. All valves of V. gibba that were dated by amino acid racemization at four sites (Po 3, Po 4, Panzano M28, and Piran M53) were scored. At Po 3 (replicate cores M12, M13, and M14), Po 4 (cores M20 and M21), and Panzano (cores M28 and M29), all additional specimens were scored under a light microscope. At Brijuni, all specimens of V. gibba from every second increment were scored. Eight alteration variables were scored on specimens of V. gibba at light-microscope magnification (10–20×): (1) presence of black pyrite framboids that form strings, clusters, or continuous coatings on internal valve surfaces; (2) loss of periostracum and/or of the internal conchiolin layer (if either external periostracum or internal conchiolin layer is visible, periostracum is scored as being preserved); (3) disarticulation; (4) internal fine-scale surface dissolution (shallow pits); (5) internal bioerosion (generated by algae and sponges, excluding predatory drilling); (6) external encrustation; (7) intense surface wear on external and internal valve surfaces (extensive pitting and wear, leading to loss of external ornamentation); and (8) penetrative blueish or dark gray staining (induced by nanopyritic inclusions that fill valve microporosity). All data are available in the Supplement.
3.4 Geographic and stratigraphic differences in the frequency of pyrite-lined valves
To evaluate stratigraphic and geographic changes in preservation of V. gibba at the centimeter scale of stratigraphic increments, we computed relative frequencies of specimens with a given alteration relative to the total number of specimens in 4 cm (pooling 2 cm increments in the upper 20 cm in each core) and 5 cm thick increments at five sites. The frequency of disarticulated shells is computed as the number of all articulated specimens in a given increment divided by the minimum number of individuals (i.e., the sum of articulated shells plus the higher number of left or right valves). Although the estimates of disarticulation are biased upward owing to disarticulation that takes place during sieving, we assume that this bias affects all increments equally. All increments were plotted and analyzed in stratigraphic analyses. However, the downcore stratigraphic profiles reflect (1) downcore changes in early diagenetic conditions within the mixed layer driven by the depth of the oxycline and by the depth of iron and sulfate reduction and (2) chronological changes in biogeochemical processes (e.g., driven by eutrophication-induced changes in bioirrigation). Therefore, assuming that preservation of valves below the mixed layer is permanent, our inferences about chronological changes in preservation are based on the subsets of stratigraphic profiles below the mixed layer (and on increments with more than 10 scored individuals). In analyses assessing bivariate and multivariate relationships among all alteration variables, we extracted the increments located below the mixed layer with more than 10 specimens, and we measured Spearman rank correlations between per-increment frequencies of pyrite-lined valves and other types of alteration. We used principal coordinate analysis (PCO) and Manhattan distances to investigate (1) geographic differences in preservation of V. gibba among all sites and (2) differences in preservation of V. gibba between the late 20th century increments (that primarily capture the main eutrophication phase) and increments that are older (corresponding to the early 20th century at the Po prodelta and the 16–19th centuries at the Isonzo prodelta) at the three prodelta sites with high sedimentation rates.
3.5 Relationship with macrobenthic community composition
To assess whether shell preservation responds to the ecosystem shift in the 20th century, we rank-correlated the frequencies of pyrite-lined valves with two indicators of macrobenthic community states typical of the eutrophication phase (marked by high abundance and size of the hypoxia-tolerant bivalve V. gibba), including (1) proportional abundances of V. gibba in 5 cm increments (relative to the total molluscan abundance) and (2) maximum shell size of V. gibba measured by the 95th percentile of length distributions per increment. The chronological increase in abundance and size of this poorly mobile species can reflect an increase in the contribution of surficial sediment modifiers to the functioning of benthic communities (V. gibba belongs to surface modifiers in the classification of mixing potential of benthic species; Queirós et al., 2013), with a concomitant decline in abundance of biodiffusors. Although proportional abundances are affected by between-core variability in time averaging and in net sedimentation rate, stratigraphic trends in proportional abundance within cores can be robust because sedimentation rates remained relatively constant during the deposition of individual cores.
4.1 Preservation of pyrite and valves at light-microscope scales
The preservation of V. gibba valves varies from well-preserved valves with (Fig. 5a–b) or without periostracum (Fig. 5c–d), with a well-preserved pallial line and the internal conchiolin groove (pl and clg in Fig. 5), to valves with signs of fine-scale dissolution and delaminated into two distinct valve layers (originally separated by the internal conchiolin layer, Fig. 5e–f and g–h). This delamination of valves into two layers is a characteristic signature of V. gibba preservation driven by the decay of the internal conchiolin layer at all sites (Figs. 5e–h, 6c–h). The internal conchiolin layer (icl) located ventrally below the pallial line can be exposed in fragments (Fig. 5i) or in delaminated valves (Fig. 5f). The interiors of valves at Po and Panzano are frequently lined by finely disseminated microcrystals and framboids (Fig. 5j–k) or by strings (Fig. 5l), continuous (Fig. 5m–n) or patchy coatings (Fig. 5o–p) formed by pyrite framboids. In contrast, internal pyrite linings are rare on valves at Piran and Brijuni (Fig. 6).
In thin sections, well-preserved valves without any pyrite framboids represent the initial preservation state prior to any alteration (Fig. 7a). The pyrite linings in thin sections are visible as linings formed by pyrite framboids dispersed on interior valve surfaces (black grains in Fig. 7b–d) and in the conchiolin layer (Fig. 7e). Pyrite linings are frequently associated with internal fine-scale dissolution and can co-occur with isolated reddish grains of Fe oxides at all sites. However, the fine-scale dissolution of valves at Po and Panzano is minor and shallow and is still associated with some surviving portions of periostracum or the conchiolin layer. Specimens from Piran and Brijuni are bored and dissolved but are rarely lined by continuous coatings of pyrite framboids (Fig. 6). However, valves at Piran and Brijuni can contain dispersed framboids that are mainly concentrated in borings (Fig. 7f). Some relatively pristine valves from Po and Panzano show a blueish- or gray-colored staining on the interior and exterior, still with well-preserved external ornamentation (Fig. 5q–t). In contrast, gray-stained valves at Piran and Brijuni are worn, degraded by bioerosion, and encrusted by bryozoans, serpulids, or coralline algae on interior sides (Fig. 6). In thin sections, macroborings produced by sponges are very rare in valves from Po and Panzano, and bioerosion is primarily limited to simple borings that are a few micrometers thick. In contrast, valves from Piran and Brijuni exhibit dense borings (Fig. 7f).
4.2 Preservation of pyrite at 100–1000× magnification
On one hand, BSE images show that pyrite framboids preserved on the interiors of well-preserved valves vary in shape, size (5–10 µm), and packing, ranging from densely and regularly packed microcrystals within spherical framboids up to loosely and irregularly packed microcrystals within irregularly shaped framboids (Fig. 8a–g). Framboids also partly fill pores between aragonite nodules (arrows in Fig. 8i) within the conchiolin layer (that is ∼ 10–100 µm thick) where they can be partly altered by Fe oxide rims (Fig. 8h–i). Larger euhedral pyrite crystals were not observed on valve interiors. At Piran and Brijuni, pyrite framboids located in borings (secondary linings) occur within strongly bored and stained valves (Fig. 8l). On the other hand, in addition to framboidal pyrite that forms primary or secondary linings, another type of pyrite preservation can be detected at high magnification and is characteristic of stained valves. In BSE images, the valves that are stained contain disseminated or dispersed inclusions of nanopyrite (< 1 µm), located in primary inter-crystalline skeletal pores or in secondary pits formed by dissolution or bioerosion in the inner or the outer layer; they are not located on valve surfaces or within the conchiolin layer (Fig. 8j–l). Valve portions with high abundance of nanopyritic inclusions are characterized by blueish or grayish color.
SEM images show that pyrite framboids on surfaces of well-preserved, non-bored, or unworn valves at the Po and Isonzo prodeltas are attached to the original interior surface (primary linings). Dispersed microcrystals and subspherical to spherical framboids consisting of microcrystals uniformly cover inner, well-preserved, and smooth surfaces or fill irregularities close to the groove around the termination of the internal conchiolin layers (Fig. 9a–d). Microcrystals and framboids co-occur and can be distributed across the whole interior surfaces in clusters (Fig. 9e) and in strings (Fig. 9f) and locally co-occur with Fe oxides and gypsum (Fig. 9f). Pristine valves show no or weak bioerosion by larger borers (sponges), although they can be penetrated by simple non-branching borings with micrometric diameters. In contrast, pyrite framboids are infrequent on interiors of valves that are affected by dense borings produced by sponges, forming complicated galleries, with or without sediment infill (Fig. 9g–h). SEM and BSE observations thus show that pyrite framboids directly attached to interior surfaces of well-preserved and weakly bored valves represent primary linings, whereas pyrite framboids occurring on highly altered valves are located in borings and represent secondary linings.
4.3 Age and depth distributions
Age distributions of valves with and without pyrite linings show right-skewed shapes in the mixed layer at the prodelta sites, with a median age equal to 7–10 (without pyrite) and 7–18 years (with pyrite linings) at Po (in the upper 20 cm) and equal to 11 (without pyrite) and 15 years (with pyrite linings) at Panzano (in the upper 6 cm), respectively (Fig. 10a–f). The increments in the mixed layer are thus dominated at these sites by the most recent cohorts younger than ∼ 10 years. Therefore, the pyrite framboids form rapidly at yearly scales at Po and Panzano. The simple preservation model with temporally constant burial outperforms or is equally efficient relative to more complex sequestration models for valves both with and without pyrite in the mixed layer at Po and Panzano. Both types of valves exhibit the same distribution shape well-fitted by the exponential distribution, with a similar steepness of the right tail (black lines in Fig. 10a–f, Table A1). The support for the simple disintegration–burial model thus indicates that both types of valves are buried at a similar rate below the mixed layer at Po and Panzano (with overlapping 95 % confidence intervals, Fig. 10a–f). Age distributions of V. gibba valves without pyrite linings in the mixed layer at Piran are right-skewed but heavy-tailed and contain valves that are older than 1000 years (median age = 1100 years; only one 140-year-old valve was lined by pyrite; figure not shown), indicating slower rates of burial than at Po or Panzano and a more complex preservation dynamic associated with exhumation. λ2 is 2 orders of magnitude smaller than λ1, and τ is comparable to 14C shell-based estimates of net sedimentation rate (∼ 0.01 cm yr−1) at Piran, indicating much longer residence times of valves in the mixed layer and a temporal decline in their disintegration rate. At the scale of the whole core, median ages of pyrite-lined valves and valves without pyrite are also comparable at Po (27 and 33 years with and without pyrite, respectively) and Panzano (100 and 124 years with and without pyrite linings, respectively) (Fig. 10g–l). However, the whole-core age distributions of valves at Po and Panzano show signs of multimodality, and the frequency with pyrite-lined valves peaks at 1986 CE at Po and at 1963 CE at Panzano. Equally old pyrite-lined valves and valves without pyrite at Po and Panzano tend to be located at similar depths within the mixed layer (Fig. 10m–o). Multimodal whole-core age distributions and stratigraphic changes in abundance indicate that input rates of V. gibba were not constant over the duration of core deposition at all sites and especially increase in abundance after∼ 1950 CE (Tomašových et al., 2018). However, the burial-rate parameter based on the exponential model (assuming the temporally constant input of V. gibba) can be realistic when based on the topcore increments characterized by yearly to decadal time averaging at Po and Panzano (i.e., these increments were deposited after the mid-20th century increase in dominance by V. gibba). The mean depth of valves younger than 10 years is 20 cm for specimens both with and without pyrite at Po, and pyrite-lined valves are located deeper (at 60 cm) than valves without pyrite (at 40 cm) in the 20-year cohort (Fig. 10m–n).
4.4 Preservation of pyrite-lined valves relative to other types of alteration
Controlling for postmortem age, valves lined by pyrite contain higher concentrations of amino acids than valves without pyrite at Po and Panzano (Fig. 11). Median concentrations of amino acids in valves with pyrite linings typically exceed those in valves without pyrite within the same age cohort (Fig. 11a–c), and the log–log relationship between postmortem age and amino acid concentrations shows that intercepts of valves lined by pyrite exceed intercepts of valves without pyrite by a factor of ∼ 2 (Fig. 11d–f). At the scale of individual specimens, pyrite-lined valves possess some relicts of periostracum or the conchiolin layer more frequently than valves without pyrite linings (Fig. 11g–i). All articulated shells of V. gibba from Po and Panzano that were opened had black strings or coatings of pyrite framboids on the valve interiors. At the scale of increments, the relations between preservation of pyrite-lined valves and other types of alteration exhibit three patterns. First, per-increment frequencies of pyrite-lined valves rank-correlate negatively with the frequencies of disarticulated shells (Fig. 12a), with the frequencies of valves without any relicts of periostracum or the conchiolin layer (Fig. 12b–c), and with the frequencies of bioerosion, staining, and encrustation (Fig. 12d–f). Second, the rank correlation between per-increment frequencies of pyrite-lined valves and frequencies of dissolved valves across all sites is low. However, partitioning the sites by high and low sedimentation rate, frequencies of pyrite-lined valves correlate with frequencies of dissolved valves positively at Po and Panzano and negatively at Piran and Brijuni (Fig. 12g). Third, with the exception of pyrite linings, all other types of alterations rank-correlate positively with each other (Fig. 12h–o). These correlations are determined by the among-site gradient in sedimentation rate (associated with the gradient in grain size and carbonate content): V. gibba valves at sites with high sedimentation are well preserved and rarely bored, encrusted, or abraded (Fig. 5). In contrast, V. gibba valves at sites with slow sedimentation show a broader range of preservational signatures, with a high abundance of bored, encrusted, worn, and stained specimens (Fig. 6). Valves with periostracum or a conchiolin layer are abundant at Po and Panzano (with 10 %–80 % specimens per increment), whereas such specimens are extremely rare at Piran and Brijuni (< 1 %). Principal coordinate analysis of increments from all sites shows a major separation in preservation of V. gibba among increments deposited at sites with low and high sedimentation rates (Fig. 13a–b). The first PCO axis correlates negatively with frequencies of pyrite linings and positively with all other alteration variables (with the exception of fine-scale dissolution).
