Abstract
High-nutrient tropical carbonate systems are known to produce sediments that, in terms of skeletal composition, are reminiscent of their extra-tropical counterparts. Such carbonate systems and associated carbonate grain assemblages in the tropics are rare in the present-day world. Nonetheless, it is crucial to gain a better understanding of those ecosystems, including their drivers and players because such settings potentially represent models for ancient depositional systems as well as for predicted future environmental conditions. One of the modern occurrences of eutrophic tropical carbonate systems is the northern Mauritanian Shelf. The marine environment is characterized by an eastern boundary upwelling system that pushes cool and nutrient-rich intermediate waters onto a wide epicontinental platform (Golfe d’Arguin) where the waters warm up to tropical temperatures. The resulting facies is mixed carbonate–siliciclastic with a dominant foramol association grading into bimol and barnamol grain assemblages in the shallowest areas forming the Banc d’Arguin. Besides this cool water-related heterozoan association, the carbonate sediment is characterized by tropical molluskan species, while chlorozoan biota (e.g., corals and algal symbiont-bearing foraminifers) are entirely absent. We here present a first comprehensive facies analysis of this model example of eutrophic tropical carbonates. Furthermore, we reconstruct the loci of carbonate production and provide a conclusive depositional model of the Banc d’Arguin that received little attention to date due to its poorly accessible nature.
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Introduction
The impact of climate change, rising sea level, and the fingerprint of human-induced eutrophication make comprehensive studies on tropical marine ecosystems more important than ever for predicting future developments (Hallock 2005; Solomon 2007; Taylor et al. 2012). Marine ecosystems in low latitudes such as mangroves, seagrass meadows, and coral reefs provide a wide range of socio-economic services, besides their important role as biodiversity hotspots that need efficient protection against the disturbances by human activity (Myers et al. 2000; Hoegh-Guldberg et al. 2007; Gilman et al. 2008; Gattuso and Hansson 2011; Fourqurean et al. 2012). Therefore, research integrating environmental steering factors, processes, and threats on carbonate sedimentation is essential for acquiring reliable insights into future developments of coastal marine ecosystems.
Biogenic sediments provide a range of proxies that can be used to reconstruct environmental conditions and settings through time (Scholle et al. 1983; Mutti and Hallock 2003; Halfar et al. 2004; Pomar et al. 2004; Wright and Burgess 2005). Particularly, the analysis of carbonate-grain assemblages has become a key tool for paleoenvironmental reconstructions from the tropics up to the polar realm (Chave 1967; Lees and Buller 1972; Hayton et al. 1995; James and Clarke 1997). Such biofacies patterns shed light on the spatial and temporal distribution of marine ecosystems in relation to past and present climatic conditions.
In the last decades, two major classification concepts of carbonate sediments have been developed. The first one is based on a combination of composite terms, such as foramol (foraminifers and mollusks) and chlorozoan (chlorophyta, hermatypic corals, and mollusks) (Lees and Buller 1972), while the more recent concept uses a bimodal approach (photozoan vs. heterozoan carbonate association), accentuating the presence or absence of photosymbiotic carbonate-producing benthic organisms (James and Clarke 1997). Both schemes provide a framework for the interpretation of modern and ancient carbonate deposits in various environmental contexts (see case studies in Flügel 2010). However, the terms heterozoan and photozoan have become, in some cases, simplified synonyms for the descriptive approach to classify non-tropical, cold-water versus tropical, warm-water regimes (cf. Nelson 1988; Nelson et al. 1988). The ongoing discussion demonstrates that both concepts have strengths and shortcomings, but that the influence of a wider range of environmental controls needs to be considered (Hallock 1988; Betzler et al. 1997a, b; Brandano and Corda 2002; Samankassou 2002; Pomar et al. 2004; Brandano et al. 2009; Kindler and Wilson 2010; Westphal et al. 2010; Betzler et al. 2011; Schäfer et al. 2011; Reijmer et al. 2012). Knowledge of the ecological context and environmental steering parameters is thus crucial for an interpretation of sub-recent and fossil facies (Martín et al. 1996, 2001; Samankassou 2002; Perry and Taylor 2009; Barange et al. 2010; Doney et al. 2012). These factors include biological evolution, temperature, salinity, trophic conditions, water depth, oxygen and CO2 concentrations, Mg/Ca ratio in the seawater, alkalinity, bathymetry, type of substrate, illumination, internal waves, and water stratification (see Westphal et al. 2010 and references therein). Neglecting one or a combination of these controls might result in paleoenvironmental misinterpretations (cf. Edinger et al. 2002; Samankassou 2002; Pomar et al. 2004). The restricted occurrences of modern heterozoan carbonate depositional systems in tropical latitudes provide a key to better constrain the multi-dimensional ecological control on carbonate sedimentation (Halfar et al. 2004; Kindler and Wilson 2010; Westphal et al. 2010; Schäfer et al. 2011; Reijmer et al. 2012).
Here we discuss the Golfe d’Arguin offshore northern Mauritania as one of the present-day tropical heterozoan carbonate factories. Previous sedimentological studies took place in different parts of the shelf such as the Baie de Lévrier (Koopmann et al. 1978, 1979), the outer shelf (Hanebuth and Lantzsch 2008; Michel et al. 2011a, b; Hanebuth et al. 2013; Klicpera et al. 2013, 2014), the innermost shelf (Barusseau et al. 2007, 2010; Aleman et al. 2014), and in the vicinity of Tidra Island (Proske et al. 2008). However, none of these studies provides a comprehensive picture of the sedimentary facies distribution. One reason for the rather low research intensity is the restricted access to the shallow waters of the Banc d’Arguin. It cannot be accessed by larger research vessels and is by far too extensive for coverage by small boats (Wolff et al. 1993c).
In this study, we combine samples from the outer Banc d’Arguin (Westphal et al. 2007; 2014) with earlier investigations from the inner Banc d’Arguin (Piessens 1979) to a comprehensive facies pattern model. The aim is to identify areas of tropical heterozoan carbonate production and facies distribution by reconstructing the sedimentation dynamics in the Golfe d’Arguin and to infer from this example general patterns of eutrophic tropical carbonate deposition.
Study area
Off northern Mauritania, the narrow West African shelf (~50 km in width) opens up into a wide gulf of more than 150 km in east–west extension (Einsele et al. 1972; Piessens 1979). The so-called Golfe d’Arguin (GdA; Fig. 1) stretches between the Baie du Lévrier (BdL; 21°10′N) and the Cap Timiris Shelf (CTS; 19°20′N) over a distance of about 200 km (Piessens and Chabot 1977).
The depositional profile of the northern GdA describes a flat-topped platform (gradient 0.3 m km−1; Fig. 1, transect A), on which extensive carbonate deposits (Banc d’Arguin; BdA) developed largely in water depths <10 m (mbsl). Vast areas of the BdA are covered by mixed carbonate–siliciclastic sediments dominated by barnamol assemblages (balanids and mollusks) sensu Hayton et al. (1995) plus admixed eolian siliciclastics (Sarnthein and Walger 1974; Westphal et al. 2007, 2014). These sediments accumulate into extensive shoals, occasionally causing water depths below 5 mbsl (Prévost 1746; Piessens 1979; Sevrin-Reyssac 1993). The bank edge forms a sharp morphological step, suddenly deepening from 10–20 mbsl down to 30–50 mbsl, and separates the inner shelf environments (<5–10 mbsl; carbonate bank) from those of the outer shelf (>30 mbsl; open platform, see Hanebuth et al. 2013).
Foramol assemblages (foraminifers and mollusks) sensu Lees and Buller (1972) and bimol assemblages (bivalve mollusks) sensu Hayton et al. (1995) with admixed eolian silt characterize the platform cover in the outer shelf (Sarnthein and Walger 1974, Piessens 1979; Michel et al. 2009). In the central and southern outermost shelf, silt-sized quartzose materials (mode at 35 µm) form confined bodies referred to as the Arguin mud wedge (AMW) and Timiris mud wedge (TMW) (cf. Hanebuth and Lantzsch 2008). These deposits started to form with transgressional inundation early in the Holocene and have grown continuously and rapidly over the past 9 kyrs (Sarnthein and Diester-Haass, 1977; Hanebuth and Lantzsch 2008). Locally, the AMW and TMW deposits are incised by gullies and canyons towards the shelf break lying at around 80–110 mbsl (Hanebuth et al. 2013). The southernmost GdA describes a homoclinal ramp profile (gradient 3–4 m km−1) with vast intertidal plains around Tidra Island (Wolff et al. 1993a, b; Proske et al. 2008; Fig. 1, transect B).
