ICES Journal of Marine Science (2011), 68(3), 427 –435. doi:10.1093/icesjms/fsr005 Sediment accumulation and bioturbation rates in the deep Northeast Atlantic determined by radiometric techniques Fernando P. Carvalho*, João M. Oliveira, and António M. M. Soares Instituto Tecnológico e Nuclear, E.N. 10, 2686-953 Sacavém, Portugal *Corresponding author: tel: +351 219 946332; fax: +351 219 941995; e-mail: [email protected]. Carvalho, F. P., Oliveira, J. M., and Soares, A. M. M. 2011. Sediment accumulation and bioturbation rates in the deep Northeast Atlantic determined by radiometric techniques. – ICES Journal of Marine Science, 68: 427 –435. Received 1 September 2009; accepted 8 January 2011. The upper layers of boxcore bottom-sediment samples from the Porcupine Abyssal Plain (five cores) and from the Iberian Abyssal Plain (eight cores) in the Northeast Atlantic were analysed for porosity, grain size, organic carbon, calcium carbonate, and radionuclides. Radiometric ages of sediment layers were determined using 230Th excess (the 230Thexc/232Th ratio method) and 14C radionuclides. Sediment accumulation rates were 0.14 and 3.2 cm kyear21 at the Porcupine and Iberian Abyssal Plains, respectively. Sediment mixing, determined through 210Pb excess, was in the upper 5– 11 cm sediment layer, likely as a result of infauna activity. Biodiffusion coefficients averaged 0.40 + 0.37 and 1.05 + 1.02 cm2 year – 1 and were not significantly different in the sediments of either abyssal plain. The low rates of sediment accumulation and bioturbation in the abyssal depths of the Northeast Atlantic suggested that immobilization of sediment-reactive man-made radionuclides released near the seafloor will take place very slowly and with limited sediment burial. Keywords: biodiffusion, 14 C sediment dating, 210 Pb, sediment mixing, Introduction Over several decades, low- and medium-activity-level radioactive wastes were dumped into the Northeast Atlantic. Disposal of radioactive waste ceased with the 1982 revision of the London Sea Dumping Convention that banned the practice (NEA/ OECD, 1984; Livingston and Povinec, 2000). Drums containing radioactive waste are not expected to retain their content for ever and may leak. Particle reactive radionuclides released into the seawater should be adsorbed by the downward flux of particles and buried in the seafloor around the dumpsites (NEA/OECD, 1984; Povinec et al., 2000). The extent of contaminant burial vs. long-range transport in the water column may depend on the balance between, on one hand, sedimentation rate and sediment mixing rate and, on the other hand, ocean currents. The abyssal depths, below 2000 m deep, cover .60% of the Earth surface, but their biology, geology, and hydrography are poorly known. The supply of sediments and organic matter to the deep ocean and their recycling on the seafloor have been a subject of continued research closely related to the fate of radionuclides and other contaminants in the deep sea (Fowler and Knauer, 1986; Ståhl et al., 2004; Lampitt et al., 2008). The flux of particles exported from the euphotic zone of the ocean to the abyss is a key factor in these oceanographic processes. The settling of these particles on the seafloor is part of the sedimentation processes that may counteract the release and diffusion of radioactive contaminants into the water column and, ultimately, may bury and immobilize pollutants contributing to their removal from the biosphere. As an essential part of these processes, sediment accumulation and mixing were investigated using radionuclide-based geochronology in two areas of the Northeast Atlantic Ocean in which radioactive # 2011 230 Th excess sediment dating. wastes were dumped. These areas are the Porcupine Abyssal Plain, at the NEA dumpsite, and the Iberian Abyssal Plain off the Portuguese coast. Results of these geochronologies are presented herein, and implications related to the fate of dumped radionuclides are discussed. Material and methods Sediment sampling Sampling areas are shown in Figure 1. Sediment samples were collected during oceanographic cruises on board the German RV “Walther