4.5 Stratigraphic trends in the frequency of pyrite-lined valves within the mixed layer
Within the mixed layer, the frequency of pyrite-lined valves does not show any consistent downcore trends at the Po prodelta (Fig. 13d). Although valves with pyrite increase in abundance below the mixed layer at the scale of 10 cm increments from 15 %–24 % at 10–20 cm to 35 %–40 % at 20–90 cm at at Po 4, there is no clear downcore trend across this transition at Po 3 where the frequency of pyrite-lined valves is ∼ 30 %–40 % both in the mixed layer and at 20–90 cm. The uppermost 5 cm at Po 3 and Po 4 already contains more than 20 % and 40 % of pyrite-lined valves, respectively (Fig. 13d). The abundances of pyrite-lined valves below the mixed layer increase from 10 %–20 % at 4–8 cm to 55 %–70 % at 12–20 cm at Panzano, with the increase coinciding with the base of the mixed layer at 6 cm. At Piran and Brijuni, the frequencies of pyrite-lined valves within the mixed layer do not show any obvious trend.
4.6 Stratigraphic trends in the frequency of pyrite-lined valves below the mixed layer
At sites with high sedimentation rate, the frequency of pyrite-lined valves is highest (50 %–80 %) in the late 20th century increments in the upper part of cores (at 20–80 cm at Po and at 8–20 cm at Panzano, Fig. 13d), coinciding with the eutrophication and high frequency of hypoxia. These increments at Po are also characterized by lower mottling, by higher preservation of flood layers, and by lower time averaging (median interquartile age range ranges up to 15 years; Tomašových et al., 2018) when compared to increments in the lower part of cores (at 80–150 cm, with median interquartile range (IQR) equal to 25–28 years; Tomašových et al., 2018). The maximum frequency of pyrite-lined valves declines downcore to 20 % at the Po prodelta (at 80–150 cm) and to 30 %–40 % at Panzano (at 20–150 cm) in increments deposited prior to the late 20th century. The frequencies of pyrite-lined valves do not change markedly at sites with slow sedimentation and are typically less than 20 % at Piran and Brijuni. The frequencies of pyrite-lined valves at Piran and Brijuni further decline when they are limited to valves not affected by bioerosion (black circles in Fig. 13d). Focusing on these sites with high sedimentation rate, PCO shows consistent separation between the latest HST and the late 20th century increments (Fig. 13c), reflecting the chronological increase in the frequency of pyrite linings. This within-core increase in the frequency of pyrite linings is coupled with an upcore increase in the frequency of valves without the periostracum (Fig. 14a), in the frequency of articulated valves, and in the frequency of valves with fine-scale dissolution (Fig. 14b–c). At sites with slower sedimentation and coarser, carbonate-rich sediments, the frequency of pyrite-lined valves remains constant upcore (< 20 %), and the frequency of pyrite-lined valves not affected by borers is < 10 %. The frequency of bored specimens gradually increases from 20 %–30 % in the lower (transgressive systems tract) increments to 70 %–80 % in the upper (late-highstand systems tract) increments at Piran (Fig. 14). In contrast, the frequency of bored specimens gradually declines from 90 %–100 % in the lower (transgressive systems tract) increments to ∼ 40 % in the upper highstand increments at Brijuni (Fig. 14). Although the frequency of pyrite linings is low, valves at Piran and Brijuni show another mode of preservation with pyrite: they frequently contain disseminated nanopyritic inclusions within borings, leading to their darkening and staining (> 20 %).
4.7 Relationship between pyrite linings and the composition of benthic communities
Per-increment maximum shell size of V. gibba correlates positively with its proportional abundance (r=0.3, p=0.0006) across all sites. Proportional abundance of V. gibba per increment correlates weakly with the per-increment frequency of valves lined with pyrite framboids (r = 0.21, p= 0.016, Fig. 15a). In contrast to regional-scale relationships that are affected by between-core differences in time averaging, the positive relationships between proportional abundance and the frequency of pyrite-lined valves are moderately high at Po (r (Po 3) = 0.61, p= 0.0015, r (Po 4) = 0.6, p=0.003, r (Po pooled) = 0.56, p < 0.0001, Fig. 15a). The relationships between maximum shell size of V. gibba and the frequency of pyrite linings are significantly positive at the scale of individual cores at sites with a high sedimentation rate (r (Po 3) = 0.65, p = 0.0007, r(Po 4) = 0.49, p= 0.017, r (Po pooled) = 0.61, p < 0.0001, r (Panzano) = 0.46, p= 0.0002, r (Piran) = 0.55, p= 0.16, r (Brijuni) = 0.11, p= 0.71, Fig. 15b). Within-core stratigraphic series at Po and Panzano show autocorrelation in the frequency of pyrite-lined valves and in abundance and maximum shell size at lag 1 (stratigraphic series at Brijuni and Piran do not show autocorrelation in these traits). Although differencing the stratigraphic series to remove autocorrelation reduces the strength of the bivariate relationships, rank correlations between the frequency of pyrite-lined valves and maximum size of V. gibba remain significantly positive at Panzano (r (size) = 0.32, p= 0.017; r (biomass) = 0.34, p= 0.02) and of borderline significance at Po if increments from Po 3 and Po 4 are pooled (r (size) = 0.3, p= 0.047; r (biomass) = 0.28, p= 0.033). Therefore, the upcore increase in the frequency of pyrite-lined shells directly parallels ecological changes characterized by an abrupt increase in maximum shell size and abundance of V. gibba, contributing to increasing importance of shallow-infaunal groups that mix uppermost sediment zones but have weaker bioirrigation potential.
5.1 Effects of net sedimentation rate and grain size on preservation of pyrite linings
Our observation that the pyrite-lined valves are preserved at high abundance in the subsurface stratigraphic record at the Po and Isonzo prodeltas (with sedimentation rates exceeding ∼ 0.2 cm yr−1) but are infrequent at Piran and Brijuni (with sedimentation rates < ∼ 0.02 cm yr−1) indicates that the first-order condition for their permanent sequestration below the mixed layer is enhanced when net sedimentation rate is high and sediments are fine-grained, with residence time of sedimentary particles (including valves) in the mixed layer (when they may be exposed to O2 from bioirrigation) not exceeding more than several years or a few decades. Some pyrite framboids on valves at coarse-grained sites with slow sedimentation represent secondary linings because they directly occur within borings in heavily bored valves (i.e., the difference between frequencies of pyrite linings in all and non-bored valves is large at Brijuni, Fig. 13d). This preservation contrasts with well-preserved pyrite-lined valves with well-developed pyrite linings (not limited to borings) at sites with a high sedimentation where exclusion of bored valves does not reduce their frequency (i.e., the difference between frequencies of pyrite linings in all and non-bored valves is small at Po and Panzano, Fig. 13d). The preservation of primary pyrite linings is thus largely limited to sites with high sedimentation rate (> 0.2 cm yr−1).
First, larger grain size and sediment porosity of coarse-grained sediments enhance advective pore-water fluxes driven by bottom currents, hydraulic sediment reworking, or bioirrigation (Taylor et al., 2003; Mermillod-Blondin, 2011; Ahmerkamp et al., 2017). These processes deepen the oxycline and promote higher exposure of organics within shells to O2 and stronger iron recycling (Aller, 1994) relative to fine-grained sediments where pore-water fluxes are dominated by diffusion (Mermillod-Blondin and Rosenberg, 2006; Meysman et al., 2006). Muddy sediments are on average oxygenated to less than 1–2 cm in the northern Adriatic Sea (Epping and Helder, 1997; Moodley et al., 1998, 2000), and zones with high concentrations of dissolved iron tend be limited to the uppermost 5 cm in the NW Adriatic Sea (Hammond et al., 1999) and in the Gulf of Trieste (Faganeli and Ogrinc, 2009). In contrast, sandy sediments exhibit stronger bioirrigation in the upper 20 cm (Faganeli and Ogrinc, 2009). Such conditions can inhibit the initial formation of reduced microenvironments. Second, the lower concentrations of iron in sediments can reduce the probability of initial pyritization at coarse-grained sites rich in carbonate sediments even in reduced microenvironments, with H2S diffusing away from the decay sites owing to the low availability of dissolved iron (Raiswell et al., 1993; Allen, 2002). Third, at sites with slow sedimentation rates (∼ 0.01 cm yr−1) and coarse and permeable sediments less rich in iron and organic carbon, regardless of bioturbation, valves will be exposed to redox fluctuations in the TAZ for longer than at sites with a high sedimentation rate, leading to intense alteration of valves by borers, encrusters, or pore waters that tend to be undersaturated with respect to aragonite in the upper 10–20 cm at the Po prodelta (Hammond et al., 1999) and in the Gulf of Trieste (Ogrinc and Faganeli, 2003). This effect will minimize both the initial formation of reduced microenvironments and their susceptibility to reoxidation. Higher levels of bioerosion, encrustation, ornamentation loss, and staining at Piran and Brijuni than at Po and Panzano (Fig. 12–13) thus indicate that slow sedimentation rates (∼ 0.01–0.03 cm yr−1) reduce the preservation potential of framboidal linings by increasing their exposure to bioirrigation or to exhumation. In contrast to very low frequency of pyrite-lined valves at sites with low sedimentation rate, frequency of valves stained by nanopyritic inclusions is higher at these sites, probably reflecting long (millennial-scale) subsurface exposure of less reactive iron-bearing minerals (relative to highly reactive iron oxides and oxyhydroxides) to sulfidic conditions (Raiswell and Canfield, 1996). A similar relationship with darkened specimens enriched in minerals possessing iron sulfides being more damaged by disarticulation, bioerosion, and encrustation, in contrast to specimens less affected by discoloration, was observed by Kolbe et al. (2011) in Ordovician brachiopods. Low sedimentation rates associated with coarse-grained sediments thus exacerbate not only residence time of skeletal remains in the shallowest sediment zones but also their net exposure to O2. Higher recycling of organic carbon, nitrogen, and sulfur at sites with slow sedimentation in the northern Adriatic Sea is supported by pore-water biogeochemical profiles that show their higher burial efficiencies at the Po prodelta relative to sites with slower sedimentation in the NW Adriatic Sea (Giordani et al., 1992, 2002; Hammond et al., 1999). Similarly, recycling efficiency of organic carbon and nitrogen is about 85 % at Piran and in the central parts of the Gulf of Trieste and less at proximal deltaic locations off the Isonzo prodelta (Faganeli and Ogrinc, 2009). High sedimentation rates typical of deltaic environments can limit mixing and irrigation via high substrate instability (MacEachern et al., 2005; Bhattacharya et al., 2020). Benthic communities at the Po Delta are indeed affected by short-term seasonal variability in sediment input and reworking (Ambrogi et al., 1990; Paganelli et al., 2012). However, habitats deeper than ∼ 20 m at the Po prodelta are largely beyond the reach of proximal deposition of thicker flood deposits (Palinkas and Nittrouer, 2007; Tesi et al., 2012). The benthic communities inhabiting these habitats seem to be mainly limited by the frequency of hypoxic events rather than by substrate instability (Crema et al., 1991; Simonini et al., 2004; Tomašových et al., 2020). Although high background sedimentation rate (or rapid episodic burial) is a necessary condition for preservation of pyrite linings, we argue below that it is not a sufficient condition and that potential for reoxidation must also be reduced by ecological factors (such as hypoxia), which limit the abundances of irrigating infauna.
5.2 Pyrite-lined valves in subsurface zones as signatures of limited bioirrigation
Pyrite framboids formed soon after, or concurrent with, the decay of tissues of V. gibba and associated microbes. This is indicated by the preferential occurrence of pyrite linings in valves with periostracum and with higher organic content (with median age < 15 years in the surface mixed layer) and the negative correlation of pyrite-lined valves with the frequencies of other types of alteration at the scale of increments (framboids arranged in filaments or strings in Figs. 5l or 7f resemble bacterial relicts; Westall, 1999; Wilson and Taylor, 2017). Two steps are necessary for preservation of pyrite linings in the subsurface stratigraphic record, including their initial formation in reduced microenvironments rich in dissolved iron and the subsequent lack of their reoxidation.
Initial sequestration in reducing, iron-rich zones. The early formation of concentrations of pyrite framboids that cluster on valve surfaces requires (1) that the organic tissues within shells do not decay or are not scavenged under aerobic conditions and (2) that sediment is rich in iron so that sulfides produced by sulfate reduction are confined to the decay location (Fisher and Hudson, 1987; Raiswell et al., 1993; Farrell et al., 2009; Schiffbauer et al., 2014). Such early sequestration conditions can occur under the decay of organics in suboxic conditions in non-sulfidic, iron-dominated porewaters (Berner, 1969; Briggs et al., 1996; Allen, 2002; Raiswell et al., 2008; Stockdale et al., 2010): (i) when freshly dead shells are episodically buried under a deposition of new sediment (obrution, Brett et al., 1997) sourced by river floods or storms, and can decay in reducing conditions beyond the reach of burrowers, the thickness of the obrution deposits needs to be sufficiently high so that pyrite is not reoxidized by burrowing infauna later (Allison, 1988; Brett et al., 2012a, b; Schiffbauer et al., 2014) and/or (ii) when bioirrigation is shallow or intermittent and biomass of decaying infaunal organisms remains tightly enclosed within shells (as in V. gibba) or within burrows (Thomsen Vorren, 1984; Hansen et al., 1996), generating reducing microenvironments even without obrution (Jørgensen, 1977). Although these two pathways can be complementary, they may also act independently.