Oceanographic setting
The oceanography of NW Africa is characterized by tropical waters (>24 °C; <35 ‰) of the northward-directed Guinea Current and cool waters of the southward flowing Canary Current (<24 °C; >35 ‰). Additionally, nutrient-enriched upwelling waters (<18 °C; <36 ‰) are pumped onto the shelf and into the photic zone by Ekman transport, induced by equatorward Trade Winds that control the eastern boundary Canary Current (Maigret 1972). During winter, a branch of the Canary Current is displaced as far south as 20°N, while during summer, the Guinea Current and thus tropical waters dominate the hydrology of the GdA (Mittelstaedt 1991; Van Camp et al. 1991). As a result, a perennial upwelling cell occurs year-round north of 21°N (Cap Blanc), whereas the upwelling activity is seasonal-controlled south of this latitude and in the study area (maximum upwelling intensities February–June and October–December, cf. Sevrin-Reyssac 1993; Fig. 2). These oscillating upwelling conditions allow for water stratification to develop during non-upwelling periods and nutrients to concentrate in calm photic water layers where they push the primary production (Huntsman and Barber 1977). As a consequence, the primary productivity off Cap Blanc is one of the highest worldwide with values exceeding 325 g C m−2 year−1 (annual mean of 200 g C m−2 year−1) and chlorophyll a (Chl-a) values of 3 to >10 mg m−3 (Marañón and Holligan 1999; Fig. 2).
Mean annual water temperatures (>23 °C) in the GdA show a pronounced seasonality with lowest sea surface temperatures (SST) of 16–17 °C recorded near Cap Blanc (April–May) corresponding to spring upwelling. Maximum water temperatures of >26 °C occur during September–October (Fig. 2) in the nearshore and intertidal areas around Tidra Island (Sevrin-Reyssac 1993). Strong insolation in spring and summer leads to a pronounced temperature gradient across the area and a high seasonal variability (Peters 1976; Koopmann et al. 1978, 1979; Ould Dedah 1993; Hagen 2001). Strong surface currents (2–3 m s−1) characterize the GdA, particularly the shallow BdA, and are related to tidal currents, the wind regime and upwelling swell. In restricted areas, such as the Baie de Saint Jean (BdSJ) the conditions become extreme with highest water temperatures and salinities reaching hypersaline concentrations (Sevrin-Reyssac 1993).
Materials and methods
Surface sediments were collected during the research cruise “PHAETON” aboard the R/V Maria S. Merian (MSM16/3, October–November 2010; Westphal et al. 2014). To access the shallow, westernmost parts of the BdA from the seaside, an auxiliary zodiac was deployed from the research vessel. Six remote sites within the BdL (station IDs 14783, 14786), along the central BdA (station ID 14833), the southern BdA (station IDs 14812, 14725), and in the CTS area (station ID 14748) were sampled (Table 1). For each of these stations, 15–24 sub-samples (SedBulk) were taken using a Van Veen grab (surface sediments; N = 125). Additionally, oceanographic profiles of the water column were measured with a miniCTD probe (temperature and salinity; N = 49) and a Secchi disk (light penetration depth; N = 44).
Carbonate content
Carbonate contents were determined as the mean weight percentage (wt % CaCO3) of four replicates per bulk sample (N = 468) following the carbometer method of Müller and Gastner (1971). The internal error of this procedure is less than ±1 % CaCO3. To improve precision, the carbometer device was calibrated at least twice daily with a calcium carbonate standard (99.5 % CaCO3).
Grain size determination
Sediment samples were classified on board the vessel into two textural groups that defined their further treatment: (1) coarse-grained bulk sediments (N = 75) that were washed and dried at +60 °C; (2) fine-grained materials (N = 45), directly wet-stored as bulk material in a cooling facility at +4 °C to reduce biodegradation of organic material. Back to the laboratory, the coarse-grained samples were dry-sieved by means of a sieve shaker, while the fine-grained sediments were first split at 500 µm and then either wet-sieved (>500 µm) or analyzed by means of a laser granulometer (<500 µm; cf. Blott et al. 2004). Laser granulometer raw data were re-calculated in Gradistat (Blott and Pye 2001) to make the applied techniques and datasets comparable. Additional grain-size data were extracted from Piessens (1979), Koopmann et al. (1979), and Michel et al. (2011a). All data were subsequently split in eight grain-size classes (<62, 62–125, 125–250, 250–500, 500–1,000, 1,000–2,000, and >2,000 µm) following Wentworth (1922). Measurements are given as the weight percentage (wt %) of the bulk sediment (SedBulk).
Component analysis
The component analysis was undertaken on surface sediments by determining a minimum of 300 skeletal grains per fraction (N = 18,823 counts). Analyzed component groups are given as mean percentages of the three coarsest fractions (>500–1,000, 1,000–2,000 and >2,000 µm) of sediments sampled at three sites per station (N = 18; Table 1). The high identification potential (>94 %) of the fraction >500 µm allowed to differentiate bivalves, gastropods, foraminifers, bryozoans, echinoderms, serpulids, coralline red algae, balanids, and undeterminable bioclasts. Bivalve and gastropod grains were determined, where possible, down to species level (N = 3,287; Suppls. 1, 2). Non-skeletal grains are classified as siliciclastics, aggregates, pellets, and undeterminable material.
Additional sediment samples were provided by an environmental monitoring program carried out by the Mauritanian government (BdSJ sediments; IMROP, 2013). Other component data were taken from Piessens (1979), Koopmann et al. (1979), and Michel et al. (2011a). All data were recalculated on a percentage basis excluding unidentified components and standardized with respect to component groups used to allow direct comparability. The abundance scale used follows the recommended classification scheme, cf. Flügel (2010, p 262).
Statistical analysis and mapping program
Sedimentary facies types were determined on the basis of grain size and composition of the sediment. A hierarchical cluster analysis (dendrogram using Ward’s method; Ward 1963) was performed using JMP data analysis software for MacOS version 9.0.2 (Fig. 5) to statistically distinguish groups and clusters of samples. Non-determinable grains were not included in the statistical analysis.
Mapping of facies data was achieved using Ocean Data View (ODV) version 4.6.2. Areas of poor sample resolution were interpolated by the Diva gridding method provided in ODV (Schlitzer 2012). The resulting facies map was later processed in a vector graphics software and manually translated into a hexagonal grid (Fig. 7) to allow a better overview of facies zones identified.
Results
Oceanographic data
CTD casts from the outer BdA give a total temperature range (water column) between 18.2 and 24.3 °C (mean = 20.6 °C; October–November 2,010). SSTs range between 18.7 and 24.3 °C (mean = 21.1 °C); sea bottom temperatures (SBT) show values between 18.2 and 24.3 °C (mean = 19.8 °C). The highest temperature contrast (entire water column) is observed in the southern BdA, where SBTs and SSTs range between 18.2 and 24.3 °C respectively (mean = 20.3 °C). The lowest temperature contrast occurs in the central BdA where SBTs and SSTs range between 19.4 and 21.2 °C respectively (mean = 19.9 °C; Table 2).
CTD-based salinity measurements show a total range between 35.1 and 38.0 ‰ (mean = 36.0 ‰) that correspond to the range of sea surface salinities (SSS; mean = 36.1 ‰). Sea bottom salinities (SBS) range from 35.9 to 36.5 ‰ (mean = 36.0 ‰). The greatest contrasts occur in the southern BdA, where the mixed surface water layer ranges between 35.8 and 38.0 ‰ (mean = 36.0 ‰). The lowest SSS range was measured in the central BdA with values between 35.7 and 36.4 ‰ (mean = 36.0 ‰; Table 2).
Secchi disk measurements (Table 3) show a light penetration averaging at 3 mbsl (N = 43). The lowest water transparencies of <2 mbsl (N = 10) are observed in the BdL and in the southern BdA (station 14748). Intermediate water transparencies of 2–4 mbsl (N = 22) are ubiquitous with the exception of the central BdA where transparencies of >4 mbsl (N = 11) are observed. Greater light penetration depths occur in the southern BdA (stations 14725, 14812) and near the CTS (Tables 2, 3).
Multi-annual remote sensing data show well-defined seasonal cycles. Area-averaged SSTs range from 18 to 26 °C for the entire area (19.0°N–21.5°N; 19.0°W–16.0°W) and are slightly higher for the GdA (19.0–27.0 °C; 19.5°N–21.0°N; 17.0°W–16.0°W) (Fig. 2a, b). The Chl-a concentrations show a seasonal pattern oscillating around 5 mg m−3 for the entire area with prominent peaks in the order of 10 to >20 mg m−3 for the GdA (Fig. 2c, d).
Sedimentary facies
Surface sediment texture
The outer BdA is covered by two sediment types: (1) Coarse-grained bioclastic sands with minor portions of rounded quartz (N = 75) and (2) quartzose sands with a low amount of coarse skeletal grains (N = 45). Rocky hardgrounds occur along the bank margin resulting in empty grabs (station 14748; N = 5) or in the recovery of cemented aggregates.
Towards the outer shelf (>30 mbsl; Fig. 1, transect A), the bioclastic sands grade into quartzose sands and silts with increasing water depth (Fig. 3b, c, d). Silt-sized muddy bodies (AMW, TMW) separate the outermost shelf with locally exposed erosion surfaces from the shelf break (Fig. 1, see Hanebuth et al. 2013 for nomenclature used).
Carbonate content
Dry bulk sediments from the outer BdA and BdL range from 16 to 85 % in calcium carbonate content (N = 468; Table 3). The highest values are recorded in the BdL (34–85 %; mean = 56 %) and in the southern BdA (21–85 %; mean = 55 %). Sediments from the central BdA range from 39 to 45 % (mean = 42 %), while the southernmost CTS shows lowest measured contents ranging from 16 to 52 % (mean = 37 %).