Herwig” in 1989 to the NEA dumpsite in the Porcupine Abyssal Plain and the Portuguese RV “A. Carvalho” in 1988 to the Iberian Abyssal Plain, using large surface–sediment boxcorers. Two sets of sediment cores were selected for analysis based on the on-board inspection of the core sediment surface and their assessment as undisturbed core samples. Sediments were subsampled from the boxcorer by inserting a stainless steel tube 12 cm in diameter by hand. Sediment subsamples were extruded on board, sliced in 1- or 2-cm layers, and frozen until analysis. Following the determination of sediment water content, samples were analysed for porosity, grain size, organic matter, and carbonate content, according to wellestablished analytical procedures (Strickland and Parsons, 1968). Radionuclide analyses Aliquots of sediment layers were analysed for several radionuclides by radiochemistry and a-spectrometry. Thorium isotopes were determined to use the activity ratio of 230Th excess, the 230 Thexc (230Th physical half-life T1/2 ¼ 8.0 × 104 years) over 232 Th (T1/2 ¼ 1.41 × 1010 years) as a geochronometer. Uranium International Council for the Exploration of the Sea. Published by Oxford Journals. All rights reserved. For Permissions, please email: [email protected] 428 F. P. Carvalho et al. Figure 1. The Northeast Atlantic and the areas investigated: the NEA dumpsite is in the Porcupine Abyssal Plain, and the “Cecir X” area in the Iberian Abyssal Plain. isotopes (238U and 234U), radium 226Ra (T1/2 ¼ 1600 years), and radioactive lead 210Pb (T1/2 ¼ 22.2 years), determined through the a-emitter granddaughter polonium isotope 210Po (T1/2 ¼ 138.4 d), were also analysed. For the purpose, each sample was spiked with known quantities of isotopic tracer (232U, 229Th, 224 Ra, and 209Po) to be used as internal standards for the determination of radiochemical yield (Carvalho et al., 2005). After the addition of tracers, samples were totally dissolved with HNO3, HCl, HF, and a few drops of H2O2. Following separation and purification of radioelements, each was electroplated on stainless steel discs, or a silver disc for Po, and measured by a-spectrometry with silicon surface-barrier detectors ORTEC EG&G (Carvalho and Oliveira, 2007). Aliquots of sediment layers were subject to radiocarbon dating using the carbonate fraction. To eliminate any contamination, 30% by weight of each sample was discarded by controlled acid leaching (0.5 M HCl at 258C). The 14C content was measured by the liquid scintillation technique, using low background Liquid Scintillation Counters (Beckman and Packard) as described elsewhere (Soares, 1989, 2005). Stable isotope enrichment values (d 13C) were determined for the CO2 gas produced at the initial stage of benzene synthesis. Radiocarbon ages were calculated in accord with the definitions recommended by Stuiver and Polach (1977). 14 C sediment dating 14 C of cosmogenic origin enters the ocean at the surface, is incorporated in authigenic CaCO3, and settles with carbonate particles from decaying planktonic organisms (Kershaw, 1985; Thomson et al., 1993, 2000). These particles end on the seafloor, and their cosmogenic 14C content allows for the age determination of sediment layers. For the Iberian Abyssal Plain, core C5 was used for 14 C carbonate dating. Experimental 14C age points below the sediment surface mixed layer (SML) were used to fit a straight line formally similar to Equation (1) to determine the sedimentation rate. 230 Thexc/232Th sediment dating 232 Th, the parent radionuclide of the thorium radioactive natural series, exists everywhere in the seafloor as well as in the Earth crust (Ivanovich and Harmon, 1992). 