The first scenario with obrution is frequently invoked in the deep-time stratigraphic record because it explains the short exposure of organic remains to O2 and their rapid sequestration below the mixed layer into the historical layer (Brett et al., 2012a). Distinct layers deposited by major decadal floods preserved in cores at the Po prodelta (Tesi et al., 2012; Tomašových et al., 2018) may have triggered episodic burial of benthic communities with V. gibba, but similar flood-event layers were not detected at Panzano. However, first, the major discharge events that lead to the deposition of flood deposits occur at decadal scales at the Po prodelta (seven events during the 20th century; Zanchettin et al., 2008), whereas age distributions of pyrite-lined valves indicate that pyrite linings form continuously at yearly scales. The frequency of flood events did not increase during the 20th century, in contrast to the increasing frequency of pyrite-lined valves in the upper parts of cores at Po and Panzano. Second, pyrite-lined valves younger than 10 years old occur at high abundance in the uppermost 5–10 cm of the mixed layer close to the sediment–water interface, indicating that they do not represent transient valves that were just recently exhumed from deeper zones. Third, equally old valves with and without pyrite linings occur at similar depths, and their age distributions at Po and Panzano are similar (Fig. 9a–f), indicating that valves with and without pyrite were buried below the mixed layer at a similar rate. A single episodic burial pulse that mixes living or recently dead shells (with decaying biomass and potential for framboid formation) with older shells (without biomass) will generate one age distribution of valves with pyrite linings dominated by younger cohorts and another age distribution of valves without pyrite linings dominated by older cohorts. Age distributions of valves with pyrite linings generated by such episodic burial should be steeper and their median ages should be lower relative to valves without linings, in contrast to our observations at both Po and Panzano. We thus suggest that the pyrite framboids did not preferentially form within valves that were rapidly buried deeper in sediments (either by new sediment deposition or by burrowers) as predicted by the obrution scenario and rather precipitated in near-surface sediment zones naturally inhabited by V. gibba.
In the second scenario, shells can be located in reducing microenvironments close to the sediment–water interface even without any fast episodic burial by obrution when irrigation is persistently patchy and a large portion of dead shells are exposed to reducing conditions in sediment pockets. The uppermost sediments become oxygen-depleted during late-summer hypoxic events in the northern Adriatic Sea (Stachowitsch, 1984; Cermelj et al., 2001), with the oxygen demand of sediments increased by the decay of phytoplankton and high-biomass benthic communities during late-summer mucilage and mass mortality events (Stachowitsch, 1984; Herndl et al., 1987, 1989; Nebelsick et al., 1997). Such organic enrichment can lead to porewater sulfidization and to exhaustion of highly reactive iron from porewaters, but organic-rich sites at the Po prodelta still show high concentrations of dissolved iron in the uppermost few centimeters (Barbanti et al., 1995). Sediment mixing by (weakly irrigating) infauna tends to counteract the exhaustion of dissolved iron and the potential buildup of H2S in porewaters because burrowers transfer particles with iron oxides from the sediment–water interface to reducing conditions in subsurface zones (Dhakar and Burdige, 1996; Faganeli and Ogrinc, 2009; van de Velde and Meysman, 2016). Several lines of evidence indicate that this second scenario, the spatially limited bioirrigation coupled with the inherent potential of decaying tissues in articulated shells of V. gibba to generate reducing microenvironments in near-surface muddy sediments with iron-dominated porewaters, is important. First, qualitative observations indicate that pyrite linings are very rare in valves of Nucula that co-occur with pyrite-lined V. gibba valves, and pyrite linings occur rarely in apertures of gastropods. The tightly articulated shells of V. gibba can be intrinsically susceptible to the formation of reducing conditions owing to (i) the overlapping periostracum, (ii) the internal groove that can lock valves to some degree, and (iii) low opening moments of a small internal ligament that can be insufficient to open valves against the sediment pressure (as in other members of the Myoidea; Trueman, 1954; Yonge, 1982). Second, the high abundance of very young and well-preserved pyrite-lined valves in the uppermost 5–10 cm of the mixed layer suggests that they form in the uppermost sediment zones and that the oxycline thus tends be shallow. With the exception of burial of V. gibba to their position just below the sediment–water interface during their life, postmortem obrution by episodic sediment deposition is not needed for the initial formation of pyrite linings when sediment irrigation is limited (but biomixing still allows iron recycling to generate zones rich in dissolved iron).
The lack of reoxidation. Most of the sulfide is reoxidized in marine environments with bioirrigation and sediment exhumation by burrowers (Canfield et al., 1993; Thamdrup et al., 1994). Reduced conditions with pyrite linings within shells or burrows will thus be transient when sedimentation rate is low and/or when bioirrigation and sediment exhumation by burrowers oxidize such microenvironments (Bertics and Ziebis, 2010). The positive relation between pyrite and fine-scale dissolution and transformation of some pyrite grains to iron oxides and gypsum indicates that some pyrite-lined valves at Po or Panzano were briefly exposed to oxygenated pore waters and were partly dissolved by sulfuric acid (Cai et al., 2006; Pirlet et al., 2010; Hu et al., 2011). However, this type of replacement was limited in extent because it did not fully remove the pyrite linings, and many valves at Po and Panzano were still buried at a sufficiently high rate relative to the timescale of pyrite oxidation so that a significant subset of pyrite-lined valves survived into the subsurface record. The conditions that ultimately allow the transit of reduced microenvironments formed by pyrite-lined shells at sites with relatively high background sedimentation rate into the subsurface stratigraphic record can occur when bioirrigation is slow or temporally impersistent. These conditions can occur when the recovery of infaunal communities in the wake of anoxic or hypoxic events (as in the northern Adriatic Sea) is slow or non-existent owing to hysteresis (when a community is pushed into an alternative stable state by hypoxia and remains in this state even when hypoxic conditions abate) (Bentley and Nittrouer, 1999; Solan et al., 2004; Elliott et al., 2007; Borja et al., 2010; Duarte et al., 2015).
Depending on the frequency and duration of hypoxic events or other disturbances limiting the recovery of benthic fauna, two preservation scenarios can be envisioned (Fig. 16). (i) If the frequency of hypoxic events is low and infaunal organisms both efficiently mixing and irrigating sediments rapidly recover, articulated shells will disarticulate and disintegrate when exposed to scavengers, borers, and degradation of organics in the TAZ. For example, maceration of the conchiolin layer triggers delamination of valves into inner and outer layers (Fig. 5e–h). Although a thick suboxic zone can develop under such conditions, the depth of the oxycline within the mixed layer will also increase (Fig. 16a). First, pyrite framboids will not nucleate on valves anymore if the labile biomass and microbes coating the decaying tissues were degraded during the earlier phase of aerobic decomposition. Second, although bacterial sulfate reduction in microenvironments surrounded by iron-dominated pore waters triggers initial formation of pyrite linings in some shells, oxidation induced by bioirrigation will catch up with pyrite-lined shells prior to their deep burial and thus inhibit their subsurface sequestration. (ii) If the frequency of hypoxic events is high relative to the recovery time of the burrowing community with efficient bioirrigators, the early recovery of deposit and detritus feeders that mix the uppermost sediments can support the formation of the ferruginous suboxic zone (Aller et al., 1986; van de Velde and Meysman, 2016), thus allowing the precipitation of pyrite framboids at the location of decaying molluscs. If subsequent recovery of bioirrigation-inducing burrowers is slow or interrupted by another hypoxic event or if communities with infrequent bioirrigators are locked by hysteresis effects (Kemp et al., 2009; Duarte et al., 2015), the oxycline can permanently remain close to the sediment–water interface (Fig. 16b), and some subset of pyrite-lined shells can remain preserved. These conditions with reduced bioirrigation are typical of eutrophied environments (Karlson et al., 2007; Lehtoranta et al., 2009). If the nutrient-fueled eutrophication or other sources of sediment organic enrichment lead to permanent anoxia of bottom waters, the concentrations of pyrite framboids within shells can be prohibited because mixing of sediments by burrowers that underlies the iron-based redox shuttle is aborted, and sulfide production by bacterial sulfate reduction in organic-rich sediments can exceed the availability of reactive iron oxides, with H2S diffusing away (Raiswell and Berner, 1985; Schenau et al., 2002; Raiswell et al., 2008; Farrell et al., 2009), or ferrous iron can be released from sediments to the non-sulfidic water column (Pakhomova et al., 2007). The absence of pyrite linings in anoxic sediments documented in the deep-time stratigraphic record (e.g., Brett et al., 1997) indicates that in marine environments with persistent bottom-water anoxia, the window for the early and rapid formation of pyrite linings (e.g., within shells of nektonic groups such as cephalopods that fell on the anoxic seafloor) will be closed when (a) the suboxic zone is not induced by biomixing and (b) organic matter degradation in surface sediments leads to the excess of hydrogen sulfide (Middelburg and Levin, 2009).
5.3 Temporal changes in bioirrigation generate stratigraphic trends in frequency of pyrite-lined valves
The upcore increase in the frequency of pyrite-lined valves at prodelta sites and the modality of whole-core age distributions of pyrite-lined valves hint to chronological changes in the preservation of pyrite linings. First, the stratigraphic increase in the frequency of pyrite-lined valves and the multivariate segregation in preservation of V. gibba valves between the early 20th century and the late 20th century increments at Po and Panzano indicate that O2 exposure of shells in the mixed layer was longer prior to and during the early than during the late 20th century. Any effects on early diagenetic pathways determined by changes in grain size can be excluded because sediment grain size remains constant downcore at Po and Panzano. Second, a general feature of the whole-core age distributions is the dominance of valves younger than 10 years, generated under active input of new dead shells into the mixed layer. Older modes in these distributions are indicative about temporal changes in conditions that favored or inhibited the preservation of pyrite linings. At Po, pyrite-lined valves show a secondary mode at ∼ 30–50 years that is formed by cohorts from the late 20th century, and most valves older than ∼ 100 years do not have pyrite linings (Fig. 10e–f). Similarly, at Panzano, pyrite-lined valves form a mode that is represented by cohorts from the late 20th century (Fig. 10g–h). Although paleoecological records of foraminifers and dinoflagellates indicate that eutrophication has affected the northern Adriatic Sea ecosystems since the 19th century (Barmawidjaja et al., 1995; Sangiorgi and Donders, 2004), a main shift in the composition of macrobenthic communities and size of the bivalve V. gibba occurs at the same stratigraphic levels where pyrite linings increase in frequency, i.e., at 80–90 cm at Po and at 12–20 cm Panzano (Fig. 15, Tomašových et al., 2018, 2020). These levels correspond to the mid-20th century at both prodeltas and coincide with an increase in nutrient load and with an increase in seasonal hypoxia and mucilage frequency in the northern Adriatic Sea (Marchetti et al., 1989; Justić, 1991). Ecological surveys performed in the late 20th century also indicate that a major shift in the composition of soft-bottom benthic communities (towards the dominance by V. gibba) in the NW Adriatic Sea took place in response to eutrophication and hypoxic events after the early 20th century (Crema et al., 1991). Two observations support the hypothesis that the stratigraphic shift towards higher pyrite frequency of pyrite-lined shells coincides with changes in the composition of macrobenthic communities towards states that still produced a well-mixed layer but were characterized by smaller bioirrigation efficiency in the late 20th century at the Po and Isonzo prodeltas. First, although the thickness of the mixed layer at the Po prodelta as estimated on the basis of sediment cores probably exceeded 20 cm prior to the late 20th century (Tomašových et al., 2018), abundant burrows of shrimps (Fig. 1d) and the 16–20 cm thick mixed layer at Po sites observed at the time of sampling in 2013 and 2014 indicate that local-scale biomixing remains active in the uppermost sediment zones. The thickness of the mixed layer documented here and by other studies (Frignani and Langone, 1991; Frignani et al., 2005; Alvisi et al., 2006, Alvisi, 2009) is typical of the mixed-layer thickness observed in other marine shelf environments (Moodley et al., 1998; Teal et al., 2010), and the depth of mixing is also not smaller than the mixed-layer thickness (< 5 cm) typical of persistently hypoxic environments on continental slopes (Meadows et al. 2000; Smith et al., 2000; Levin et al., 2003). Second, our inference about the role of inefficient bioirrigation in sequestration of pyrite linings in the subsurface stratigraphic record, as envisioned in the scenario in Fig. 16b, is supported by changes in the functional composition in benthic communities. At the Po and Isonzo prodeltas, the late 20th century infauna is dominated by shallow-burrowing deposit and detritus feeders that modify the uppermost centimeters of surface sediments, including Owenia fusiformis, Varicorbula gibba, or Ampelisca diadema (Occhipinti-Ambrogi et al., 2005; Solis-Weiss et al., 2007; N'Siala et al., 2008). These patterns differ from early 20th century ecological surveys (Vatova, 1949; Crema et al., 1991; Schinner, 1993; Schinner et al., 1997) and the early 20th century increments in cores (Gallmetzer et al., 2017; Tomašových et al., 2018) that indicate that pre-eutrophication benthic communities were dominated by biodiffusors with relatively high irrigation potential, such as Ova, Amphiura, or Turritella. The ophiuroid Amphiura filiformis extensively reworks and irrigates sediments (Solan and Kennedy 2002; Vopel et al., 2003), although predation pressure can reduce its irrigation effects (Wrede et al. 2017). The gastropod Turritella communis is not abundant at prodelta sites and tends to occur at deeper sites with slower sedimentation rates in the late 20th century surveys (Chiantore et al., 2001). In contrast to Amphiura, the ophiuroid Ophiura albida that is abundant at the Po sites belongs to the functional group of slow biodiffusors (Queirós et al., 2013).