Over the entire GdA, carbonate contents exceed >80 % in the northern GdA and in the vicinity of Cap Blanc with slightly decreasing contents from north to south and from shallow to deeper water. The lowest carbonates contents occur in nearshore settings and around Tidra Island (Fig. 3a).
Grain-size distribution
Sand-sized fractions dominate (82 %) the bulk sediments from the BdA and BdL throughout (N = 113; Fig. 3) with fine-grained (125–250 µm) and coarse-grained (500–1,000 µm) sands averaging at 25 and 21 %, respectively. Silt and clay-sized materials (<63 µm) average at 14 %; gravel-sized sediments (>2,000 µm) at 3 %. Restricted areas such as the BdL show a shift towards finer grain-size classes, dominated by sand-sized fractions (70 %) with fine-grained sand accounting for 21 % and medium-grained sand (250–500 µm) for 15 % of the bulk sediment. Silt and clay-sized materials average at 29 %; gravel-sized at material not more than 1 %. Particle size curves (Fig. 3) show monomodal distributions in the southern BdA (mode 500–1,000 µm at station 14725) and the CTS (mode 125–250 µm at station 14748) or polymodal distributions of particles in the BdL (stations 14783, 14786), the central BdA (station 14833) and the southern BdA (station 14812).
GdA-wide grain-size distributions show a dominance of sand-sized classes with larger areas covered by 80–100 % sand (Fig. 3c) south of Cap Blanc and towards the outer shelf, in the central to southern BdA and around Tidra Island. Gravel-rich deposits occur in the area between the central BdA and Cap Blanc as well as in the CTS (Fig. 3b). Periplatform muds (<63 µm) are restricted to the BdL (<40 %), the Cuvette d’Arguin (<60 %) and to off-bank settings below the storm wave-base (>20 mbsl). On the outer shelf (>50–100 mbsl), the AMW and TMW show accumulations in the silt to fine-sand range (35–125 µm) of <40 and <80 %, respectively (Fig. 3d).
Non-skeletal components
Abiogenic grains are rare to sparse constituents throughout the outer BdA sediments averaging at 3 % of the component-analyzed samples (fractions >500 µm). Siliciclastics average at 2 % with a maximum of 9 % in the southern BdA (station 14725). Aggregated grains average at 1 % but can show elevated contents of up to 5 % (BdL, station 14783).
Over the entire GdA, abiogenic grains occur in quantities exceeding >25 % of the component-analyzed samples (fractions >500 µm) along nearshore areas (e.g., Cap Blanc, Cuvette d’Arguin, Timiris Island) but also offshore in the AMW area. Siliciclastics (quartz grains; Fig. 4a) average at 19 % with local enrichments (<89 %) south of Cap Blanc and in the southern BdA. Fecal pellets average at 8 % with maximum contents of up to 35 % restricted to low-energy settings such as the BdL and the Cuvette d’Arguin (Fig. 4b). Aggregates average at 6 % but can reach contents of 63 % along nearshore environments (e.g., south of Cap Blanc; BdL) and close to submarine outcrops. Accumulations in aggregates (>50 %) can also occur as allochthonous deposits within low-energy regimes (e.g., Cuvette d’Arguin; Fig. 4b).
Skeletal components
Mollusks The variety of mollusk grains present in the BdA and BdL sediments is characteristic of an environment influenced by mixed coastal and open marine conditions (Michel et al. 2011a, b). Whole and reworked shells occur as common to abundant constituents in most sediment types and water depths averaging at 50 % of the component-analyzed materials (fractions >500 µm). The highest contents (82 %) were found in the central BdA.
The GdA-wide distribution of mollusk shells shows abundant contents averaging at 56 % (fractions >500 µm) and a maximum of up to 93 % in the central BdA and around Cap Blanc. Lower contents of 83 % occur in the northern Cuvette d’Arguin and in nearshore areas close to the Baie d’Arguin.
Balanids Hard-substrate-related balanid grains (Balanus cf. trigonus; Darwin, 1854) are ubiquitous in the outer BdA (Gruvel 1912). Such balanid accumulations average at 35 % (fractions >0.5 mm) with highest concentrations of 67 % in the northern BdL (station 14783). Percentages around 55 % occur in the southern BdL (station 14786) and in the southern BdA (stations 14725 and 14812).
Over the entire GdA, balanid grains average at 17 % (fractions >500 µm; Fig. 4d) with dominant occurrences (>50 %) restricted to shallow subtidal waters (<10 mbsl) in the BdL (60 %), the northern BdA (56 %), and in the southern BdA (58 %). Balanid sands can accumulate to extensive shoals forming shallows of <5 mbsl more than 100 km offshore. The majority of balanid grains recovered from the BdA are disarticulated plates, however, some entire shells are found as clusters attached to rocks (southern BdA) or to larger mollusk shells such as Venus crebrisulca in the central BdA.
Coralline red algae Sediment samples from the outer BdA and BdL provide no significant records of coralline red algae, however, their abundance over the entire GdA averages at 6 % (fractions >500 µm; Fig. 4e) with enrichments of up to 63 % restricted to the southern BdA.
Foraminifers Foraminifers are very rare (<2 %) in the outer BdA. The GdA-wide distribution of foraminifers averages at 5 % (Fig. 4f) with higher concentrations in fine-grained sediments alongside the outer shelf and in the CTS area. The highest occurrences (>30 %; Fig. 6g, h) of the bulk sediment were identified as Tetragonostomina rhombiformis (Mikhalevich 1975). Other sparse to common distributed taxa are the benthic taxa Siphonaperta sp., Quinqueloculina sp., Eponides sp., Homotrema sp., and the planktonic Globigerinoides ruber (Cushman 1927) see details in Reymond et al. (2014).
Bryozoans Samples from the BdA margin and BdL show rare to sparse bryozoan records averaging at 2 % (fractions >500 µm). The highest contents are restricted to the southern BdA (station 14812) where bryozoans may reach up to 10 % of the sediment constituents.
The same quantity in distribution and local appearance applies for the entire GdA. In the central BdA, abundant in situ bryoliths were identified formed by symbiotic associations between the bryozoan Acanthodesia commensale (Kirkpatrick and Metzelaar 1922) and hermit crabs (Klicpera et al. 2013). Other common (<10 %) bryozoans in the CTS area are free-living cupuladriid colonies (e.g., Discoporella spp., Reussirella spp., and Cupuladria spp.; Klicpera et al. 2014).
Echinoderms Remains of echinoderms average at 1 % (fractions >500 µm) in the samples from the BdA. However, their abundance in the fraction >2 mm can be as high as 7 %, especially in the southern BdA where the infaunal species Heliophora orbicularis (Linnaeus, 1758) is a common constituent in surface sediments (Fig. 6e).
The GdA-wide distribution of echinoderm grains averages at 2 % (Fig. 4h) with local accumulations of up to 18 % of the sediment constituents in the southern BdA and up to 17 % in the outer shelf area south of Cap Blanc (northern BdA).
Mollusk taphonomy
Mollusk assemblages from the BdA were further investigated taxonomically for their ecological significance in the study area. In total, 109 taxa were identified from 3,657 mollusk shells that were picked from eight sampling sites in BdL and BdA and one additional sample from the BdSJ (fractions >500 µm). Among these, 3,287 identified bivalve grains account for 90 % of the mollusk grains (Table 4; Fig. 4c) and clearly highlight the dominance of bivalve mollusks in the GdA.
Sediment samples from the outer BdA and BdL show high abundances of the bivalves Donax burnupi (Sowerby III, 1894) with >50 % (occasionally >90 %) in BdL and CTS; Timoclea ovata (Pennant, 1777) with >50 % in CTS area, and Papillicardium papillosum (Poli, 1791) with 30–50 % in BdL area of the component analyzed fractions (Table 4). The complete list of bivalve and gastropod taxa identified is given as supplements to this study.
Over the entire GdA, extensive deposits of Venus crebrisulca (Lamarck, 1818) shells indicate economically significant stocks that were investigated in Goudswaard et al. (2007). In nearshore areas, the species Senilia senilis (=Anadara senilis; Linnaeus, 1758) yields abundant archeological material and represents the main mollusk exploited by ancient human populations living in the GdA hinterland (Barusseau et al. 2007). The deeper outer shelf (>30 mbsl) shows remains and in situ records of Pinna rudis (Linnaeus, 1758) and scattered shells identified as the chemosymbiotic bivalve Solemya togata (Poli, 1791) prospering in muddy to fine-grained sediments (Westphal et al. 2014).
Integrated facies analysis
The facies-type definition of surface sediments is based on a cluster analysis (N = 251; Fig. 5) gathering data from the present study and from the literature (re-analyzed datasets; cf. section Materials and methods). In total, six grain assemblages (F1 to F4 including subgroups F3A, F3B, F4A and F4B) are distinguished (Fig. 7), whose characteristics and interpretations are listed in Table 5.
Discussion
Cool-water-related grain assemblages in the GdA highlight a strong environmental control under which marine carbonate-secreting biota have developed. A complex oceanographic regime and the co-occurrence of tropical key species together with a dominant cool-water-related community suggest that temperature–depth relationships alone may not account for the presence of heterozoan carbonates at low latitudes. The following environmental parameters were identified to have a significant effect on the formation of tropical heterozoan carbonates in the GdA: (1) upwelling-induced high nutrient water conditions, (2) low water transparencies due to high Chl-a levels and re-suspended sediments, (3) a strong hydrological regime, and (4) annual high water temperatures. Additionally, the availability of hard bottoms and other topographic shelf features in the shallow BdA act as steering factors affecting carbonate production. The impact of these controls on benthos ecology, sediment formation, reworking, and distribution results in a characteristic facies zonation (Fig. 7) discussed in the following sections.