230Th also exists as a member of the uranium (238U) radioactive natural series. Through sediment layers, the activity ratio 230Th/232Th could be expected to be constant, reflecting the 238U/232Th activity ratios. However, in the upper layers of seafloor sediments, an excess of 230Th exists as a result of the deposition of sedimentary particles carrying 230Th from the 234U decay in the water column. The 230Thexc/232Th activity ratio in the sediments can be used to determine sedimentation rates (Ivanovich and Harmon, 1992). In sediments of the 429 Sediment accumulation and bioturbation rates in the deep NE Atlantic Porcupine Abyssal Plain, the 230Thexc/232Th ratio method was applied to determine the sedimentation rate in the core WH2. The 230Thexc/232Th ratio experimental points located below the SML, defined by subjective graphic analysis, were fitted by least squares to the equation AR(x) l x , = AR(0) exp − v (1) where AR(x) is the 230Thexc/232Th activity ratio at sediment depth x below the sediment surface, l the 230Th radioactive decay constant, and v the sedimentation rate (cm year21; Lalou, 1982; Thomson et al., 2006). The age of the SML (TML) and the extrapolated age of the sediment at the surface (T0) were determined according to the expression T0 = TML − Pbexc and sediment bioturbation C(x) l 1/2 = C(0) exp − x , DB (2) with C(x) equal to 210Pbexc activity at depth x (cm) below the water–sediment interface, l the 210Pb radioactive decay constant, and DB the biodiffusion rate (Erlenkeuser, 1980; De Master and Cochran, 1982; Kershaw et al., 1986). Table 1. Location, depth, 210 (3) where v is the sedimentation rate (cm year21) calculated from the 14 C profile below the mixed layer, and L (cm) is the mixed layer depth determined by the 210Pbexc. As the activity of 210Pbexc accumulated in the sediments is maintained by the continuous supply of 210Pb with the sedimenting particles that compensates 210Pbexc radioactive decay, the steady-state inventory of 210Pbexc can be expressed through 210 All sediment samples were analysed for 210Pb and 226Ra. Without 210 Pb accretion and removal in seafloor sediments, the 226Ra and 210 Pb activities should be in radioactive equilibrium. However, owing to the downward transport of 210Pb originated from the 226 Ra decay in the water column, there is a net excess of 210Pb relative to 226Ra in the upper layers of sediments. If sediments are not disturbed, freshly deposited 210Pb would remain in the top sediment layer, and the layers underneath would display an exponential decrease in 210Pbexc through a layer of which the thickness would depend on the sediment accumulation rate. In undisturbed abyssal sediments, the 210Pbexc would remain in the most superficial layer. The 210Pbexc over 226Ra, i.e. the unsupported 210Pb in the upper layers of bottom sediments, allowed for determining the biologically induced mixing of sediment, also called biodiffusion. Biodiffusion rates were calculated from the equation L , v IPbexc = A[1 − exp(−lPb )], (4) where IPbexc is the inventory of unsupported 210Pb in the sediment cores (Bq m22), A the annual flux of unsupported 210Pb in the particle flux arriving at the seafloor (Bq m22 year21), and lPb the radioactive decay constant of 210Pb. Results and discussion Characteristics of sediments and radionuclide profiles Two sets of sediment cores from the Iberian and Porcupine Abyssal Plains were analysed for radionuclides and sedimentological parameters (Table 1). Sediments from the Porcupine Abyssal Plain were calcareous ooze with high carbonate content, 82 – 88% dry weight, of pelagic origin. The organic matter content of these sediments was very low, 0.28 –0.40% dry weight in the top 1 cm, decreasing rapidly in deeper sediment layers. Sediments from the Iberian Abyssal Plain had a greater contribution of material from the continental margin, with fine sands and clays accounting, respectively, for 5 –51 and 17– 45% dry weight of the top 1 cm. In those sediments, carbonates accounted only for 25 –40% dry weight and organic matter for 0.20 –0.60% dry weight in the upper 1 cm. The main features in the abyssal sediments are illustrated with two core profiles in Figure 2. In the upper 6 –8 cm of sediment, the Pbexc inventory, 210Pb deposition rate, and biodiffusion rates in the sediment cores. Core Position Iberian Abyssal Plain C1 41840′ N 11855′ W C2 41840′ N 10855′ W C3 41840′ N 10805′ W C5 40850′ N 11855′ W C6 40850′ N 10855′ W C7 40850′ N 10805′ W C9 40800′ N 11855′ W C11 40800′ N 10855′ W x + 1 s.d. Porcupine Abyssal Plain WH2 45807.8′ N 17812.3′ W WH2B 45807.8′ N 17812.3′ W WH1A 