The pyrite framboids lining intra-skeletal pores (originally filled with organic tissues) in well-preserved shells represent a unique indicator of slow, spatially and temporally limited irrigation. Such conditions can be produced by delayed recoveries from hypoxic events and/or by community states with low bioirrigation potential unable to recover anymore even when the frequency of hypoxic events returns to pre-impact levels (Steckbauer et al., 2011). These conditions can also characterize marine benthic ecosystems prior to the appearance of adaptations that allow deep bioirrigation or marine benthic ecosystems that were impoverished in functioning in the aftermath of mass extinctions. In permanently normoxic environments with intense bioturbation where most labile biomass degrades within the aerobic zone and any early pyrite is oxidized, the frequency of shells with shell-lined pyrite transferred into the permanent record will be negligible. This index can also be used to track the net O2 exposure of skeletal remains and recycling efficiency of iron and sulfides in the deep-time stratigraphic record because pyrite-lined shells represent a distinct taphonomic and diagenetic signature of fossil assemblages preserved in fine-grained sediments (Kobluk and Risk, 1977; Hudson, 1982; Bjerreskov, 1991; Underwood and Bottrell, 1994; Farrell et al., 2009; Brett et al., 2012a), especially in organisms with internal skeletal cavities that do not immediately open after their death (Hudson, 1982; Fisher, 1986; Loope and Watkins, 1989; Jin et al., 2007). On one hand, preservation of well-preserved, frequently articulated skeletal remains of organisms with otherwise fragile elements, coupled with pyrite linings, is a typical taphonomic feature of assemblages preserved in fine-grained sediments in Paleozoic (Brett et al., 2012a, b) or in Mesozoic successions (Hudson, 1982; Fernández-López et al., 2000; Paul et al., 2008; Reolid, 2014). On the other hand, actualistic studies assessing skeletal alteration of molluscs, brachiopods, or echinoderms rarely record this type of preservation in surface Holocene sediments (Staff and Powell, 1990; Kowalewski et al., 1994; Kidwell et al., 2005; Best et al., 2007). It is possible that the concentration of actualistic studies on the taphonomic processes in the uppermost, typically well-irrigated portions of the mixed layer and on environments with slow sedimentation rates underestimates this type of preservation. However, here, we suggest that prodelta sediments in the northern Adriatic Sea affected by the late 20th century eutrophication can represent analogue conditions that lead to preservation of well-preserved and pyrite-lined shells in the deep-time stratigraphic record. In contrast to obrution models invoking rapid burial to explain the initial sequestration of shells (so that they do not disarticulate and decay under reducing conditions), the pathway observed in prodelta sediments in the northern Adriatic Sea probably occurs without episodic burial of valves (by burrowers or by new sediment) because (1) very young pyrite-lined valves (< 10 years old) occur in the uppermost zones, (2) stochastic burial by burrowers would lead to deeper location of pyrite-lined valves and some differences in the depth of valves with and without pyrite, and (3) mixing smears out the depth location of shells after the deposition of thin flood layers, so that the depth of shell burial initiated by obrution does not remain constant. However, background net sedimentation rates need to be sufficiently high so that the time for burial of skeletal remains is shorter than the time to irrigate the mixed layer.
Preservation of pyrite-lined shells as a function of rapid and permanent sequestration of shells in pockets rich in dissolved iron is an indicator of inefficient bioirrigation at sites with high background sedimentation rates in the northern Adriatic Sea. Although sediment mixing affects the uppermost 10–20 cm of sediments in the northern Adriatic Sea, irrigation is reduced relative to pre-eutrophication community states. The preservation pathway that leads to primary pyrite linings and their long-term preservation is indicative of permanently limited depths of O2 penetration induced by bioirrigation that can be difficult to detect on the basis of trace fossils and ichnofabric only. Pyrite-lined valves thus represent a unique type of alteration that contrasts with other types of alteration (including the frequency of stained valves with nanopyritic inclusions) whose incidence increases with residence time in the TAZ. Our analyses indicate that obrution by episodic events is not necessary for preservation of well-preserved pyrite-lined valves and that the key factor is low bioirrigation, although still conditioned by relatively high background sedimentation rates that are typical of prodeltas. We suggest that the increase in the frequency of valves with pyrite below the mixed layer at 80–90 cm at the Po prodelta and at 12–20 cm at the Isonzo prodelta represents a temporal signal of the decline in the rate of bioirrigation in muddy sediments of the northern Adriatic Sea driven by a late 20th century increase in the frequency of hypoxia that delayed the recovery of infaunal communities. Although the rates of pyrite formation can also vary over long timescales owing to long-term changes in seawater chemistry (Leavitt et al., 2013; Algeo et al., 2015) and depend on the supply of organic matter and iron availability (Goldhaber et al., 1977; Berner and Raiswell, 1983; Berner, 1984; Berner and Westrich, 1985; Kershaw et al., 2018; Wignall et al., 2005; Bond and Wignall, 2010), we hypothesize that the frequency of pyrite-lined shells (belonging to organisms that inhabit oxic sediment zones) can improve inferences about irrigation efficiency of past benthic communities preserved in the fossil record.
The R language source code is available in the Supplement.
The dataset reported with scoring and age data of individual shells from two cores collected at Po, from Panzano, Piran, and Brijuni, is available in a tab-delimited txt file in the Supplement. This file is a data source for analyses shown in the R language code.
The supplement related to this article is available online at: https://doi.org/10.5194/bg-18-5929-2021-supplement.
AT designed the study. IG, AH, and MZ conducted sampling, and AT, IG, AH, and MB conducted taphonomic scoring. AT conducted analyses, and all authors contributed to writing and revisions.
The contact author has declared that neither they nor their co-authors have any competing interests.
Publisher’s note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
We thank Carlton Brett, Lidya Tarhan, and the anonymous reviewer for critical comments. This work was supported by the Austrian Science Fund (FWF) (grant no. P24901, 2013), by the Slovak Research and Development Agency (APVV 0555-17), and by the Slovak Scientific Grant Agency (VEGA 2/0169-19). Many thanks to the captain of the sampling vessel, Jernej Sedmak, for his commitment during the sampling campaigns in 2013 and 2014.
This research has been supported by the Austrian Science Fund (grant no. P24901), the Agentúra na Podporu Výskumu a Vývoja (grant no. APVV 17-0555), and the Ministerstvo školstva, vedy, výskumu a športu Slovenskej republiky (grant no. VEGA 2/0169/19).
This paper was edited by Aninda Mazumdar and reviewed by Lidya Tarhan, Carlton Brett, and one anonymous referee.
Ahmerkamp, S., Winter, C., Krämer, K., Beer, D. D., Janssen, F., Friedrich, J., Kuypers, M. M., and Holtappels, M.: Regulation of benthic oxygen fluxes in permeable sediments of the coastal ocean, Limnol. Oceanogr., 62, 1935–1954, 2017.
Algeo, T. J., Luo, G. M., Song, H. Y., Lyons, T. W., and Canfield, D. E.: Reconstruction of secular variation in seawater sulfate concentrations, Biogeosciences, 12, 2131–2151, https://doi.org/10.5194/bg-12-2131-2015, 2015.
Allen, R. E.: Role of diffusion–precipitation reactions in authigenic pyritization, Chem. Geol., 182, 461–472, 2002.
Allen, A. P., Kosnik, M. A., and Kaufman, D. S., 2013. Characterizing the dynamics of amino acid racemization using time-dependent reaction kinetics: a Bayesian approach to fitting age-calibration models, Quat. Geochronol., 18, 63–77, 2013.
Aller, R. C.: Carbonate dissolution in nearshore terrigenous muds: the role of physical and biological reworking, J. Geol., 90, 79–95, 1982.
Aller, R. C.: Bioturbation and remineralization of sedimentary organic matter: effects of redox oscillation, Chem. Geol., 114, 331–345, 1994.
Aller, R. C. and Cochran, J. K.: The critical role of bioturbation for particle dynamics, priming potential, and organic C remineralization in marine sediments: local and basin scales, Front. Earth Sci., 7, 157, https://doi.org/10.3389/feart.2019.00157, 2019.
Aller, R. C., Mackin, J. E., and Cox Jr, R. T.: Diagenesis of Fe and S in Amazon inner shelf muds: apparent dominance of Fe reduction and implications for the genesis of ironstones, Cont. Shelf Res., 6, 263–289, 1986.
Allison, P. A.: The role of anoxia in the decay and mineralization of proteinaceous macro-fossils, Paleobiology, 14, 139–154, 1988.
Alvisi, F.: A simplified approach to evaluate sedimentary organic matter fluxes and accumulation on the NW Adriatic Shelf (Italy), Chem. Ecol., 25, 119–134, 2009.
Alvisi, F. and Cozzi, S.: Seasonal dynamics and long-term trend of hypoxia in the coastal zone of Emilia Romagna (NW Adriatic Sea, Italy), Sci. Total Environ., 541, 1448–1462, 2016.
Alvisi, F., Frignani, M., Brunetti, M., Maugeri, M., Nanni, T., Albertazzi, S., and Ravaioli, M.: Climate vs. anthropogenic changes in North Adriatic shelf sediments influenced by freshwater runoff, Clim. Res., 31, 167–179, 2006.
Ambrogi, R., Bedulli, D., and Zurijni, G.: Spatial and temporal patterns in structure of macrobenthic assemblages. A three-year study in the northern Adriatic Sea in front of the Po River Delta, Mar. Ecol., 11, 25–41, 1990
Amorosi, A., Centineo, M. C., Dinelli, E., Lucchini, F., and Tateo, F.: Geochemical and mineralogical variations as indicators of provenance changes in Late Quaternary deposits of SE Po Plain, Sediment. Geol., 151, 273–292, 2002.
Anderson, E. P., Schiffbauer, J. D., and Xiao, S.: Taphonomic study of Ediacaran organic-walled fossils confirms the importance of clay minerals and pyrite in Burgess Shale – type preservation, Geology, 39, 643–646, 2011.
Andersson, J. H., Middelburg, J. J., and Soetaert, K.: Identifiability and uncertainty analysis of bio-irrigation rates, J. Mar. Res., 64, 407–429, 2006.
Arcon, I., Ogrinc, N., Kodre, A., and Faganeli, J.: EXAFS and XANES characterization of sedimentary iron in the Gulf of Trieste (N. Adriatic), J. Synchrotron Radiat., 6, 659–660, 1999.
Barbanti, A., Bergamini, M. C., Frascari, F., Miserocchi, S., Ratta, M., and Rosso, G.: Diagenetic processes and nutrient fluxes at the sediment-water interface, Northern Adriatic Sea, Italy, Mar. Freshwater Res., 46, 55–67, 1999.
Barmawidjaja, D. M., Van der Zwaan, G. J., Jorissen, F. J., and Puskaric, S.: 150 years of eutrophication in the northern Adriatic Sea: evidence from a benthic foraminiferal record, Mar. Geol., 122, 367–384, 1995.
Baucon, A., Bednarz, M., Dufour, S., Felletti, F., Malgesini, G., de Carvalho, C. N., Niklas, K. J., Wehrmann, A., Batstone, R., Bernardini, F., and Briguglio, A.: Ethology of the trace fossil Chondrites: form, function and environment, Earth-Sci. Rev., 202, 102989, https://doi.org/10.1016/j.earscirev.2019.102989, 2020.
Beam, J. P., Scott, J. J., McAllister, S. M., Chan, C. S., McManus, J., Meysman, F. J., and Emerson, D.: Biological rejuvenation of iron oxides in bioturbated marine sediments, ISME J., 12, 1389–1394, 2018.
Bentley, S. J. and Nittrouer, C. A.: Physical and biological influences on the formation of sedimentary fabric in an oxygen-restricted depositional environment; Eckernforde Bay, southwestern Baltic Sea, Palaios, 14, 585–600, 1999.
Berner, R. A.: Migration of iron and sulfur within anaerobic sediments during early diagenesis, Am. J. Sci., 267, 19–42, 1969.
Berner, R. A.: Sedimentary pyrite formation: an update, Geochim. Cosmochim. Ac., 48, 605–615, 1984.
Berner, R. A. and Raiswell, R.: Burial of organic carbon and pyrite sulfur in sediments over Phanerozoic time: a new theory, Geochim. Cosmochim. Ac., 47, 855–862, 1983.
Berner, R. A. and Westrich, J. T.: Bioturbation and the early diagenesis of carbon and sulfur, Am. J. Sci., 285, 193–206, 1985.
Bertics, V. J. and Ziebis, W.: Bioturbation and the role of microniches for sulfate reduction in coastal marine sediments, Environ. Microbiol., 12, 3022–3034, 2010.
Best, M. M. and Kidwell, S. M.: Bivalve taphonomy in tropical mixed siliciclastic-carbonate settings, I. Environmental variation in shell condition, Paleobiology, 26, 80–102, 2000.
Best, M. M., Ku, T. C., Kidwell, S. M., and Walter, L. M.: Carbonate preservation in shallow marine environments: unexpected role of tropical siliciclastics, J. Geol., 115, 437–456, 2007.
Bhattacharya, J. P., Howell, C. D., MacEachern, J. A., and Walsh, J. P.: Bioturbation, sedimentation rates, and preservation of flood events in deltas, Palaeogeogr. Palaeocl., 560, 110049, https://doi.org/10.1016/j.palaeo.2020.110049, 2020.
Bjerreskov, M.: Pyrite in Silurian graptolites from Bornholm, Denmark, Lethaia, 24, 351–361, 1991.
Boekschoten, G. J.: Shell borings of sessile epibiontic organisms as palaeoecological guides (with examples from the Dutch coast), Palaeogeogr. Palaeocl., 2, 333–379, 1966.
Bond, D. P. and Wignall, P. B.: Pyrite framboid study of marine Permian–Triassic boundary sections: a complex anoxic event and its relationship to contemporaneous mass extinction, Geol. Soc. Am. Bull., 122, 1265–1279, 2010.
Boyle, R. A., Dahl, T. W., Dale, A. W., Shields-Zhou, G. A., Zhu, M. Y., Brasier, M. D., Canfield, D. E., and Lenton, T. M.: Stabilization of the coupled oxygen and phosphorus cycles by the evolution of bioturbation, Nat. Geosci., 7, 671–676, 2014.
Borja, A., Franco, J., and Perez, V.: A marine biotic index to establish the ecological quality of soft-bottom benthos within European estuarine and coastal environments, Mar. Pollut. Bull., 40, 1100–1114, 2000.
Borja, Á., Dauer, D. M., Elliott, M., and Simenstad, C. A.: Medium-and long-term recovery of estuarine and coastal ecosystems: patterns, rates and restoration effectiveness, Estuar. Coast., 33, 1249–1260, 2010.