Oceanographic parameters
Temperature
The remote sensing SST dataset (Fig. 2) and the studies of Cuq (1993), Ould Dedah (1993), and Ould Mahfoudh et al. (1991) showed that water temperatures in the GdA undergo significant seasonal variations. This pattern is attributed to the changing influence of (1) the tropical Guinea Current (<35 ‰, >24 °C); (2) the temperate Canary Current (>35 ‰, <24 °C) coupled with upwelling-induced cool intermediate waters, and (3) shallow subtidal to intertidal coastal waters (BdA and BdL; >39 ‰, >28 °C) heated by solar-driven evaporation. Seasonal displacements of either cold (Canary Current) or warm (Guinean Current) water masses in the GdA thus cause a pronounced hydrographic heterogeneity in both, a spatial and temporal dimension (Sevrin-Reyssac 1993).
The CTD dataset taken in October–November 2010 (MSM16-3) indicates a temperature contrast of up to 5.6 °C (18.7–24.3 °C; Table 2) in the southern BdA. This significant variation in temperature is related to cold upwelled waters (<20 °C) and warm coastal waters (>22 °C) from the intertidal settings close by. The temperature variation, however, is in agreement with Ould Dedah (1993) reporting a maximum temperature variability of up to 9 °C in the southern BdA. Such upwelling-induced cool water intrusions in epicontinental seas cause distinct thermal fronts, to which the benthos adapts by forming ‘atypical’ eurythermal communities in the shallow bank (cf. Westphal et al. 2010; Michel et al. 2011a, Schäfer et al. 2011; Reijmer et al. 2012; Table 6.). Nonetheless, such conditions put intensive stress on most carbonate secreting biota and explains the absence of temperature-sensitive groups (e.g., chlorozoan biota; Halfar et al. 2006).
Salinity
Similar to water temperature, the salinity pattern displays distinct variations over the year with values between 35.5 and 37.0 ‰ for the seaward part of the BdA and values exceeding 38 ‰ for inshore environments (Ould Dedah 1993). CTD measurements taken in October–November 2010 (MSM16-3) agree with those of previously reported ranges showing a range between 35.1 and 38.0 ‰ (mean = 36.1 ‰) for the outer BdA and BdL. Again, the highest contrasts are identified in the southern BdA, where salinity-depleted waters of the Guinean Current collide with salinity-enriched coastal waters. The highest salinity records are reported from isolated and restricted bays in the innermost BdA such as the semi-enclosed BdSJ, where salinities can exceed 52.0 ‰ and peak up to 80.0 ‰ (Sevrin-Reyssac 1993). Apart from these extremes, the salinity contrast in the southern BdA and other nearshore areas under upwelling control (BdL; Table 2) restricts stenohaline biota, while euryhaline species (e.g., osmoregulating balanids, cf. Anderson (1994); mollusks, cf. Michel et al. (2011a); and Zostera noltii seagrass meadows, cf. Vermaat et al. (1993)) prosper under such conditions.
Nutrients and photic zone
Trophic-controlled settings with eutrophic conditions are known to influence the formation of chlorozoan versus heterozoan communities in tropical marine environments (Hallock and Schlager 1986; Birkeland 1987; Halfar and Ingle 2003; Halfar et al. 2004, 2006; Pomar et al. 2004; Reijmer et al. 2012). The nutrient availability in the GdA is thus the most important steering factor coupled with the following environmental controls: (1) seasonal trade winds that push the Canary Current south of 21°N, inducing upwelling of nutrients (Mittelstaedt 1991; Sevrin-Reyssac 1993; Barton 1998; Martinez et al. 1999; Pastor et al. 2008); (2) calm water conditions during non-upwelling periods that allow waters to stratify and phytoplankton to grow in the photic layer (Huntsman and Barber 1977) and (3) seasonal offshore-directed winds from the Saharan hinterland providing iron-rich dust as additional fertilizer (Sarnthein and Walger 1974; Sarnthein and Diester-Haass 1977; Brust et al. 2011).
Hence, eutrophic waters play a key role in the ecology of the GdA (see also Fig. 2c, d), particularly in those areas where the plankton-enriched water layers can interact with macrobenthic communities in the shallow BdA (cf. Wolff et al. 1993c). These contact zones were identified at the bank margin along a corridor stretching from north to south between Cap Blanc and Cap Timiris (Fig. 7). Here, the highest Chl-a values occur with peaks of >20 mg/m3 (Chl-a; Fig. 2d). Secchi-disk measurements support the eutrophic to mesotrophic nature of the outer BdA with oligotrophic waters restricted to the innermost shelf where extensive seagrass meadows prosper. This eutrophic environment makes the NW African waters one of the most productive areas of our oceans (Marañón and Holligan 1999). A high biological productivity (cf. Berghuis et al. 1993) is furthermore indicated by the sedimentological record indicating largely dysoxic and aphotic conditions in the outer shelf of the GdA. Such limiting settings hamper the development of photoautotrophic carbonate biota (e.g., zooxanthellate corals, calcareous green algae, photosymbiont-bearing foraminifera), while filter-feeding, light-independent marine organisms prosper. Profiteers are fast growing high nutrient-related mollusks (e.g., chemoautotrophs; cf. Michel et al. 2011a), filter-feeding balanids and bryozoans; cf. Klicpera et al. 2013, 2014).
Thermocline and hydrodynamic regime
CTD casts taken in the proximal outer shelf and bank environment (topographic nomenclature cf. Hanebuth et al. 2013) show a poor water stratification throughout due to water depths of largely <30 mbsl (Table 1). In addition, offshore-directed winds and a M2-type tidal regime (principal lunar semi-diurnal with amplitudes averaging at 1.61 m; Wolff and Smit 1990) result in strong bank-top currents (velocities of >3 m s−1), often appearing as a series of stationary waves of up to 1 m in height along the BdA margin (Westphal et al. 2014). These observations agree with local topographic features such as hardgrounds along bank and platform margin, occasionally incised by valleys and large-scale gullies at the BdA margin and in the outer shelf (Fig. 1). Moreover, these features are indicative of a complex oceanography with density currents following topographic contours (Peters 1976). The high-energy setting has also been reported by Sevrin-Reyssac (1993) who related the high diversity of marine environments in the BdA to the complex and strong hydrology. Such hydrological conditions, in particular, make it challenging for marine biota prospering under low-energy regimes, while infaunal or sessile epifaunal filter-feeding taxa benefit from it.
Shelf morphology and substrate
Shelf morphology and substrate relationships were shown in Betzler et al. (1997a, b), Pomar (2001); Pomar and Ward (1995), (1999), and Pomar et al. (2004) to be important drivers of carbonate production. While vast areas of the platform-like northern BdA (Fig. 1, transect A) are covered by mixed carbonate-siliciclastic sands, some exposed Mid-Pleistocene erosion surfaces along the bank margin provide escarpment structures and hardgrounds (details in Hanebuth et al. 2013). Such rare hard substrates meet the ecological requirements of most hardground-related biota (e.g., certain bivalves, balanids, bryozoans) in the GdA and might explain the high amount of balanid grains several tens to up to 100 km away from rocky shoreline (see also Domain 1985; Duineveld et al. 1993; Michel et al. 2011b; Klicpera et al. 2013, 2014).
Towards the southern GdA, the shelf profile turns into a ramp profile (Fig. 1, transect B) with a significant siliciclastic input derived from intertidal settings close-by. The development of a platform in the northern GdA and a ramp in the southern half might be related to different relationships between shelf morphology and biotic settings (see Betzler et al. 1997a, b) or unknown regional differential tectonics (cf. Hanebuth et al. 2013).
Terrigenous influence
Input of terrigenous material into the GdA occurs throughout the year but increases during winter storms attributed to Harmattan trade winds (Holz et al. 2004; Michel et al. 2009; Mulitza et al. 2010). Lying adjacent to and downwind of the Saharan Desert and Sahel zone, the GdA is connected to a large source of silt-sized eolian dust (Sarnthein and Walger 1974; Sarnthein and Diester-Haass 1977; Glaccum and Prospero 1980), and lies beneath the prevailing dust-loaded wind trajectories. D’Almeida (1989) estimated the amount of Saharan dust at 0.6–0.7 Pg (1 Pg = 109 metric tons) year−1, of which about one–third is blown into the North Atlantic Ocean (Duce et al. 1991). The absence of fluvial runoff turns eolian dust into the only terrigenous source of bio-available nutrients (e.g., iron and phosphorous-rich dust; Brust et al. 2011). Winnowing and partitioning lead to redistribution across the shelf and to selective downslope transport along topographically and hydrodynamically defined pathways (Michel et al. 2009; Hanebuth and Henrich 2009). More sand-sized terrestrial input comes from migrating siliciclastic dunes that occupy the coastline bordering the innermost BdA (cf. Mount 1984). Minor amounts of siliciclastics are hydrodynamically reworked submarine paleodunes of which some onshore records are exposed in the Cap Blanc area (Westphal et al. 2014). As a result, resuspended eolian sediments affect most marine habitats in the BdA thus causing reduced water transparencies and aphotic conditions below 2 mbsl. Such settings are restrictive to light-dependent, sessile and slow-growing organisms, not capable to adapt to high sedimentation rates and low light conditions. In contrast, fast-growing soft-bottom dwellers (e.g., certain infaunal mollusks) non-sensitive to high terrestrial loads and aphotic conditions prosper under such setting.