46807.0′ N 16842.1′ W WH22B 46803.9′ N 16802.2′ W WH26B 46824.5′ N 16841.3′ W x + 1 s.d. Depth (m) I 210Pbexc (Bq m22) 210 Biodiffusion coefficient Pb annual deposition (Bq m22 year21) DB (cm2 year21) r n 3 700 2 750 3 000 5 100 4 500 2 300 5 150 2 350 2 150 3 650 3 260 4 450 3 180 2 220 5 607 3 750 3 533 + 1 063 66 112 100 136 98 67 172 115 108 + 33 0.64 0.29 0.46 0.09 1.26 0.14 0.16 0.16 0.40 + 0.37 20.89 20.90 20.92 20.73 20.70 20.87 20.85 20.81 5 6 5 6 7 4 6 4 4 730 4 730 4 725 4 236 4 540 2 706 3 340 4 397 2 524 3 416 3 242 + 732 83 102 135 78 105 100 + 20 0.14 1.03 0.08 2.91 1.10 1.05 + 1.02 20.85 20.61 20.87 20.86 20.92 9 5 5 6 6 430 F. P. Carvalho et al. Figure 2. Profiles of sediment porosity, organic carbon (Corg), calcium carbonate (CaCO3), 210Pb total, and 226Ra in two sediment cores from the Iberian Abyssal Plain. Top, station C5 (5100 m); bottom, station C9 (5150 m). porosity decreased exponentially from values around 0.85 –0.60 or less, depending on the sediment grain size. The calcium carbonate content was generally lower in the sediment upper layers than in the deeper ones owing to the dissolution of carbonates below the lisocline, which in the Northeast Atlantic is at around 4700 m deep (van der Loeff and Lavaleye, 1984; Rabouille et al., 2001). The organic matter in the sediments was always low, but still comparatively higher in the top few centimetres of sediment than in deeper sediment layers. The radium (226Ra) activity in the upper sediment layers was clearly lower than in deeper sediment layers, probably because of the partial dissolution of radium with carbonates below the lisocline depth, and to changes in the carbonate flux during recent centuries (Rabouille et al., 2001). 210Pb activity in the upper sediment layers was systematically higher than radium activity (Figure 2 and Supplementary Tables S1 and S2). Depending on the core, 210Pb activity became lower than 226Ra activity in sediment layers between 5 and 11 cm below the water–sediment interface and stayed lower in deeper sediment layers (Figures 3 and 4). Recent oceanographic research in the Northeast Atlantic has revealed a significant flux of organic and inorganic debris varying with primary productivity and exported from the euphotic zone to the abyssal floor. The seasonality of this supply is notable and may drive the abundance of populations of benthic organisms (Fabiano et al., 2001; Vanucci et al., 2001; Brunnegård et al., 2004; Smart, 2008; Soto et al., 2010). This particle flux carries particlebound radionuclides, such as 210Pb, 230Th, and 14C, to the seafloor, as demonstrated by sediment traps (Fowler and Knauer, 1986; Rouch, 1987; Lampitt et al., 2008). In abyssal depths, at the water–sediment interface, 94% of the organic particles including phytoplankton debris are used by benthic fauna and rapidly oxidized; just 6% of the deposited organic matter is buried and not used (Heip et al., 2001; Ståhl et al., 2004). Therefore, most of the particulate matter arriving on the abyssal seafloor is 431 Sediment accumulation and bioturbation rates in the deep NE Atlantic Figure 3. 210 Pb excess in sediment cores from the Iberian Abyssal Plain. reprocessed and, with it, probably most of the associated flux of inorganic materials and radioactive elements is processed too, then redistributed in the sediment mixed layer. As the abundance of organic matter in the deposition flux seems to control benthic fauna activity and biomass, it may play an indirect role in controlling sediment mixing and contaminant biodiffusion rates in the seafloor sediment. 14 C sediment dating Sediment dating using 14C of the sediment carbonate fraction was performed in core C5 from the Iberian Basin (Figure 5). The age of core layers yielded a sedimentation rate of 3.2 cm kyear21. The top 5 cm of sediment, not used in fitting the regression, indicated sediment mixing that was in line with and provided further confirmation that the 210Pbexc present in the surface layer was indeed the result of sediment reworking. 