Boldrin, A., Carniel, S., Giani, M., Marini, M., Aubry, F. B., Campanelli, A., Grilli, F., and Russo, A.: Effects of bora wind on physical and biogeochemical properties of stratified waters in the northern Adriatic, J. Geophys. Res.-Ocean., 114, C08S92, https://doi.org/10.1029/2008JC004837, 2009.
Borkow, P. S. and Babcock, L. E.: Turning pyrite concretions outside-in: role of biofilms in pyritization of fossils, Sedim. Record, 1, 4–7, 2003.
Brand, U. and Morrison, J. O.: Diagenesis and pyritization of crinoid ossicles, Can. J. Earth Sci., 24, 2486–2498, 1987.
Brett, C. E., Dick V. B., and Baird, G. C: Comparative taphonomy and paleoecology of Middle Devonian dark gray and black shale facies from western New York, edited by: Landing, E. and Brett, C. E., Dynamic stratigraphy and depositional environments of the Hamilton Group (Middle Devonian) in New York State, Part II, New York State Museum/Geological Survey, 5–36, 1991.
Brett, C. E., Baird, G. C., and Speyer, S. E.: Fossil lagerstatten: Stratigraphic record of paleontological and taphonomic events, in: Paleontological events: Stratigraphic, ecological, and evolutionary implications, edited by: Brett, C. E. and Baird, G. C., Columbia University Press, New York, 3–40, 1997.
Brett, C. E., Zambito IV, J. J., Hunda, B. R., and Schindler, E.: Mid-Paleozoic trilobite Lagerstätten: Models of diagenetically enhanced obrution deposits, Palaios, 27, 326–345, 2012a.
Brett, C. E., Zambito IV, J. J., Schindler, E., and Becker, R. T.: Diagenetically-enhanced trilobite obrution deposits in concretionary limestones: The paradox of “rhythmic events beds”, Palaeogeogr. Palaeocl., 367, 30–43, 2012b.
Briggs, D. E. G., Bottrell, S. H., and Raiswell, R.: Pyritization of soft-bodied fossils: Beecher's Trilobite Bed, Upper Ordovician, New York, Geology, 19, 1221–1224, 1991.
Briggs, D. E. G., Raiswell, R., Bottrell, S. H., Hatfield, D., and Bartels, C.: Controls on the pyritization of exceptionally preserved fossils: an analysis of the Lower Devonian Hunsrück Slate of Germany, Am. J. Sci., 296, 633–663, 1996.
Bromley, R. G. and Ekdale, A. A.: Composite ichnofabrics and tiering of burrows, Geol. Mag., 123, 59–65, 1986.
Brown, P. R.: Pyritization in some molluscan shells, J. Sediment. Res., 36, 1149–1152, 1996.
Brush, M. J., Giani, M., Totti, C., Testa, J. M., Faganeli, J., Ogrinc, N., Kemp, W. M., and Umani, S.F.. Eutrophication, Harmful Algae, Oxygen Depletion, and Acidification. Coastal Ecosystems in Transition: A Comparative Analysis of the Northern Adriatic and Chesapeake Bay, 75–104, 2021.
Borger, E. D., Tiano, J., Braeckman, U., Ysebaert, T., and Soetaert, K.: Biological and biogeochemical methods for estimating bioirrigation: a case study in the Oosterschelde estuary, Biogeosciences, 17, 1701–1715, https://doi.org/10.5194/bg-17-1701-2020, 2020.
Buatois, L. A. and Mángano, M. G.: The déjà vu effect: Recurrent patterns in exploitation of ecospace, establishment of the mixed layer, and distribution of matgrounds, Geology, 39, 1163–1166, 2011.
Buatois, L. A., Mángano, M. G., Minter, N. J., Zhou, K., Wisshak, M., Wilson, M. A., and Olea, R. A.: Quantifying ecospace utilization and ecosystem engineering during the early Phanerozoic – The role of bioturbation and bioerosion, Sci. Adv., 6, eabb0618, https://doi.org/10.1126/sciadv.abb0618, 2020.
Cai, W. J., Chen, F., Powell, E. N., Walker, S. E., Parsons-Hubbard, K. M., Staff, G. M., Wang, Y., Ashton-Alcox, K. A., Callender, W. R., and Brett, C. E.: Preferential dissolution of carbonate shells driven by petroleum seep activity in the Gulf of Mexico, Earth Planet. Sc. Lett., 248, 227–243, 2006.
Cai, Y., Schiffbauer, J. D., Hua, H., and, Xiao, S.: Preservational modes in the Ediacaran Gaojiashan Lagerstätte: pyritization, aluminosilicification, and carbonaceous compression, Palaeogeogr. Palaeocl., 326–328, 109–117, 2012.
Canfield, D. E. and Farquhar, J.: Animal evolution, bioturbation, and the sulfate concentration of the oceans, P. Natl. Acad. Sci. USA, 106, 8123–8127, 2009.
Canfield, D. E., Thamdrup, B., and Hansen, J. W.: The anaerobic degradation of organic matter in Danish coastal sediments: iron reduction, manganese reduction, and sulfate reduction, Geochim. Cosmochim. Ac., 57, 3867–3883, 1993.
Carstensen, J., Conley, D.J., Bonsdorff, E., Gustafsson, B. G., Hietanen, S., Janas, U., Jilbert, T., Maximov, A., Norkko, A., Norkko, J., and Reed, D. C.: Hypoxia in the Baltic Sea: Biogeochemical cycles, benthic fauna, and management, AMBIO, 43, 26–36, 2014.
Cermelj, B., Ogrinc, N., and Faganeli, J.: Anoxic mineralization of biogenic debris in near-shore marine sediments (Gulf of Trieste, northern Adriatic), Sci. Total. Environ., 266, 143–152, 2001.
Chiantore, M., Bedulli, D., Cattaneo-Vietti, R., Schiaparelli, S., and Albertelli, G: Long-term changes in the Mollusc–Echinoderm assemblages in the north and coastal middle Adriatic Sea, Atti Assoc. It. Oceanol. Limnol., 14, 63–75, 2001.
Christensen, A. M.: Feeding biology of the sea star Astropecten irregularis Pennant, Ophelia, 8, 1–134, 1970.
Christensen, B., Vedel, A., and Kristensen, E.: Carbon and nitrogen fluxes in sediment inhabited by suspension-feeding (Nereis diversicolor) and non-suspension-feeding (N. virens) polychaetes, Mar. Ecol. Prog. Ser., 192, 203–217, 2000.
Cozzi, S., Ivančić, I., Catalano, G., Djakovac, T., and Degobbis, D.: Dynamics of the oceanographic properties during mucilage appearance in the Northern Adriatic Sea: analysis of the 1997 event in comparison to earlier events, J. Marine Syst., 50, 223–241, 2004.
Crema, R., Castelli, A., and Prevedelli, D. Long term eutrophication effects on macrofaunal communities in northern Adriatic Sea, Mar. Pollut. Bull., 22, 503–508, 1991.
Davies, D. J., Powell, E. N., and Stanton Jr, R. J.: Relative rates of shell dissolution and net sediment accumulation-a commentary: can shell beds form by the gradual accumulation of biogenic debris on the sea floor?, Lethaia, 22, 207–212, 1989.
Degobbis, D., Precali, R., Ivancic, I., Smodlaka, N., Fuks, D., and Kveder, S.: Long-term changes in the northern Adriatic ecosystem related to anthropogenic eutrophication, Int. J. Environ. Pollut., 13, 495–533, 2000.
Dhakar, S. P. and Burdige, D. J.: A coupled, non-linear, steady state model for early diagenetic processes in pelagic sediments, Am. J. Sci., 296, 296–330, 1996.
Djakovac, T., Degobbis, D., Supić, N., and Precali, R.: Marked reduction of eutrophication pressure in the northeastern Adriatic in the period 2000–2009, Estuar, Coast. Shelf Sci., 115, 25–32, 2012.
Djakovac, T., Supić, N., Aubry, F. B., Degobbis, D., and Giani, M.: Mechanisms of hypoxia frequency changes in the northern Adriatic Sea during the period 1972–2012, J. Marine Syst., 141, 179–189, 2015.
Dolenec, T., Faganeli, J., and Pirc, S.: Major, minor and trace elements in surficial sediments from the open Adriatic Sea: a regional geochemical study, Geol. Croat., 51, 59–73, 1998.
Droser, M. L. and Bottjer, D. J.: Trends in depth and extent of bioturbation in Cambrian carbonate marine environments, western United States, Geology, 16, 233–236, 1988.
Droser, M. L., Jensen, S., and Gehling, J. G.: Trace fossils and substrates of the terminal Proterozoic–Cambrian transition: implications for the record of early bilaterians and sediment mixing, P. Natl. Acad. Sci. USA, 99, 12572–12576, 2002.
Duarte, C. M., Borja, A., Carstensen, J., Elliott, M., Krause-Jensen, D., and Marbà, N.: Paradigms in the recovery of estuarine and coastal ecosystems, Estuar. Coast., 38, 1202–1212, 2015.
Elliott, M., Burdon, D., Hemingway, K. L., and Apitz, S. E.: Estuarine, coastal and marine ecosystem restoration: confusing management and science – a revision of concepts, Estuar. Coast. Shelf S., 74, 349–366, 2007.
Emery, K. O. and Rittenberg, S. C.: Early diagenesis of California basin sediments in relation to origin of oil, AAPG Bull., 36, 735–806, 1952.
Epping, E. H. and Helder, W.: Oxygen budgets calculated fromin situ oxygen microprofiles for Northern Adriatic sediments, Cont. Shelf Res., 17, 1737–1764, 1997.
Faganeli, J. and Ogrinc, N.: Oxic–anoxic transition of benthic fluxes from the coastal marine environment (Gulf of Trieste, northern Adriatic Sea), Mar. Freshwater Res., 60, 700–711, 2009.
Faganeli, J., Avčin, A., Fanuko, N., Malej, A., Turk, V., Tušnik, P., Vrišer, B., and Vukovič, A.: Bottom layer anoxia in the central part of the Gulf of Trieste in the late summer of 1983, Mar. Pollut. Bull., 16, 75–78, 1985.
Faganeli, J., Planinc, R., Smodiš, B., Stegnar, P., and Ogorelec, B.: Marine geology of the Gulf of Trieste (northern Adriatic): geochemical aspects, Mar. Geol., 99, 93–108, 1991.
Faganeli, J., Pezdic, J., Ogorelec, B., Misic, M., and Najdek, M.: The origin of sedimentary organic matter in the Adriatic, Cont. Shelf Res., 14, 365–384, 1994.
Faresi, L., Bettoso, N., and Aleffi, I. F.: Vertical distribution of soft bottom macrozoobenthos in the Gulf of Trieste (Northern Adriatic Sea), Ann. Ser. Hist. Natur., 22, 123–132, 2012.
Farrell, Ú. C., Martin, M. J., Hagadorn, J. W., Whiteley, T., and Briggs, D. E.: Beyond Beecher's Trilobite Bed: Widespread pyritization of soft tissues in the Late Ordovician Taconic foreland basin, Geology, 37, 907–910, 2009.
Fedra, K., Ölscher, E. M., Scherübel, C., Stachowitsch, M., and Wurzian, R. S.: On the ecology of a North Adriatic benthic community: distribution, standing crop and composition of the macrobenthos, Mar. Biol., 38, 129–145, 1976.
Fernández-López, S. R., Duarte, L. V., and Henriques, M. H. P.: Ammonites from lumpy limestones (Lower Pliensbachian, Portugal). Taphonomic analysis and palaeoenvironmental implications, Rev. Soc. Geol. España, 13, 3–15, 2000.
Fisher, I. S. J.: Pyrite replacement of mollusc shells from the Lower Oxford Clay (Jurassic) of England, Sedimentology, 33, 575–585, 1986.
Fisher, I. S. J. and Hudson, J. D.: Pyrite formation in Jurassic shales of contrasting biofacies, Geol. Soc. Spec. Publ., 26, 69–78, 1987.
Frignani, M. and Langone, L.: Accumulation rates and 137Cs distribution in sediments off the Po River delta and the Emilia-Romagna coast (northwestern Adriatic Sea, Italy), Cont. Shelf Res., 11, 525–542, 1991.
Frignani, M., Langone, L., Ravaioli, M., Sorgente, D., Alvisi, F., and Albertazzi, S.: Fine-sediment mass balance in the western Adriatic continental shelf over a century time scale, Mar. Geol., 222, 113–133, 2005.
Gabbott, S. E., Xian-Guang, H., Norry, M. J., and Siveter, D. J.: Preservation of Early Cambrian animals of the Chengjiang biota, Geology, 32, 901–904, 2004.
Gaines, R. R., Briggs, D. E., and Yuanlong, Z.: Cambrian Burgess Shale–type deposits share a common mode of fossilization, Geology, 36, 755–758, 2008.
Gallmetzer, I., Haselmair, A., Stachowitsch, M., and Zuschin, M.: An innovative piston corer for large-volume sediment samples, Limnol. Oceanogr. Method., 14, 698–717, 2016.
Gallmetzer, I., Haselmair, A., Tomašových, A., Stachowitsch, M., and Zuschin, M.: Responses of molluscan communities to centuries of human impact in the northern Adriatic Sea, PLoS One, 12, e0180820, https://doi.org/10.1371/journal.pone.0180820, 2017.
Gehling, J. G.: Microbial mats in terminal Proterozoic siliciclastics; Ediacaran death masks, Palaios, 14, 40–57, 1999.
Germano, J. D., Valente, R. M., Carey, D. A., and Solan, M.: The use of Sediment Profile Imaging (SPI) for environmental impact assessments and monitoring studies: lessons learned from the past four decades, Oceanogr. Mar. Biol. An Ann. Rev., 49, 235–298, 2011.
Gerwing, T. G., Cox, K., Gerwing, A. M. A., Carr-Harris, C. N., Dudas, S. E., and Juanes, F.: Depth to the apparent redox potential discontinuity (aRPD) as a parameter of interest in marine benthic habitat quality models, Int. J. Sediment. Res., 33, 149–156, 2018.