Facies distribution across the entire Golfe d’Arguin
Present biogenic sediments represent a mixture of fresh (Fig. 6c, h; herein called modern) and relict material (Fig. 6a, e; herein called sub-recent) that have been generated in the last several 1,000 years (detailed radiocarbon ages in Michel et al. 2011a). Three large facies belts are distinguished in the GdA: (1) a mollusk-dominated inner shelf facies, locally enriched in (a) bivalves (F1; northern GdA), (b) mud with peloids and aggregates (F3A, intrabank depression) or (c) siliciclastics (F3B, southern GdA and intertidal plains); (2) a bank margin facies characterized by (a) high amounts of balanids and mollusks (F4A) and (b) enrichments in coralline red algae (F4B, southern BdA); and (3) an outer shelf facies showing scattered parautochthonous and allochthonous skeletal material (benthic foraminifers, mollusks, echinoderms) in silty to fine-sandy siliciclastic material (Figs. 7, 8).
Inner shelf facies
The inner shelf shows contrasting marine environments. Bimol grain assemblages (F1) dominate and cover more than 50 % of the inner shelf facies (Fig. 7, Table 5). North of 20°N, the GdA (including bank margin and outer shelf areas) is covered by up to 75 % of sediments referring to the assemblage F1. This pattern coincides with the maximum southward displacement of the Canary Current during winter (Mittelstaedt 1991; Hagen 2001; Pastor et al. 2008), which is known to induce upwelling offshore and thus pushes the primary production. Trajectories of oceanic swell and surface currents suggest that the inner shelf bivalve community is linked to food-enriched waters provided by upwelling (Fig. 7). Such bimol assemblages are also known from other modern upwelling regions such as the Western Sahara shelf (Summerhayes et al. 1976), the southern Australian shelf (James et al. 1992, 2001), the Gulf of California (Halfar et al. 2004, 2006) or the Gulf of Panama (Reijmer et al. 2012) and clearly demonstrate that a high-productive but low-diverse bimol assemblage can exist in low latitudes.
Parts of the innermost shelf (Cuvette d’Arguin, Fig. 1) show increasing water depths (>20 mbsl) with a low-energy mollusk grain assemblage (F3A) dominated by benthic foraminifers, aggregates, and peloid grains in a very fine-grained matrix (Fig. 7, Table 5). These elements indicate calm hydrological conditions below storm wave-base, a setting limited to restricted marine environments in the Cuvette d’Arguin and in the BdL that are protected from oceanic swell (Aleman et al. 2014).
The southern inner shelf facies around Tidra Island is characterized by intertidal conditions with extensive seagrass plains and a dominant siliciclastic input. The sedimentary cover shows an undifferentiated infaunal mollusk grain assemblage (F3B) with high contents of terrestrial quartz grains due to the proximity to the desertic hinterland (Fig. 7, Table 5). Seagrass plains (Zostera noltii) represent the largest primary producer of organic carbon (Wolff and Smit 1990) and provide similarly a rich food resource and habitat for intertidal mollusk and decapod species. The abundant bivalve Anadara senilis, for example, provides a biomass contribution of (8.1 g m−2 ash free dry weight = 48 % of the total tidal flat biomass; Wolff et al. 1993b) thus representing the most important macrobenthic mollusk taxon in the intertidal inner shelf and a main contributor to nearshore bimol assemblages.
Bank margin facies
The facies distribution in the outer BdA shows a dominant barnamol assemblage (F4A; Fig. 7; Table 5) that covers the entire bank margin (10–20 mbsl) along a narrow corridor from the BdL over the central BdA down to the CTS (19.5°N). Exposed Mid-Pleistocene erosion surfaces provide submarine hardgrounds along the bank margin that favor the development of a light-independent and suspension-feeding balanid community, able to cope with strong hydrodynamics and eutrophic conditions. Modern and sub-recent balanid remains (mostly preserved as disarticulated plates) are ubiquitous in all samples from the bank margin and BdL and indicate an important, yet relatively poorly investigated contributor of carbonate. Although barnamol assemblages are usually associated with cool-temperate water regimes (cf. Hayton et al. 1995), balanids are today cosmopolitan players due to human-mediated translocations (Carlton et al. 2011).
Larger bimol grain assemblages (F1, Fig. 7) appear close to upwelling hotspots (south of Cap Blanc and in the CTS area) and indicate high-nutrient settings by an often-dominant appearance of Donax burnupi (1–40 mbsl) and Venus crebrisulca (4–25 mbsl). The ecological requirements of these two species agree with upwelling conditions; they are well known for their high productivity in nutrient-rich waters (cf. Ansell 1983).
Towards the southern BdA, barnamol assemblages are enriched in remains of calcareous red algae (F4B; Fig. 7; Table 5). Although the presence of red algae could not be confirmed by the MSM16-3 cruise, a number of studies provide data on restricted red algae occurrences (Piessens 1979; Koopmann et al. 1979; John et al. 2004). Some even confirm the presence of Maërl-forming taxa (e.g., Lithothamnion sp.; Lithophyllum sp.) in the outer BdA (Birkett et al. 1998; Jackson 2003; Goudswaard et al. 2007). Based on the component analysis of GdA-wide data, red-algal contents remain low (<3 % in the inner BdA) with restricted enrichments of up to >50 % (fractions >500 µm; Fig. 4e) in the southern BdA (Piessens 1979).
Outer shelf facies
The outer shelf (>30 mbsl) shows sediments with a fine-grained quartzose texture and scattered reworked bioclasts of the foramol assemblage (F2; Figs. 4g, h; 7; Table 5). Skeletal grains are largely reworked by biological (e.g., boring sponge Cliona sp.) and physical abrasive processes, implying that the material originates from remote production areas (e.g., bank-, nearshore environments). Such processes were shown in Hallock (1988) to significantly influence carbonate production and accumulation, especially under eutrophic tropical conditions. The outer shelf thus acts as a large-scale depositional plane for parautochthonous and allochthonous skeletal and fine-clastic material (e.g., AMW, TMW; Fig. 8) deposited under comparatively little hydrodynamic activity und below the storm wave-base (Michel et al. 2009). The presence of endobenthic chemosymbiotic bivalves (e.g., Anodontia sp., Solemya togata) in the outer shelf underlines the constraining nature of this environment characterized by an upwelling-induced high productivity with resulting dysoxic and aphotic sea bottom conditions (Figs. 7, 8).
Past and present tropical heterozoan carbonate systems
The sedimentary composition in the GdA largely corresponds to the temperate-water foramol association sensu Lees and Buller (1972). Within this association, distinct heterozoan grain assemblages exist, whose constituents show both, elements typical of extra-tropical carbonates (e.g., mollusks, balanids, bryozoans, foraminifers, red algae), and tropical indicators (e.g., tropical bivalves and gastropods), see Kindler and Wilson (2010) for details. This dichotomy suggests that modern heterozoan carbonate formation in low latitudes (Table 6) is not straightforward, and that classical depositional models sensu Lees and Buller (1972) or James and Clarke (1997) should be used carefully and with critical reflection. As shown in this study, the oceanographic setting largely overprints carbonate formation by seasonally shifting thermal fronts, intermittent mixing processes and an upwelling-induced high-nutrient regime causing low light conditions. Coastal environments, in contrast, are less influenced by upwelling phenomena but show more terrestrial influences.
This ‘atypical’ modern carbonate production is reflected best in the diversity pattern of bivalves representing ubiquitous components in all samples from the GdA. Their biodiversity is remarkably low (approx. 200 species; Michel et al. 2011a, b) compared to other tropical and sub-tropical locations (650–1200 species; Crame 2000), while their composition shows cosmopolitan and endemic NW African and tropical taxa (Table 4, Suppl. 1).
Such a pattern is characteristic of eutrophic marine environments favoring the development of a high productive filter-feeding communities (e.g., bivalves, balanids, bryozoans) that are well adapted to only sporadic food availability and changing hard substrate availability.
Similar heterozoan carbonate environments are known from other modern and ancient settings worldwide (see also Table 6). The careful analysis of carbonate sediments including associated drivers, but also players, ideally on species level, is the key to identify the environmental context and to achieve a robust reconstruction or paleoenvironmental settings. The GdA provides such a valuable example for a world without coral reefs and thus serves as a modern analogue for conditions preserved in the fossil record.
Conclusions
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(1)
Modern heterozoan carbonates in the tropical Golfe d’Arguin off northern Mauritania are characterized by a strong multi-dimensional control that is attributed to upwelling-induced eutrophic settings, low illuminations, and tropical water temperatures governing a shallow-marine carbonate factory (Banc d’Arguin).