230 Thexc/232Th sediment dating In the sediments of the Porcupine Abyssal Plain, the 230 Thexc/232Th ratio method was used in the dating core WH2 (Figure 6 and Supplementary Table S3). The sedimentation rate calculated by the best fit equation was 0.14 cm kyear21. Again, the top sediment layers (6 cm) did not follow the decreasing trend with increasing sediment depth, likely the result of sediment reworking, as seen in the 210Pbexc profile (Figure 4). Both sediment cores, C5 from the Iberian and WH2 from the Porcupine Abyssal Plain, indicated that the rates of sediment accumulation were very low. For comparison, sedimentation 432 Figure 4. F. P. Carvalho et al. 210 Pb excess in sediment cores from the Porcupine Abyssal Plain. Figure 5. Conventional age (years before present, BP) in sediment core C5 from the Iberian Abyssal Plain. The best fitting line (solid line) to experimental points below the SML is y ¼ 24.91 + 0.00316 x, where y is the sediment depth (cm) and x the 14C age (years). Correlation coefficient r ¼ 0.965; v, sedimentation rate. rates at the outer continental shelf off the Portuguese coast at depths of 75 –230 m are 0.16 –0.55 cm year21 and at the continental rise at depths of 520– 2860 m are 0.04 –0.38 cm year21, some Figure 6. Sedimentation rate (v) in sediment core WH2 from the Porcupine Abyssal Plain, computed from the best fit of the 230Th excess/232Th activity ratio against depth (cm) in sediment layers below the SML. Regression equation: AR(x) ¼ 17.2 exp(20.0641 x). Correlation coefficient r ¼ 20.96. three orders of magnitude greater than in the abyssal plains (Carvalho and Ramos, 1990). The sedimentation rate in the Iberian Basin was higher than in the Porcupine Basin and this, in conjunction with the sediment grain size composition, suggested terrigenous contributions to the Iberian Abyssal Plain, probably with material from the Iberian continental margin. 433 Sediment accumulation and bioturbation rates in the deep NE Atlantic Actually, sediment slumps in continental shelf deposits have been documented in the sediment records of 210Pbexc and 137Cs from atmospheric fallout. In the area, sediment slumps seemed to be driven along the Nazaré canyon that extends from the west coast of Portugal to the deep sea, and this explained the higher rates of sedimentation measured at the continental rise (Carvalho and Ramos, 1990). These sediment slumps might have a wider effect than initially thought, supplying sediments to the adjacent Iberian Abyssal Plain too. With such extremely low rates of sedimentation in both abyssal plains, the thickness of sediment layers sampled down to 10 –30 cm below the water–sediment interface encompassed the entire Holocene epoch (10 kyears). Moreover, the sediment layers below the top 0.5 cm were too old to contain unsupported 210Pb carried with settling sediment particles. Indeed, the 210Pbexc signal of seafloor sediments fades through radioactive decay in about a century (i.e. five 210Pb half-lives). This interval is not compatible with the presence of 210Pbexc in the much older 0.5 –11 cm sediment layers, unless freshly deposited unsupported 210Pb had been buried into the sediment by the biological activity of infauna through mechanisms of diffusive type (biodiffusion). This activity is likely carried out by the small Foraminifera and Sipunculidae that contribute to most of the infaunal biomass in the region (van der Loeff and Lavalaye, 1984; Smith et al., 1986; Thomson et al., 2000). Biological activity on the seafloor can therefore create a sediment SML 5– 11 cm thick in the cores of both abyssal basins (Figures 3 and 4). Further, the irregular vertical distribution of 210Pbexc in the SML between cores argues in favour of biologically mediated transport based on particle mixing, rather than on a geochemical, passive pore-water diffusion mechanism. 