Giani, M., Savelli, F., Berto, D., Zangrando, V., Ćosović, B., and Vojvodić, V.: Temporal dynamics of dissolved and particulate organic carbon in the northern Adriatic Sea in relation to the mucilage events, Sci. Total. Environ., 353, 126–138, 2005.
Gibson, B. M., Schiffbauer, J. D., and Darroch, S. A.: Ediacaran-style decay experiments using mollusks and sea anemones, Palaios, 33, 185–203, 2018.
Gingras, M. K., Pemberton, S. G., Dashtgard, S., and Dafoe, L.: How fast do marine invertebrates burrow?, Palaeogeogr. Palaeocl., 270, 280–286, 2008.
Gingras, M. K., Zonneveld, J. P., and Konhauser, K. O.: Using X-ray radiography to observe Fe distributions in bioturbated sediment, in: Experimental Approaches to Understanding Fossil Organisms, edited by: Hembree, D. I., Platt, B. F., and Smith, J. J., Springer, Dordrecht, 195–206, 2014.
Giordani, P., Hammond, D. E., Berelson, W. M., Montanari, G., Poletti, R., Milandri, A., Frignani, M., Langone, L., Ravaioli, M., Rovatti, G., and Rabbi, E.: Benthic fluxes and nutrient budgets for sediments in the Northern Adriatic Sea: burial and recycling efficiencies, in: Marine Coastal Eutrophication, edited by: Vollenweider, R. A., Marchetti, R., and Viviani, R., Elsevier, 251–275, 1992.
Giordani, P., Helder, W., Koning, E., Miserocchi, S., Danovaro, R., and Malaguti, A.: Gradients of benthic–pelagic coupling and carbon budgets in the Adriatic and Northern Ionian Sea, J. Marine Syst., 33, 365–387, 2002.
Goldhaber, M. B., Aller, R. C., Cochran, J. K., Rosenfeld, J. K., Martens, C. S., and Berner, R. A.: Sulfate reduction, diffusion, and bioturbation in Long Island Sound sediments; report of the FOAM Group, Am. J. Sci., 277, 193–237, 1977.
Gougeon, R. C., Mángano, M. G., Buatois, L. A., Narbonne, G. M., and Laing, B. A.: Early Cambrian origin of the shelf sediment mixed layer, Nat. Commun., 9, 1–7, 2018.
Hansen, K., King, G. M., and Kristensen, E.: Impact of the soft-shell clam Mya arenaria on sulfate reduction in an intertidal sediment, Aquat. Microb. Ecol., 10, 181–194, 1996.
Harazim, D., McIlroy, D., Edwards, N. P., Wogelius, R. A., Manning, P. L., Poduska, K. M., Layne, G. D., Sokaras, D., Alonso-Mori, R., and Bergmann, U.: Bioturbating animals control the mobility of redox-sensitive trace elements in organic-rich mudstone, Geology, 43, 1007–1010, 2015.
Hartnett, H. E., Keil, R. G., Hedges, J. I., and Devol, A. H.: Influence of oxygen exposure time on organic carbon preservation in continental margin sediments, Nature, 391, 572–575, 1998.
Haselmair, A., Gallmetzer, I., Tomašových, A., Wieser, A. M., Übelhör, A., and Zuschin, M.: Basin-wide infaunalisation of benthic soft-bottom communities driven by anthropogenic habitat degradation in the northern Adriatic Sea, Mar. Ecol. Prog. Ser., 671, 45–65, 2021.
Hammond, D. E., Giordani, P., Berelson, W. M., and Poletti, R.: Diagenesis of carbon and nutrients and benthic exchange in sediments of the Northern Adriatic Sea, Mar. Chem., 66, 53–79, 1999.
Herndl, G. J., Faganeli, J., Fanuko, N., Peduzzi, P., and Turk, V.: Role of bacteria in the carbon and nitrogen flow between water-column and sediment in a shallow marine bay (Bay of Piran, Northern Adriatic Sea), Mar. Ecol., 8, 221–236, 1987.
Herndl, G. J., Peduzzi, P., and Fanuko, N.: Benthic community metabolism and microbial dynamics in the Gulf of Trieste (Northern Adriatic Sea), Mar. Ecol. Prog. Ser., 53, 169–178, 1989.
Hines, M. E., Faganeli, J., and Planinc, R.: Sedimentary anaerobic microbial biogeochemistry in the Gulf of Trieste, northern Adriatic Sea: influences of bottom water oxygen depletion, Biogeochemistry, 39, 65–86, 1997.
Holmes, S. P. and Miller, N.: Aspects of the ecology and population genetics of the bivalve Corbula gibba, Mar. Ecol. Prog. Ser., 315, 129–140, 2006.
Hrs-Brenko, M.: The role of bivalve Corbula gibba (Olivi, 1792) (Corbulidae, Mollusca Bivalvia) in the recruitment of benthic communities in the Northern Adriatic, Pomorski zbornik, 41, 195–208, 2003.
Hrs-Brenko M.: The basket shell, Corbula gibba Olivi, 1792 (Bivalve Mollusks) as a species resistant to environmental disturbances: A review, Acta Adriat., 47, 49–64, 2006.
Hu, X., Cai, W. J., Wang, Y., Guo, X., and Luo, S.: Geochemical environments of continental shelf-upper slope sediments in the northern Gulf of Mexico, Palaeogeogr. Palaeocl., 312, 265–277, 2011.
Hudson, J. D.: Pyrite in ammonite-bearing shales from the Jurassic of England and Germany, Sedimentology, 29, 639–667, 1982.
Hunda, B. R., Hughes, N. C., and Flessa, K. W.: Trilobite taphonomy and temporal resolution in the Mt. Orab shale bed (Upper Ordovician, Ohio, USA), Palaios, 21, 26–45, 2006.
Jerolmack, D. J. and Sadler, P.: Transience and persistence in the depositional record of continental margins, J. Geophys. Res.-Earth, 112, JF000555, https://doi.org/10.1029/2006JF000555, 2007.
Jin, J., Zhan, R., Copper, P., and Caldwell, W. G. E.: Epipunctae and phosphatized setae in Late Ordovician plaesiomyid brachiopods from Anticosti Island, eastern Canada, J. Paleontol., 81, 666–683, 2007.
Johannessen, S. C. and Macdonald, R. W.: There is no 1954 in that core! Interpreting sedimentation rates and contaminant trends in marine sediment cores, Mar. Pollut. Bull., 64, 675–678, 2012.
Jokinen, S. A., Virtasalo, J. J., Jilbert, T., Kaiser, J., Dellwig, O., Arz, H. W., Hänninen, J., Arppe, L., Collander, M., and Saarinen, T.: A 1500-year multiproxy record of coastal hypoxia from the northern Baltic Sea indicates unprecedented deoxygenation over the 20th century, Biogeosciences, 15, 3975–4001, https://doi.org/10.5194/bg-15-3975-2018, 2018.
Jørgensen, B. B.: Bacterial sulfate reduction within reduced microniches of oxidized marine sediments, Mar. Biol., 41, 7–17, 1977.
Justić, D.: Hypoxic conditions in the northern Adriatic Sea: historical development and ecological significance, Geol. Soc. Spec. Publ., 58, 95–105, 1991.
Kardon, G.: Evidence from the fossil record of an antipredatory exaptation: conchiolin layers in corbulid bivalves, Evolution, 52, 68–79, 1998.
Karlson, K., Bonsdorff, E., and Rosenberg, R.: The impact of benthic macrofauna for nutrient fluxes from Baltic Sea sediments, AMBIO, 36, 161–167, 2007.
Kaufman, D. S. and Manley, W. F.: A new procedure for determining DL amino acid ratios in fossils using reverse phase liquid chromatography, Quaternary Sci. Rev., 17, 987–1000, 1998.
Kędzierski, M., Uchman, A., Sawlowicz, Z., and Briguglio, A.: Fossilized bioelectric wire – the trace fossil Trichichnus, Biogeosciences, 12, 2301–2309, https://doi.org/10.5194/bg-12-2301-2015, 2015.
Kemp, W. M., Faganeli, J., Puskaric, S., Smith, E. M., and Boynton, W. R.: Pelagic-benthic coupling and nutrient cycling. Ecosystems at the land-sea margin: Drainage basin to coastal sea, Estuar. Coast. Shelf S., 55, 295–340, 1999.
Kemp, W. M., Testa, J. M., Conley, D. J., Gilbert, D., and Hagy, J. D.: Temporal responses of coastal hypoxia to nutrient loading and physical controls, Biogeosciences, 6, 2985–3008, https://doi.org/10.5194/bg-6-2985-2009, 2009.
Kershaw, S., Tang, H., Li, Y., and Guo, L.: Oxygenation in carbonate microbialites and associated facies after the end-Permian mass extinction: Problems and potential solutions, J. Palaeogeogr., 7, 32–47, 2018.
Kidwell, S. M., Best, M. M., and Kaufman, D. S.: Taphonomic trade-offs in tropical marine death assemblages: Differential time averaging, shell loss, and probable bias in siliciclastic vs. carbonate facies, Geology, 33, 729–732, 2005.
Kobluk, D. R. and Risk, M. J.: Algal borings and framboidal pyrite in Upper Ordovician brachiopods, Lethaia, 10, 135–143, 1977.
Kosnik, M. A., Kaufman, D. S., and Hua, Q.: Identifying outliers and assessing the accuracy of amino acid racemization measurements for geochronology: I. Age calibration curves, Quat. Geochronol., 3, 308–327, 2008.
Kowalewski, M., Flessa, K. W., and Aggen, J. A.: Taphofacies analysis of Recent shelly cheniers (beach ridges), northeastern Baja California, Mexico. Facies, 31, 209–242, 1994.
Kralj, M., Lipizer, M., Čermelj, B., Celio, M., Fabbro, C., Brunetti, F., Francé, J., Mozetič, P., and Giani, M.: Hypoxia and dissolved oxygen trends in the northeastern Adriatic Sea (Gulf of Trieste), Deep-Sea Res. Pt. II, 164, 74–88, 2019.
Krampitz, G., Drolshagen, H., and Hotta, S.: Simultaneous binding of calcium and bicarbonate by conchiolin of oyster shells, Experientia, 39, 1104–1105, 1983.
Kristensen, E., Penha-Lopes, G., Delefosse, M., Valdemarsen, T., Quintana, C. O., and Banta, G. T.: What is bioturbation? The need for a precise definition for fauna in aquatic sciences, Mar. Ecol. Prog. Ser., 446, 285–302, 2012.
Kristensen, E., Delefosse, M., Quintana, C. O., Flindt, M. R., and Valdemarsen, T.: Influence of benthic macrofauna community shifts on ecosystem functioning in shallow estuaries, Front. Mar. Sci., 1, 00041, https://doi.org/10.3389/fmars.2014.00041, 2014.
Kristensen, E., Røy, H., Debrabant, K., and Valdemarsen, T.: Carbon oxidation and bioirrigation in sediments along a Skagerrak-Kattegat-Belt Sea depth transect, Mar. Ecol. Prog. Ser., 604, 33–50, 2018.
Leavitt, W. D., Halevy, I., Bradley, A. S., and Johnston, D. T.: Influence of sulfate reduction rates on the Phanerozoic sulfur isotope record, P. Natl. Acad. Sci. USA, 110, 11244–11249, 2013.
Lehto, N., Glud, R.N., á Norði, G., Zhang, H., and Davison, W.: Anoxic microniches in marine sediments induced by aggregate settlement: biogeochemical dynamics and implications, Biogeochemistry, 119, 307–327, 2014.
Lehtoranta, J., Ekholm, P., and Pitkänen, H.: Coastal eutrophication thresholds: a matter of sediment microbial processes, AMBIO, 38, 303–308, 2009.
Lenstra, W. K., Hermans, M., Séguret, M. J., Witbaard, R., Behrends, T., Dijkstra, N., van Helmond, N. A., Kraal, P., Laan, P., Rijkenberg, M. J., and Severmann, S.: The shelf-to-basin iron shuttle in the Black Sea revisited, Chem. Geol., 511, 314–341, 2019.
Levin, L. A., Rathburn, A. E., Gutiérrez, D., Muñoz, P., and Shankle, A.: Bioturbation by symbiont-bearing annelids in near-anoxic sediments: implications for biofacies models and paleo-oxygen assessments, Palaeogeogr. Palaeocl., 199, 129–140, 2003.
Lewy, Z. and Samtleben, C.: Functional morphology and palaeontological significance of the conchiolin layers in corbulid pelecypods, Lethaia, 12, 341–351, 1979.
Liu, A. G., McMahon, S., Matthews, J. J., Still, J. W., and Brasier, A. T.: Petrological evidence supports the death mask model for the preservation of Ediacaran soft-bodied organisms in South Australia, Geology, 47, 215–218, 2019.
Lohrer, A. M., Thrush, S. F., and Gibbs, M. M.: Bioturbators enhance ecosystem function through complex biogeochemical interactions, Nature, 431, 1092–1095, 2004.
Loope, D. B. and Watkins, D. K.: Pennsylvanian fossils replaced by red chert; early oxidation of pyritic precursors, J. Sediment. Res., 59, 375–386, 1989.
MacEachern, J. A., Bann, K. L., Bhattacharya, J. P., and Howell Jr., C. D.: Ichnology of deltas, in: River Deltas: Concepts, Models, and Examples, edited by: Giosan, L. and Bhattacharya, J. P., SEPM Society for Sedimentary Geology, Tulsa, 49–85, 2005.
Machain-Castillo, M. L., Ruiz-Fernández, A. C., Gracia, A., Sanchez-Cabeza, J. A., Rodríguez-Ramírez, A., Alexander-Valdés, H. M., Pérez-Bernal, L. H., Nava-Fernández, X. A., Gómez-Lizárraga, L. E., Almaraz-Ruiz, L., and Schwing, P. T.: Natural and anthropogenic oil impacts on benthic foraminifera in the southern Gulf of Mexico, Mar. Environ. Res., 149, 111–125, 2019.
Maire, O., Lecroart, P., Meysman, F., Rosenberg, R., Duchêne, J. C., and Grémare, A.: Quantification of sediment reworking rates in bioturbation research: a review, Aquat. Biol., 2, 219–238, 2008.