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(2)
A characteristic foramol association with distinct bimol and barnamol grain assemblages exists in the shallowest areas. Dominant components are bivalves, balanids, benthic foraminifers and other filter feeders—subordinate components are serpulids, echinoderms, and red algae. Photosymbiotic organisms such as zooxanthellate corals are entirely absent, although the setting is tropical.
-
(3)
By combining new and existent surface sediment data, we could reconstruct the full sediment pattern in the Golfe d’Arguin. Sedimentary components are mixed carbonate–siliciclastic showing a well-adapted, light-independent marine biota whose skeletal remains are organized in six mollusk-dominated assemblages and along three larger facies belts.
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(4)
This modern analogue of a tropical heterozoan carbonate system demonstrates the response of a shallow-marine ecosystem to eutrophication and desertification. Moreover, it clearly demonstrates that a “cool water-related” heterozoan carbonate fauna can exist in low-latitude high-nutrient settings. It thus provides invaluable insights for the classification and interpretation of tropical eutrophic settings in the fossil record and provides an important model for future perspectives in the context of climate change.
References
Acker JG, Leptoukh G (2007) Online analysis enhances use of NASA Earth science data. EOS Trans Am Geophys Union 88:14–17. doi:10.1029/2007EO020003
Aleman N, Certain R, Courp T, et al. (2010) Le Golfe d’Arguin: Carte morpho-bathymétrique 1/250
Aleman N, Certain R, Dia A, Barusseau JP, Courp T (2014) Post-glacial filling of a semi-enclosed basin: the Arguin Basin (Mauritania). Mar Geol 349:126–135
Anderson DT (1994) Barnacles: structure, function, development and evolution. Chapman and Hall, London 357 p
Ansell AD (1983) The biology of the genus Donax. In: McLachlan A, Erasmus T (eds) Sandy beaches as ecosystems. Dr. W. Junk Publishers, The Hague, pp 607–636
Barange M, Field J, Harris R, Hofmann E (2010) Marine ecosystems and global change. Oxford University Press, Oxford
Barton ED (1998) Eastern boundary of the North Atlantic: Northwest Africa and Iberia. In: Robinson AR, Brink KH (eds) The Sea. Wiley, New York, pp 633–657
Barusseau J-P, Vernet R, Saliège J-F, Descamps C (2007) Late Holocene sedimentary forcing and human settlements in the Jerf el Oustani Ras el Sass region (Banc d’Arguin, Mauritania). Géomorph Reli Process Environ 7:7–18
Barusseau J-P, Certain R, Vernet R, Saliège J-F (2010) Late Holocene morphodynamics in the littoral zone of the Iwik Peninsula area (Banc d’Arguin — Mauritania). Geomorph 121:358–369. doi:10.1016/j.geomorph.2010.05.006
Berghuis EM, Duineveld GCA, Hegeman J (1993) Primary production and distribution of phytopigments in the water column and sediments on the upwelling shelf off the Mauritanian coast (Northwest Africa). Hydrobiologia 258:81–93
Betzler C, Brachert TC, Braga JC, Martin JM (1997a) Nearshore, temperate, carbonate depositional systems (lower Tortonian, Agua Amarga Basin, southern Spain): implications for carbonate sequence stratigraphy. Sediment Geol 113:27–53
Betzler C, Brachert TC, Nebelsick J (1997b) The warm temperate carbonate province: a review of the facies, zonations, and delimitations. Cour Forsch-Inst Senckenberg 201:83–99
Betzler C, Braga JC, Jaramillo-Vogel D, Romer M, Hubscher C, Schmiedl G, Lindhorst S (2011) Late Pleistocene and Holocene cool-water carbonates of the Western Mediterranean Sea. Sedimentology 58:643–669
Birkeland C (1987) Nutrient availability as a major determinant of differences among coastal hard-substratum communities in different regions of the tropics. In: Birkland C (ed) Differences between Atlantic and Pacific tropical marine coastal ecosystems: community structure, ecological processes and productivity. UNESCO Reports in Marine Science, Paris, pp 45–90
Birkett DA, Maggs CA, Dring MJ (1998) Maerl (volume V). An overview of dynamic and sensitivity characteristics for conservation management of marine SACs. Scot Ass Mar Sci (UK Marine SACs Project), pp 1–116. (www.english-nature.org/uk-marine/reports/pdfs/maerl.pdf)
Blott SJ, Pye K (2001) GRADISTAT: a grain size distribution and statistics package for the analysis of unconsolidated sediments. Earth Surf Proc Land 26:1237–1248
Blott SJ, Croft DJ, Pye K et al (2004) Particle size analysis by laser diffraction. Geol Soc Lond Spec Publ 232:63–73. doi:10.1144/GSL.SP.2004.232.01.08
Brandano M, Corda L (2002) Nutrients, sea level and tectonics: constrains for the facies architecture of a Miocene carbonate ramp in central Italy. Terra Nova 14:257–262
Brandano M, Frezza V, Tomassetti L, Cuffaro M (2009) Heterozoan carbonates in oligotrophic tropical waters: the Attard member of the lower coralline limestone formation (Upper Oligocene, Malta). Palaeogeogr Palaeoclimatol Palaeoecol 274:54–63. doi:10.1016/j.palaeo.2008.12.018
Brust J, Schulz-Bull DE, Leipe T, Chavagnac V, Waniek JJ (2011) Descending particles: from the atmosphere to the deep ocean–a time series study in the subtropical NE Atlantic. Geophys Res Lett 38:L06603. doi:10.1029/2010gl045399
Carlton JT, Newman WA, Pitombo FB (2011). In the wrong place—alien marine crustaceans: distribution, biology and impacts. Springer Netherlands, Dordrecht. doi:10.1007/978-94-007-0591-3
Chave K (1967) Recent carbonate sediments: an unconventional view. Geol Educ 5:200–204
Crame JA (2000) Evolution of taxonomic diversity gradients in the marine realm: evidence from the composition of recent bivalve faunas. Paleobiology 26:188–214
Cushman JA (1927) Recent foraminifera from off the west coast of America. Scripps Institute for Oceanography. Bull Tech Ser 1(10):119–188
Cuq F (1993) Remote sensing of sea surface and coastal features in the area of the Golfe d’Arguin, Mauritania. Hydrobiologia 258:33–40
D’Almeida GA (1989) Desert aerosol: characteristics and effects on climate. In: Leinen M, Sarnthein M (eds) Palaeoclimatology and palaeometeorology: modern and past patterns of global atmospheric transport. Kluwer Academic Publishers, Dordrecht, pp 311–338
Domain F (1985) Carte sédimentologigue du plateu continental Mauretanien 1:200.000. Nouadhibou
Doney SC, Ruckelshaus MJ, Duffy E et al (2012) Climate change impacts on marine ecosystems. Ann Rev Mar Sci 4:11–37. doi:10.1146/annurev-marine-041911-111611
Duce RA, Liss PS, Merrill JT, Atlas EL, Buat-Menard P (1991) The atmospheric input of trace species to the world ocean. Global Biochem Cycles 5:193–259
Duineveld GCA, De Wilde PAWJ, Berghuis EM, Kok A (1993) The benthic infauna and benthic respiration off the Banc d’Arguin (Mauritania, Northwest Africa). Hydrobiologia 258:107–117
Edinger EN, Copper P, Risk MJ, Atmojo W (2002) Oceanography and reefs of recent and Paleozoic tropical epeiric seas. Facies 47:127–149
Einsele G, Herm D, Sarnthein M, Schwarz HU (1972) Bericht über die Landesexpedition nach Senegal und Mauretanien in Ergänzung zur Meteorfahrt 25/71. Techn Bericht Deutsche Forschungsgemeinschaft, 28 p
Flügel E (2010) Microfacies of carbonate rocks: analysis, interpretation and application. Springer, Berlin
Fourqurean JW, Duarte CM, Kennedy H et al (2012) Seagrass ecosystems as a globally significant carbon stock. Nat Geosci 5:505–509. doi:10.1038/ngeo1477
Gattuso JP, Hansson L (2011) Ocean acidification. Oxford University Press, Oxford
Gilman EL, Ellison J, Duke NC, Field C (2008) Threats to mangroves from climate change and adaptation options: a review. Aquat Bota 89:237–250. doi:10.1016/j.aquabot.2007.12.009
Glaccum RA, Prospero JM (1980) Saharan aerosols over the tropical north Atlantic. Miner Mar Geol 37:295–321
Goudswaard PC, Smaal AC, Wagué A (2007) The ecological implications of exploitation of the bivalve Venus rosalina in Mauritanian waters, Report No. C124A-07.Wageningen Imares, Amsterdam, 132 p
Gould HR, Steward RH (1956) Continental terrace sediments in the northeastern Gulf of Mexico. In: Hough JL, Menard HW (eds) Finding ancient shore lines, vol 3. SEPM Spec Publ, Mexico, pp 2–19
Gruvel A (1912) Mission Gruvel sur la cote occidentale d’Afrique (1909–1910) et collection du Museum d’histoire naturelle Les Cirrhipedes. Bull Mus Hist Nat Paris 18:344–350