Manini, E., Fabiano, M., and Danovaro, R.: Benthic response to mucilaginous aggregates in the northern Adriatic Sea: biochemical indicators of eutrophication, Chem. Ecol., 17, 171–179, 2000.
Marchetti, R., Provini, A., and Crosa, G.: Nutrient load carried by the River Po into the Adriatic Sea, 1968–1987, Mar. Pollut. Bull, 20, 168–172, 1989.
Mautner, A. K., Gallmetzer, I., Haselmair, A., Schnedl, S. M., Tomašových, A., and Zuschin, M.: Holocene ecosystem shifts and human-induced loss of Arca and Ostrea shell beds in the north-eastern Adriatic Sea, Mar. Pollut. Bull., 126, 19–30, 2018.
Meadows, A., Meadows, P. S., West, F. J. and Murray, J. M.: Bioturbation, geochemistry and geotechnics of sediments affected by the oxygen minimum zone on the Oman continental slope and abyssal plain, Arabian Sea, Deep-Sea Res. Pt. II, 47, 259–280, 2000.
Meile, C. and Van Cappellen, P.: Particle age distributions and O2 exposure times: timescales in bioturbated sediments, Global Biochem. Cy., 19, GB3013, https://doi.org/10.1029/2004GB002371, 2005.
Mermillod-Blondin, F. and Rosenberg, R.: Ecosystem engineering: the impact of bioturbation on biogeochemical processes in marine and freshwater benthic habitats, Aquat. Sci., 68, 434–442, 2006.
Mermillod-Blondin, F.: The functional significance of bioturbation and biodeposition on biogeochemical processes at the water–sediment interface in freshwater and marine ecosystems, J. N. Am. Benthol. Soc., 30, 770–778, 2011.
Meysman, F. J., Boudreau, B. P., and Middelburg, J. J.: Relations between local, nonlocal, discrete and continuous models of bioturbation, J. Mar. Res., 61, 391–410, 2003.
Meysman, F. J., Galaktionov, O. S., Gribsholt, B., and Middelburg, J. J.: Bioirrigation in permeable sediments: Advective pore-water transport induced by burrow ventilation, Limnol. Oceanogr., 51, 142–156, 2006.
Michaud, E., Desrosiers, G., Mermillod-Blondin, F., Sundby, B., and Stora, G.: The functional group approach to bioturbation: II. The effects of the Macoma balthica community on fluxes of nutrients and dissolved organic carbon across the sediment–water interface, J. Exp. Mar. Biol. Ecol., 337, 178–189, 2006.
Middelburg, J. J. and Levin, L. A.: Coastal hypoxia and sediment biogeochemistry, Biogeosciences, 6, 1273–1293, https://doi.org/10.5194/bg-6-1273-2009, 2009.
Moodley, L., Heip, C. H., and Middelburg, J. J.: Benthic activity in sediments of the northwestern Adriatic Sea: sediment oxygen consumption, macro-and meiofauna dynamics, J. Sea Res., 40, 263–280, 1998.
Moodley, L., Chen, G., Heip, C., and Vincx, M.: Vertical distribution of meiofauna in sediments from contrasting sites in the Adriatic Sea: clues to the role of abiotic versus biotic control, Ophelia, 53, 203–212, 2000.
Moraitis, M. L., Tsikopoulou, I., Geropoulos, A., Dimitriou, P. D., Papageorgiou, N., Giannoulaki, M., Valavanis, V. D., and Karakassis, I.: Molluscan indicator species and their potential use in ecological status assessment using species distribution modeling, Mar. Environ. Res., 140, 10–17, 2018.
Mozetič, P., Solidoro, C., Cossarini, G., Socal, G., Precali, R., Francé, J., Bianchi, F., De Vittor, C., Smodlaka, N., and Umani, S. F.: Recent trends towards oligotrophication of the northern Adriatic: evidence from chlorophyll a time series, Estuar. Coast., 33, 362–375, 2010.
Nebelsick, J. H., Schmid, B., and Stachowitsch, M.: The encrustation of fossil and recent sea-urchin tests: ecological and taphonomic significance, Lethaia, 30, 271–284, 1997.
Nerlović, V., Doğan, A., and Hrs-Brenko, M.: Response to oxygen deficiency (depletion): Bivalve assemblages as an indicator of ecosystem instability in the northern Adriatic Sea, Biologia, 66, 1114–1126, 2011.
Nilsson, H. C. and Rosenberg, R.: Succession in marine benthic habitats and fauna in response to oxygen deficiency: analysed by sediment profile-imaging and by grab samples, Mar. Ecol. Prog. Ser., 197, 139–149, 2000.
Norkko, A., Villnäs, A., Norkko, J., Valanko, S., and Pilditch, C.: Size matters: implications of the loss of large individuals for ecosystem function, Sci. Rep., 3, 1–7, 2013.
Novek, J. M., Dornbos, S. Q., and McHenry, L. J.: Palaeoredox geochemistry and bioturbation levels of the exceptionally preserved early Cambrian Indian Springs biota, Nevada, USA, Lethaia, 49, 604–616, 2016.
N'Siala, G. M., Grandi, V., Iotti, M., Montanari, G., Prevedelli, D., and Simonini, R.: Responses of a northern Adriatic Ampelisca–Corbula community to seasonality and short-term hydrological changes in the Po river, Mar. Environ. Res., 66, 466–476, 2008.
Occhipinti-Ambrogi, A., Savini, D., and Forni, G.: Macrobenthos community structural changes off Cesenatico coast (Emilia Romagna, Northern Adriatic), a six-year monitoring programme, Sci. Total. Environ., 353, 317–328, 2005.
Ogrinc, N. and Faganeli, J.: Stable carbon isotopes in pore waters of coastal marine sediments (the Gulf of Trieste, N Adriatic), Acta Chim. Slov., 50, 645–662, 2003.
Paganelli, D., Marchini, A., and Occhipinti-Ambrogi, A.: Functional structure of marine benthic assemblages using Biological Traits Analysis (BTA): a study along the Emilia-Romagna coastline (Italy, North-West Adriatic Sea), Estuar. Coast. Shelf Sci., 96, 245–256, 2012.
Pakhomova, S. V., Hall, P. O., Kononets, M. Y., Rozanov, A. G., Tengberg, A., and Vershinin, A. V.: Fluxes of iron and manganese across the sediment–water interface under various redox conditions, Mar. Chem., 107, 319–331, 2007.
Palinkas, C. M. and Nittrouer, C. A.: Modern sediment accumulation on the Po shelf, Adriatic Sea, Cont. Shelf Res., 27, 489–505, 2007.
Paul, C. R. C., Allison, P. A., and Brett, C. E.: The occurrence and preservation of ammonites in the Blue Lias Formation (lower Jurassic) of Devon and Dorset, England and their palaeoecological, sedimentological and diagenetic significance, Palaeogeogr. Palaeocl., 270, 258–272, 2008.
Penna, N., Rinaldi, A., Montanari, G., Di Paolo, A., and Penna, A.: Mucilaginous masses in the Adriatic Sea in the summer of 1989, Water Res., 27, 1767–1771, 1993.
Petersen, J. K., Hansen, J. W., Laursen, M. B., Clausen, P., Carstensen, J., and Conley, D. J.: Regime shift in a coastal marine ecosystem, Ecol. Appl., 18, 497–510, 2018.
Pirlet, H., Wehrmann, L. M., Brunner, B., Frank, N., Dewanckele, J. A. N., Van Rooij, D., Foubert, A., Swennen, R., Naudts, L., Boone, M., and Cnudde, V.: Diagenetic formation of gypsum and dolomite in a cold-water coral mound in the Porcupine Seabight, off Ireland, Sedimentology, 57, 786–805, 2010.
Powell, E. N., Hu, X., Cai, W. J., Ashton-Alcox, K. A., Parsons-Hubbard, K. M., and Walker, S. E.: Geochemical controls on carbonate shell taphonomy in Northern Gulf of Mexico continental shelf and slope sediments, Palaios, 27, 571–584, 2012.
Precali, R., Giani, M., Marini, M., Grilli, F., Ferrari, C. R., Pečar, O., and Paschini, E.: Mucilaginous aggregates in the northern Adriatic in the period 1999–2002: typology and distribution, Sci. Total. Environ., 353, 10–23, 2005.
Pruss, S., Fraiser, M., and Bottjer, D. J.: Proliferation of Early Triassic wrinkle structures: implications for environmental stress following the end-Permian mass extinction, Geology, 32, 461–464, 2004.
Queirós, A. M., Birchenough, S. N., Bremner, J., Godbold, J. A., Parker, R. E., Romero-Ramirez, A., Reiss, H., Solan, M., Somerfield, P. J., Van Colen, C., and Van Hoey, G.: A bioturbation classification of European marine infaunal invertebrates, Ecol. Evol., 3, 3958–3985, 2013.
Raiswell, R. and Berner, R. A.: Pyrite formation in euxinic and semi-euxinic sediments, Am. J. Sci., 285, 710–724, 1985.
Raiswell, R., Whaler, K., Dean, S., Coleman, M. L., and Briggs, D. E. G.: A simple three-dimensional model of diffusion-with-precipitation applied to localised pyrite formation in framboids, fossils and detrital iron minerals, Mar. Geol., 113, 89–100, 1993.
Raiswell, R. and Canfield, D. E.: Rates of reaction between silicate iron and dissolved sulfide in Peru Margin sediments, Geochim. Cosmochim. Ac., 60, 2777–2787, 1996.
Raiswell, R., Newton, R., Bottrell, S. H., Coburn, P. M., Briggs, D. E., Bond, D. P., and Poulton, S. W.: Turbidite depositional influences on the diagenesis of Beecher's Trilobite Bed and the Hunsrück Slate; sites of soft tissue pyritization, Am. J. Sci., 308, 105–129, 2008.
Renz, J. R., Powilleit, M., Gogina, M., Zettler, M. L., Morys, C., and Forster, S.: Community bioirrigation potential (BIPc), an index to quantify the potential for solute exchange at the sediment-water interface, Mar. Environ. Res., 141, 214–224, 2018.
Reolid, M.: Pyritized radiolarians and siliceous sponges from oxygen-restricted deposits (Lower Toarcian, Jurassic), Facies, 60, 789–799, 2014.
Rhoads, D. C. and Germano, J. D.: Interpreting long-term changes in benthic community structure: a new protocol, Hydrobiologia, 142, 291–308, 1986.
Riedel, B., Zuschin, M., and Stachowitsch, M.: Tolerance of benthic macrofauna to hypoxia and anoxia in shallow coastal seas: a realistic scenario, Mar. Ecol. Prog. Ser., 458, 39–52, 2012.
Rosenberg, R., Nilsson, H. C., and Diaz, R. J.: Response of benthic fauna and changing sediment redox profiles over a hypoxic gradient, Estuar. Coast. Shelf S., 53, 343–350, 2001.
Saleh, F., Pittet, B., Perrillat, J. P., and Lefebvre, B.: Orbital control on exceptional fossil preservation, Geology, 47, 103–106, 2019.
Saleh, F., Pittet, B., Sansjofre, P., Guériau, P., Lalonde, S., Perrillat, J. P., Vidal, M., Lucas, V., El Hariri, K., Kouraiss, K., and Lefebvre, B.: Taphonomic pathway of exceptionally preserved fossils in the Lower Ordovician of Morocco, Geobios, 60, 99–115, 2020.
Sandnes, J., Forbes, T., Hansen, R., Sandnes, B., and Rygg, B.: Bioturbation and irrigation in natural sediments, described by animal-community parameters, Mar. Ecol. Prog. Ser., 197, 169–179, 2000.
Sangiorgi, F. and Donders, T. H.: Reconstructing 150 years of eutrophication in the north-western Adriatic Sea (Italy) using dinoflagellate cysts, pollen and spores, Estuar. Coast. Shelf S., 60, 69–79, 2004.
Savrda, C. E. and Ozalas, K.: Preservation of mixed-layer ichnofabrics in oxygenation-event beds, Palaios, 8, 609–612, 1993.
Schaffner, L. C., Jonsson, P., Diaz, R. J., Rosenberg, R., and Gapcynski, P.: Benthic communities and bioturbation history of estuarine and coastal systems: effects of hypoxia and anoxia, in: Marine Coastal Eutrophication, edited by: Vollenweider, R. A., Marchetti, R., and Viviani, R., Elsevier, 1001–1016, 1992.
Schieber, J.: Styles of agglutination in benthic foraminifera from modern Santa Barbara Basin sediments and the implications of finding fossil analogs in Devonian and Mississippian black shales, in: Anoxia. Evidence for Eukaryote Survival and Paleontological Strategies, edited by: Altenbach, A. V., Bernhard, J. M., and Seckbach, J., Springer, Dordrecht, 573–589, 2012.
Schieber, J. and Baird, G.: On the origin and significance of pyrite spheres in Devonian black shales of North America, J. Sediment. Res., 71, 155–166, 2001.
Schiffbauer, J. D., Xiao, S., Cai, Y., Wallace, A. F., Hua, H., Hunter, J., Xu, H., Peng, Y., and Kaufman, A. J.: A unifying model for Neoproterozoic–Palaeozoic exceptional fossil preservation through pyritization and carbonaceous compression, Nat. Commun., 5, 1–12, 2014.
Schinner, G. O. F.: Burrowing behavior, substratum preference, and distribution of Schizaster canaliferus (Echinoidea: Spatangoida) in the northern Adriatic Sea, Mar. Ecol., 14, 129–145, 1993.
Schinner, F., Stachowitsch, M., and Hilgers, H.: Loss of benthic communities: warning signal for coastal ecosystem management, Aq. Cons.-Mar. Freshw. Ecosyst., 6, 343–352, 1997.
Schenau, S. J., Passier, H. F., Reichart, G. J., and De Lange, G. J.: Sedimentary pyrite formation in the Arabian Sea, Mar. Geol., 185, 393–402, 2002.