Hagen E (2001) Northwest African upwelling scenario. Oceanol Acta 24:113–128
Halfar J, Ingle JC Jr (2003) Modern warm-temperate and subtropical shallow-water benthic foraminifera of the Southern Gulf of California, Mexico. J Foram Res 33:309–329
Halfar J, Godinez-Orta L, Mutti M et al (2004) Nutrient and temperature controls on modern carbonate production: an example from the Gulf of California, Mexico. Geology 32:213–216. doi:10.1130/G20298.1
Halfar J, Godinez-Orta L, Mutti M, Valdez-Holguin JE, Borges JM (2006) Carbonates calibrated against oceanographic parameters along a latitudinal transect in the Gulf of California, Mexico. Sedimentology 53:297–320
Hallock P (1988) The role of nutrient availability in bioerosion: consequences to carbonate buildups. Palaeogeogr Palaeoclimatol Palaeoecol 63:275–291
Hallock P (2005) Global change and modern coral reefs: new opportunities to understand shallow-water carbonate depositional processes. Sediment Geol 175:19–33. doi:10.1016/j.sedgeo.2004.12.027
Hallock P, Schlager W (1986) Nutrient excess and the demise of coral reefs and carbonate platforms. Palaios 1:389–398
Hallock P, Hine AC, Vargo GA, Elrod JA, Jaap WC (1988) Platforms of the Nicaraguan rise: examples of the sensitivity of carbonate sedimentation to excess trophic resources. Geology 16:1104–1107
Hanebuth TJJ, Henrich R (2009) Recurrent decadal-scale dust events over Holocene western Africa and their control on canyon turbidite activity (Mauritania). Quat Sci Rev 28:261–270. doi:10.1016/j.quascirev.2008.09.024
Hanebuth TJJ, Lantzsch H (2008) A Late Quaternary sedimentary shelf system under hyperarid conditions: unravelling climatic, oceanographic and sea-level controls (Golfe d’Arguin, Mauritania, NW Africa). Mar Geol 256:77–89. doi:10.1016/j.margeo.2008.10.001
Hanebuth TJJ, Mersmeyer H, Kudrass HR, Westphal H (2013) Aeolian to shallow-marine shelf architecture off a major desert since the Late Pleistocene (northern Mauritania). Geomorphology 203:132–147
Hayton S, Nelson C, Hood S (1995) A skeletal assemblage classification system for non-tropical carbonate deposits based on New Zealand Cenozoic limestones. Sediment Geol 100:123–141
Hoegh-Guldberg O, Mumby PJ, Hooten J et al (2007) Coral reefs under rapid climate change and ocean acidification. Science 318:1737–1742. doi:10.1126/science.1152509
Holz C, Stuut JW, Henrich R (2004) Terrigenous sedimentation processes along the continental margin off NW Africa: implications from grain-size analysis of seabed sediments. Sedimentology 51:1145–1154
Huntsman SA, Barber RT (1977) Primary production off northwest Africa: the relationship to wind and nutrient conditions. Deep-Sea Res 24:25–33
IMROP (2013) Atlas maritime des zones vulnérables en Mauritanie—Un appui à la gestion écosystémique et équitable. IMROP, Nouhadibou 156 p
Jackson A (2003) BIOTIC species information for Lithothamnion corallioides. (http://www.marlin.ac.uk/biotic/)
James NP, Clarke JAD (1997) Cool-water carbonates, vol 56. SEPM Spec Publ, London, pp 1–440
James NP, Bone Y, Von der Borch CC, Gostin VA (1992) Modern carbonate and terrigenous clastic sediments on a cool-water, high-energy, mid- latitude shelf: lacepede, southern Australia. Sedimentology 39:877–903
James NP, Bone Y, Collins LB, Kyser TK (2001) Surficial sediments of the Great Australian Bight: facies dynamics and oceanography on a vast cool-water carbonate shelf. J Sediment Res 71:549–567
John DM, Prud’homme van Reine WF, Lawson GW, Kostermans TB, Price JH (2004) A taxonomic and geographical catalogue of the seaweeds of the western coast of Africa and adjacent islands. Beih Nova Hedwigia 127:1–139
Kindler P, Wilson MEJ (2010) Carbonate grain associations: their use and environmental significance, a brief review. In: Mutti M, Piller WE, Betzler C (eds) Carbonate systems during the Oligocene-Miocene climate transition. International Association of Sedimentologists Special Publications Wiley-Blackwell, Chichester (West Sussex), pp 35–48
Kirkpatrick R, Metzelaar J (1922) On an instance of Commensalism between a Hermit Crab and a Polyzoon. Proc Zool Soc London 92(4):983–990
Klicpera A, Taylor PD, Westphal H (2013) Bryoliths constructed by bryozoans in symbiotic associations with hermit crabs in a tropical heterozoan carbonate system, Golfe d’Arguin, Mauritania. Mar Biodiv 43:429–444. doi:10.1007/s12526-013-0173-4
Klicpera A, Taylor PD, Westphal H (2014) Bryozoans on the move: adaptations to hard substrate-limiting tropical heterozoan carbonates (Banc d’Arguin, Mauritania). Mar Biodiv. doi:10.1007/s12526-014-0279-3
Koopmann BJ, Sarnthein M, Schrader H (1978) Sedimentation influenced by upwelling in the subtropical Baie du Levrier (West Africa). In: Boje R, Tomczak M (eds) Proceeding of III International Symposium on upwelling ecosystems. Springer Verlag, New York, pp 282–288
Koopmann BJ, Lees A, Piessens P, Sarnthein M (1979) Skeletal carbonate sands and wind-derived silty marls off the Saharan coast: Baie du Léevrier, Arguin Platform, Mauritania. Meteor Forsch-Ergebn C:15–57
Lees A, Buller AT (1972) Modern temperate-water and warm-water shelf carbonate sediments contrasted. Mar Geol 13:M67–M73
Logan BW, Harding JL, Ahr WM, Williams JD, Snead RG (1969) Late quaternary sediments of Yucatan Shelf, Mexico. In: Bass MN, DE Cebulski, McBirney AR (eds) Carbonate sediments and reefs. Yucatan Shelf, Mexico, vol 11. AAPG Mem, Oklahoma, pp 5–128
Maigret J (1972) Campagnes expérimentale de pêche des sardinelles et autres espèces pélagiques (juillet, 1970–octobre 1971). Tome I. Observations concernant l’océanographie et la biologie des espèces. Sec Stat Aff Etrang France; Mis Pêche et Mar March; Mauritanie. SCET- International, BCE P 083, Paris, 140 p
Marañón E, Holligan PM (1999) Photosynthetic parameters of phytoplankton from 50 N to 50 S in the Atlantic Ocean. Mar Ecol Progr Ser 176:191–203
Martín JM, Braga JC, Betzler C, Brachert T (1996) Sedimentary model and high-frequency cyclicity in a Mediterranean, shallow-shelf, temperate-carbonate environment (uppermost Miocene, Agua Amarga Basin, southern Spain). Sedimentology 43:263–277
Martín JM, Braga JC, Betzler C (2001) The Messinian Guadalhorce corridor: the last northern, Atlantic-Mediterranean gateway. Terra Nova 13:418–424
Martinez P, Bertrand P, Shimmield GB et al (1999) Upwelling intensity and ocean productivity changes off Cape Blanc (northwest Africa) during the last 70,000 years: geochemical and micropalaeontological evidence. Mar Geol 158:57–74
Michel J, Westphal H, Hanebuth TJJ (2009) Sediment partitioning and winnowing in a mixed eolian-marine system (Mauritanian shelf). Geo-Marine Lett 29:221–232. doi:10.1007/s00367-009-0136-8
Michel J, Vicens GM, Westphal H (2011a) Modern heterozoan carbonates from a eutrophic tropical shelf (Mauritania). J Sediment Res 81:641–655. doi:10.2110/jsr.2011.53
Michel J, Westphal H, Von Cosel R (2011b) The mollusk fauna of soft sediments from the tropical, upwelling-influenced shelf of Mauritania (northwestern Africa). Palaios 26:447–460. doi:10.2110/palo.2010.p10-148r
Mikhalevich VI (1975) Novyj rod I vid Foraminifer (Foraminifera, Textulariidae) u zapadnogo poberezhja Afriki. Vestnik zoologii 1:86–87
Mittelstaedt E (1991) The ocean boundary along the northwest African coast: circulation and oceanographic properties at the sea surface. Progr Oceanogr 26:307–355. doi:10.1016/0079-6611(91)90011-A
Mount JF (1984) Mixing of siliciclastic and carbonate sediments in shallow shelf environments. Geology 12:432–435
Mulitza S, Heslop D, Pittauerova D et al (2010) Increase in African dust flux at the onset of commercial agriculture in the Sahel region. Nature 466:226–228. doi:10.1038/nature09213
Müller G, Gastner M (1971) The “Karbonate-Bombe”, a simple device for the determination of the carbonate content in sediments, soils and other materials. N Jb Miner Mh 10:446–469
Mutti M, Hallock P (2003) Carbonate systems along nutrient and temperature gradients: some sedimentological and geochemical constraints. Int J Earth Sci 92:465–475. doi:10.1007/s00531-003-0350-y
Myers N, Mittermeier RA, Mittermeier CG et al (2000) Biodiversity hotspots for conservation priorities. Nature 403:853–858. doi:10.1038/35002501
Nelson CS (1988) An introductory perspective on non-tropical shelf carbonates. Sediment Geol 60:3–12
Nelson CS, Keane SA, Philip SH (1988) Non-tropical carbonate deposits on the modern New Zealand shelf. Sediment Geol 60:71–94
Ould Dedah S (1993) Wind, surface water temperature, surface salinity and pollution in the area of the Banc d’Arguin, Mauritania. Hydrobiologia 258:9–19
Ould Mahfoudh MOTS, Dobrovine B, Ould Dedah S (1991) Atlas hydrologique des eaux superficielles du Banc d’Arguin. Département Ressources et Environment et Laboratoire d’Hydrologie et Environment, Centre National de Recherches Oceanographiques et des Peches (IMROP). http://hdl.handle.net/1834/518
Pastor M, Pelegri J, Hernandezguerra A et al (2008) Water and nutrient fluxes off Northwest Africa. Cont Shelf Res 28:915–936. doi:10.1016/j.csr.2008.01.011
Perry C, Taylor K (2009) Environmental sedimentology. Wiley, New York
Peters H (1976) The spreading of the water masses of the Banc d’Arguin in the upwelling area off the northern Mauritanian coast. Meteor Forsch Ergebn 18:78–100
Piessens P (1979) Influence relative des sources de production et du transport dans la formation de faciès calcaires biogéniques: les sédiments quaternaires de la plate-forme d’Arguin (Mauritanie) et comparaison avec des régions côtières européennes (Irlande et Hébrides). Ph.D. thesis, Université Catholique de Louvain, Louvain-la-Neuve, 133 p
Piessens P, Chabot AG (1977) Bathymetry and sediments of the Arguin Platform, Mauritania, West Africa. Mém Inst Géol Univ Louvain 29:369–379
Pomar L (2001) Types of carbonate platforms: a genetic approach. Basin Res 13:313–334. doi:10.1046/j.0950-091x.2001.00152.x
Pomar L, Ward W (1995) Sea-level changes, carbonate production and platform architecture: the Llucmajor platform, Mallorca, Spain. Sequence stratigraphy and depositional response to eustatic, tectonic and climatic forcing. Academic Press, Dordrecht, p 87
Pomar L, Ward W (1999) Reservoir-scale heterogeneity in depositional packages and diagenetic patterns on a reef-rimmed platform, upper Spain Miocene, Mallorca. Bull AAPG 83:1759–1773
Pomar L, Brandano M, Westphal H (2004) Environmental factors influencing skeletal grain sediment associations: a critical review of Miocene examples from the western Mediterranean. Sedimentology 51:627–651. doi:10.1111/j.1365-3091.2004.00640.x
Prévost (1746) Carte de la Coste occidentale d’Afrique Depuis le Cap Blanc jusqu’a Tanit
Proske U, Hanebuth TJJ, Meggers H, Leroy SAG (2008) Tidal flat sedimentation during the last millennium in the northern area of Tidra Island, Banc d’Arguin, Mauritania. J Afr Earth Sci 50:37–48. doi:10.1016/j.jafrearsci.2007.09.002
Reijmer JJG, Bauch T, Schäfer P (2012) Carbonate facies patterns in surface sediments of upwelling and non-upwelling shelf environments (Panama, East Pacific). Sedimentology 59:32–56. doi:10.1111/j.1365-3091.2010.01214.x
Reymond CE, Mateu-Vicens G, Westphal H (2014) Foraminiferal assemblages from a transitional tropical upwelling zone in the Golfe d’Arguin, Mauritania. Estuar Coast Shelf Sci 148:70–84. doi:10.1016/j.ecss.2014.05.034
Samankassou E (2002) Cool-water carbonates in a paleoequatorial shallow-water environment: the paradox of the Auernig cyclic sediments (Upper Pennsylvanian, Carnic Alps, Austria-Italy) and its implications. Geology 30:655–658
Sarnthein M, Diester-Haass L (1977) Eolian-sand turbidites. J Sediment Petrol 47:868–890
Sarnthein M, Walger E (1974) Der äolische Sandstrom aus der W-Sahara zur Atlantikküste. Geol Rdsch 63:1065–1087
Schäfer P, Fortunato H, Bader B, Liebetrau V, Bauch T, Reijmer JJG (2011) Growth rates and carbonate production by coralline red algae in upwelling and non-upwelling settings along the Pacific coast of Panama. Palaios 26:420–432
Schlitzer R (2012) Ocean Data View (ODV). http://odv.awi.de
Scholle PA, Bebout DG, Moore CH (1983) Carbonate depositional environments. AAPG Mem 33:1–708
Sevrin-Reyssac J (1993) Hydrology and underwater climate of the Banc d’Arguin, Mauritania: a review. Hydrobiologia 258:1–8
Solomon S (2007) Climate Change 2007: The Physical Science Basis: Contributions of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change (IPCC). Cambridge University Press, Cambridge
Summerhayes CP, Milliman JD, Briggs SR, Bee AG, Hogan C (1976) Northwest African shelf sediments: influence of climate and sedimentary processes. J Geol 84:277–300
Taylor GT, Muller-Karger FE, Thunell RC et al (2012) Ecosystem responses in the southern Caribbean Sea to global climate change. Proc Nat Acad Sci USA 109:19315–19320. doi:10.1073/pnas.1207514109
Van Camp L, Nykjaer L, Mittelstaedt E, Schlittenhardt P (1991) Upwelling and boundary circulation off Northwest Africa as depicted by infrared and visible satellite observations. Progr Oceanogr 26:357–402
Vermaat JE, Beijer JAJ, Gijistra R et al (1993) Leaf dynamics and standing stocks of intertidal Zostera noltii Hornem. and Cymodocea nodosa (Ucria) Ascherson on the Banc d’Arguin (Mauritania). Hydrobiologia 258:59–72
Ward JH Jr (1963) Hierarchical grouping to optimize an objective function. J Am Statist Ass 58(301):236–244
Wentworth CK (1922) A scale of grade and class terms for clastic sediments. J Geol 30:377–392
Westphal H, Freiwald A, Hanebuth T, and cruise participants (2007) Report and preliminary results of Poseidon cruise 346, MACUMA. Las Palmas (Spain)—Las Palmas (Spain), 28.12.2006—15.1.2007. Berichte Univ Bremen No. 260:1–49
Westphal H, Halfar J, Freiwald A (2010) Heterozoan carbonates in subtropical to tropical settings in the present and past. Int J Earth Sci 99:153–169. doi:10.1007/s00531-010-0563-9
Westphal H, Beuck L, Braun S, Freiwald A, Hanebuth TJJ, Hetzinger S, Klicpera A, Kudrass H, Lantzsch H, Lundälv T, Vicens GM, Preto N, Reumont J, Schilling S, Taviani M, Wienberg V (2014) PHAETON–Paleoceanographic and paleoclimatic record on the Mauritanian Shelf–Cruise No. MSM16/3–October 13–November 20, 2010, Bremerhaven (Germany)–Mindelo (Cap Verde). MARIA S. MERIAN-Berichte, MSM16/3, DFG-Senatskomm Ozeanogr, 57 p doi:10.2312/cr_msm16_3
Wolff WJ, Smit CJ (1990) The Banc d’Arguin, Mauritania as an environment for coastal birds. Ardea 78:17–38
Wolff WJ, Van der Land J, Nienhuis PH, De Wilde PAWJ (1993a) Ecological studies in the coastal waters of Mauritania. Hydrobiologia 258:vii–ix
Wolff WJ, Duiven AG, Duiven P et al (1993b) Biomass of macrobenthic tidal flat fauna of the Banc d’Arguin, Mauritania. Hydrobiologia 258:151–163
Wolff WJ, Land J, Nienhuis PH, De Wilde PAWJ (1993c) The functioning of the ecosystem of the Banc d’Arguin, Mauritania: a review. Hydrobiologia 258:211–222
Wright V, Burgess P (2005) The carbonate factory continuum, facies mosaics and microfacies: an appraisal of some of the key concepts underpinning carbonate sedimentology. Facies 51:19–25
Acknowledgments
Participants and crew of the Maria S. Merian Cruise MSM-16 leg 3 are acknowledged for providing support. We are grateful to the Mauritanian authorities for their permission to carry out research in their territorial waters. Many thanks are due to Abdoul Dia from the Mauritanian Institute for Oceanographic Research (IMROP) for his collaboration during the cruise and to the Programme Biodiversité, Gaz, Pétrole (BGP) for additional data. Thanks to Michael Sarnthein (University of Kiel) for providing historical sample material. Nicolas Aleman and Raphaël Certain (both CEFREM, Perpignan) are acknowledged for additional bathymetric data. The manuscript benefited immensely from reviews by Franz T. Fürsich (GeoZentrum Nordbayern) and one anonymous reviewer. The DFG Senate Commission on Oceanography is thanked for providing funding for the research cruise to HW. This project was partially funded through the DFG Research Center/Cluster of Excellence MARUM (Sediment Dynamics, SD2) and is part of the PhD thesis of AK.
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Klicpera, A., Michel, J. & Westphal, H. Facies patterns of a tropical heterozoan carbonate platform under eutrophic conditions: the Banc d’Arguin, Mauritania. Facies 61, 421 (2015). https://doi.org/10.1007/s10347-014-0421-5
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DOI: https://doi.org/10.1007/s10347-014-0421-5