Schnedl, S. M., Haselmair, A., Gallmetzer, I., Mautner, A. K., Tomašových, A., and Zuschin, M.: Molluscan benthic communities at Brijuni Islands (northern Adriatic Sea) shaped by Holocene sea-level rise and recent human eutrophication and pollution, The Holocene, 28, 1801–1817, 2018.
Simboura, N. and Zenetos, A.: Benthic indicators to use in ecological quality classification of Mediterranean soft bottom marine ecosystems, including a new biotic index, Mediterr. Mar. Sci., 3, 77–111, 2002.
Simonini, R., Ansaloni, I., Bonvicini Pagliai, A. M., and Prevedelli, D.: Organic enrichment and structure of the macrozoobenthic community in the northern Adriatic Sea in an area facing Adige and Po mouths, ICES J. Mar. Sci., 61, 871–881, 2004.
Slagter, S., Tarhan, L. G., Hao, W., Planavsky, N. J., and Konhauser, K. O.: Experimental evidence supports early silica cementation of the Ediacara Biota, Geology, 49, 51–55, 2021.
Smith, C. R., Levin, L. A., Hoover, D. J., McMurtry, G., and Gage, J. D.: Variations in bioturbation across the oxygen minimum zone in the northwest Arabian Sea, Deep-Sea Res. Pt. II, 47, 227–257, 2000.
Solan, M. and Kennedy, R.: Observation and quantification of in situ animal-sediment relations using time-lapse sediment profile imagery (t-SPI), Mar. Ecol. Prog. Ser., 228, 179–191, 2002.
Solan, M., Cardinale, B. J., Downing, A. L., Engelhardt, K. A., Ruesink, J. L., and Srivastava, D. S.: Extinction and ecosystem function in the marine benthos, Science, 306, 1177–1180, 2004.
Solan, M., Ward, E. R., White, E. L., Hibberd, E. E., Cassidy, C., Schuster, J. M., Hale, R., and Godbold, J. A.: Worldwide measurements of bioturbation intensity, ventilation rate, and the mixing depth of marine sediments, Sci. Data, 6, 1–6, 2019.
Solis-Weiss, V., Aleffi, F., Bettoso, N., Rossi, R., and Orel, G.: The benthic macrofauna at the outfalls of the underwater sewage discharges in the Gulf of Trieste (northern Adriatic Sea), Ann. Ser. Hist. Natur., 17, 1–16, 2007.
Spagnoli, F., Dinelli, E., Giordano, P., Marcaccio, M., Zaffagnini, F., and Frascari, F.: Sedimentological, biogeochemical and mineralogical facies of Northern and Central Western Adriatic Sea, J. Marine Syst., 139, 183–203, 2014.
Stachowitsch, M.: Mass mortality in the Gulf of Trieste: the course of community destruction, Mar. Ecol., 5, 243–264, 1984.
Stachowitsch, M.: Anoxia in the Northern Adriatic Sea: rapid death, slow recovery, Geol. Soc. Spec. Publ., 58, 119–129, 1991.
Staff, G. M. and Powell, E. N.: Local variability of taphonomic attributes in a parautochthonous assemblage: can taphonomic signature distinguish a heterogeneous environment?, J. Paleontol., 64, 648–658, 1990.
Steckbauer, A., Duarte, C. M., Carstensen, J., Vaquer-Sunyer, R., and Conley, D. J.: Ecosystem impacts of hypoxia: thresholds of hypoxia and pathways to recovery, Environ. Res. Lett., 6, 025003, https://doi.org/10.1088/1748-9326/6/2/025003, 2011.
Stefanon, A. T. and Boldrin, A.: The oxygen crisis of the northern Adriatic Sea waters in late fall 1977 and its effects on benthic communities, in: Proceedings of 6th International Science Symposium World Underwater Federation (CMAS), edited by: Blanchard, J., Mair, J., and Morrison, I., National Environmental Research Council, Edinburgh, 167–175, 1982.
Stockdale, A., Davison, W., and Zhang, H.: Formation of iron sulfide at faecal pellets and other microniches within suboxic surface sediment, Geochim. Cosmochim. Ac., 74, 2665–2676, 2010.
Strang, K. M., Armstrong, H. A., Harper, D. A., and Trabucho-Alexandre, J. P.: The Sirius Passet Lagerstätte: silica death masking opens the window on the earliest matground community of the Cambrian explosion, Lethaia, 49, 631–643, 2016.
Tarhan, L. G., Droser, M. L., Planavsky, N. J., and Johnston, D. T.: Protracted development of bioturbation through the early Palaeozoic Era, Nat. Geosci., 8, 865–869, 2015.
Tarhan, L. G., Hood, A. V., Droser, M. L., Gehling, J. G., and Briggs, D. E.: Exceptional preservation of soft-bodied Ediacara Biota promoted by silica-rich oceans, Geology, 44, 951–954, 2016.
Taylor, A., Goldring, R., and Gowland, S.: Analysis and application of ichnofabrics, Earth-Sci. Rev., 60, 227–259, 2003.
Teal, L. R., Bulling, M. T., Parker, E. R., and Solan, M.: Global patterns of bioturbation intensity and mixed depth of marine soft sediments, Aquat. Biol., 2, 207–218, 2008.
Teal, L. R., Parker, E. R., and Solan, M.: Sediment mixed layer as a proxy for benthic ecosystem process and function, Mar. Ecol. Prog. Ser., 414, 27–40, 2010.
Tesi, T., Langone, L., Goñi, M. A., Wheatcroft, R. A., Miserocchi, S., and Bertotti, L.: Early diagenesis of recently deposited organic matter: A 9-yr time-series study of a flood deposit, Geochim. Cosmochim. Ac., 83, 19–36, 2012.
Thamdrup, B., Fossing, H., and Jørgensen, B. B.: Manganese, iron and sulfur cycling in a coastal marine sediment, Aarhus Bay, Denmark, Geochim. Cosmochim. Ac., 58, 5115–5129, 1994.
Thayer, C. W.: Sediment-mediated biological disturbance and the evolution of marine benthos, in: Biotic Interactions in Recent and Fossil Benthic Communities, edited by: Tevesz, M. J. S. and McCall, P. L., Springer, Boston, 479–625, 1983.
Thomsen, E. and Vorren, T. O.: Pyritization of tubes and burrows from Late Pleistocene continental shelf sediments off North Norway, Sedimentology, 31, 481–492, 1984.
Trueman, E. R.: Observations on the mechanism of the opening of the valves of a burrowing lamellibranch, Mya arenaria, J. Exp. Biol., 31, 291–305, 1954.
Tomašových, A., Kidwell, S. M., Barber, R. F., and Kaufman, D. S.: Long-term accumulation of carbonate shells reflects a 100-fold drop in loss rate, Geology, 42, 819–822, 2014.
Tomašových, A., Gallmetzer, I., Haselmair, A., Kaufman, D. S., Vidović, J., and Zuschin, M.: Stratigraphic unmixing reveals repeated hypoxia events over the past 500 yr in the northern Adriatic Sea, Geology, 45, 363–366, 2017.
Tomašových, A., Gallmetzer, I., Haselmair, A., Kaufman, D.S., Kralj, M., Cassin, D., Zonta, R., and Zuschin, M.: Tracing the effects of eutrophication on molluscan communities in sediment cores: outbreaks of an opportunistic species coincide with reduced bioturbation and high frequency of hypoxia in the Adriatic Sea, Paleobiology, 44, 575–602, 2018.
Tomašových, A., Gallmetzer, I., Haselmair, A., Kaufman, D. S., Mavrič, B., and Zuschin, M.: A decline in molluscan carbonate production driven by the loss of vegetated habitats encoded in the Holocene sedimentary record of the Gulf of Trieste, Sedimentology, 66, 781–807, 2019a.
Tomašových, A., Kidwell, S. M., Alexander, C. R., and Kaufman, D. S.: Millennial-scale age offsets within fossil assemblages: Result of bioturbation below the taphonomic active zone and out-of-phase production, Paleoceanogr. Paleocl., 34, 954–977, 2019b.
Tomašových, A., Albano, P. G., Fuksi, T., Gallmetzer, I., Haselmair, A., Kowalewski, M., Nawrot, R., Nerlović, V., Scarponi, D., and Zuschin, M.: Ecological regime shift preserved in the Anthropocene stratigraphic record, P. Roy. Soc. B, 287, 20200695, https://doi.org/10.1098/rspb.2020.0695, 2020.
Tomašových, A., Gallmetzer, I., Haselmair, A., and Zuschin, M.: Inferring time averaging and hiatus durations in the stratigraphic record of high-frequency depositional sequences, Sedimentology, 2022, doi.org/10.1111/sed.12936, 2021.
Underwood, C. J. and Bottrell, S. H.: Diagenetic controls on multiphase pyritization of graptolites, Geol. Mag., 131, 315–327, 1994.
Valente, R. M. and Cuomo, C.: Did multiple sediment-associated stressors contribute to the 1999 lobster mass mortality event in Western Long Island Sound, USA?, Estuaries, 28, 529–540, 2005.
van de Velde, S. and Meysman, F. J.: The influence of bioturbation on iron and sulphur cycling in marine sediments: a model analysis, Aquat. Geochem., 22, 469–504, 2016.
Vatova A.: La fauna bentonica dell'alto e medio Adriatico, Nova Thalassia, 1, 1–110, 1949.
Villnäs, A., Norkko, J., Lukkari, K., Hewitt, J., and Norkko, A.: Consequences of increasing hypoxic disturbance on benthic communities and ecosystem functioning, Plos One, 7, e44920, https://doi.org/10.1371/journal.pone.0044920, 2012.
Virtasalo, J. J., Löwemark, L., Papunen, H., Kotilainen, A. T., and Whitehouse, M. J.: Pyritic and baritic burrows and microbial filaments in postglacial lacustrine clays in the northern Baltic Sea, J. Geol. Soc. London, 167, 1185–1198, 2010.
Virtasalo, J. J., Whitehouse, M. J., and Kotilainen, A. T.: Iron isotope heterogeneity in pyrite fillings of Holocene worm burrows, Geology, 41, 39–42, 2013.
Volkenborn, N., Meile, C., Polerecky, L., Pilditch, C. A., Norkko, A., Norkko, J., Hewitt, J. E., Thrush, S. F., Wethey, D. S., and Woodin, S. A.: Intermittent bioirrigation and oxygen dynamics in permeable sediments: An experimental and modeling study of three tellinid bivalves, J. Mar. Res., 70, 794–823, 2012.
Vopel, K., Thistle, D., and Rosenberg, R.: Effect of the brittle star Amphiura filiformis (Amphiuridae, Echinodermata) on oxygen flux into the sediment, Limnol. Oceanogr., 48, 2034–2045, 2003.
Walker, S. E. and Goldstein, S. T.: Taphonomic tiering: experimental field taphonomy of molluscs and foraminifera above and below the sediment–water interface, Palaeogeogr. Palaeocl., 149, 227–244, 1999.
Westall, F.: The nature of fossil bacteria: a guide to the search for extraterrestrial life, J. Geophys. Res.-Planets, 104, 16437–16451, 1999.
Wignall, P. B., Newton, R., and Brookfield, M. E.: Pyrite framboid evidence for oxygen-poor deposition during the Permian–Triassic crisis in Kashmir, Palaeogeogr. Palaeocl., 216, 183–188, 2005.
Wijsman, J. W. M., Herman, P. M. J., Middelburg, J. J., and Soetaert, K.: A model for early diagenetic processes in sediments of the continental shelf of the Black Sea, Estuar. Coast. Shelf S., 54, 403–421, 2002.
Wilson, M. A. and Taylor, P. D.: Exceptional pyritized cyanobacterial mats encrusting brachiopod shells from the Upper Ordovician (Katian) of the Cincinnati, Ohio, region, Palaios, 32, 673–677, 2017.
Wheatcroft, R. A.: Preservation potential of sedimentary event layers, Geology, 18, 843–845, 1990.
Woodin, S. A., Wethey, D. S., and Volkenborn, N.: Infaunal hydraulic ecosystem engineers: cast of characters and impacts, Integr. Comp. Biol., 50, 176–187, 2010.
Wrede, A., Dannheim, J., Gutow, L. and Brey, T.: Who really matters: influence of German Bight key bioturbators on biogeochemical cycling and sediment turnover, J. Exp. Mar. Biol. Ecol., 488, 92–101, 2017.
Wrede, A., Beermann, J., Dannheim, J., Gutow, L. and Brey, T.: Organism functional traits and ecosystem supporting services–A novel approach to predict bioirrigation, Ecol. Indic., 91, 737–743, 2018.
Yonge, C. M.: On the habits and adaptations of Aloidis (Corbula) gibba, J. Mar. Biol. Assoc. UK, 26, 358–376, 1946.
Yonge, C. M.: Ligamental structure in Mactracea and Myacea (Mollusca: Bivalvia), J. Mar. Biol. Assoc. UK, 62, 171–186, 1982.
Zanchettin, D., Traverso, P., and Tomasino, M.: Po River discharges: a preliminary analysis of a 200-year time series, Climatic Change, 89, 411–433, 2008.
Zhu, M., Babcock, L. E., and Steiner, M.: Fossilization modes in the Chengjiang Lagerstätte (Cambrian of China): testing the roles of organic preservation and diagenetic alteration in exceptional preservation, Palaeogeogr. Palaeocl., 220, 31–46, 2005.
Zillén, L., Conley, D. J., Andrén, T., Andrén, E., and Björck, S.: Past occurrences of hypoxia in the Baltic Sea and the role of climate variability, environmental change and human impact, Earth-Sci. Rev., 91, 77–92, 2008.
Zuschin, M., Stachowitsch, M., Pervesler, P., and Kollmann, H.: Structural features and taphonomic pathways of a high-biomass epifauna in the northern Gulf of Trieste, Adriatic Sea, Lethaia, 32, 299–316, 1999.
Zuschin, M. and Stachowitsch, M.: Epifauna-dominated benthic shelf assemblages: lessons from the modern Adriatic Sea, Palaios, 24, 211–221, 2009.