210 Pbexc biodiffusion and inventory Biodiffusion rates (DB) calculated from Equation (2) and using 210 Pb excess data ranged from 0.14 to 1.26 cm2 year21 (average 0.40 cm2 year21) in the Iberian Abyssal Plain and from 0.12 to 2.91 cm2 year21 (average 1.05 cm2 year21) in the Porcupine Abyssal Plain. Because of the wide ranges of values, the average rates of biodiffusion are not significantly different between basins and are in the range of values reported in the literature for the Northeast Atlantic (Table 1). In general, and based on extensive pioneer work on biodiffusion in sediments, the values of DB generally are in the range 0.03 –0.3 cm2 year21 in ocean sediments and between 3.1 and 38 cm2 year21 in coastal environments (Turekian et al., 1978). The inventory of 210Pb excess in the upper sediment layers averaged 3533 + 1063 and 3442 + 732 Bq m22 in the Iberian and Porcupine Abyssal Plains, respectively (Table 1). Assuming that these inventories are maintained in steady state by a continuous supply of unsupported 210Pb flux from the oceanic water column to the seafloor, the average annual 210Pbexc flux calculated using Equation (4) was 100 Bq m22 year21 at both sites (Table 1). The deposition fluxes are comparable with values determined in other studies at similar latitudes of the Northeast Atlantic: 94 + 38 Bq m22 year21 (Kershaw, 1985; Kershaw et al., 1986) and 67 + 22 Bq m22 year21 (Smith et al., 1986). The 14C age of the sediment SML in core C5 from the Iberian Abyssal Plain, TML ¼ 3132 years, is similar to the results for NE Atlantic abyssal sediments. In general, however, the extrapolated ages for the sediment surface (T0) vary far more than TML values (Table 2). The variation suggests different mixing extent of new and old particles in the sediment cores, but all of them corroborate the fact that 210Pbexc present below the sediment surface is likely the result of sediment reworking and burial of 210Pbexc (Table 2). Conclusions Rates of sediment accumulation in the NE Atlantic abyssal plains were very low, about three orders of magnitude less than those determined on the continental shelf and slope off the coast of Portugal. For the abyssal plains, the average rate of sedimentation was one order of magnitude greater in the Iberian Abyssal Plain (3.2 cm kyear21), likely the result of the advection of sediments from the continental margin, than in the Porcupine Abyssal Plain (0.14 cm kyear21), where the sediments are almost exclusively of oceanic origin. Despite the differences in sedimentation rates between basins, it is clear that sediment accumulation in the abyssal floor of the NE Atlantic is very slow. The sediment mixing or bioturbation (DB) in the surface layers of the abyssal seafloor may contribute to the mixing of sediment-bound contaminants and their removal from the water–sediment interface into the sediment. In these abyssal regions, the sediment SML has a thickness of some 5 – 11 cm. Nevertheless, in both basins contaminant burial will also be very slow, as shown from the 210Pbexc profiles and biodiffusion values. These sediment processes may be too slow to effectively counteract the dispersal of contaminants released near the abyssal floor in the long term. Table 2. Sedimentation rate (v), SML thickness (L), age of the mixed layer (TML), age of the sediment at the surface (T0), and biodiffusion coefficient (DB) of NE Atlantic sediments. Abyssal basin Iberian Madeira Porcupine Porcupine Iberian Golfe de Gascogne Porcupine Iberian Porcupine a Depth (m) 5 448 5 161 4 768 4 758 5 255 4 800 4 300 5 150 4 730 v (cm kyear21) 0.8a 1.8a 2.1a 2.2a 2.14a 3.25a 3.13a 3.2a 0.14b Sedimentation rates estimated using 14C. Sedimentation rates estimated using 230Thexc/232Th. b L (cm) 4.1 3.7 6.1 5.8 – 4.0 – 5 7 TML (years) 4 800 3 370 3 050 3 250 2 890 2 500 2 600 3 132 – T0 (years) 988 2 015 673 1 014 1 441 945 890 1 406 – DB (cm2 year21) – 0.13 – – – – – 0.16 0.14 Source Kershaw (1985) Kershaw (1985) Kershaw (1985) Kershaw (1985) Rouch (1987) Rouch (1987) Rouch (1987) This study This study 434 Supplementary material Supplementary material is available at ICESJMS online. Supplementary Table S1 lists concentrations of 210Pb and 226Ra (Bq kg21 dry weight) in sediment cores from the Iberian Abyssal Plain, and Supplementary Table S2 the same parameters for the Porcupine Abyssal Plain. Supplementary Table S3 lists uranium and thorium concentrations (Bq kg21+1s dry weight) in sediment core WH2 from the Porcupine Abyssal Plain. Acknowledgements Thanks are due to W. Feldt, Labör für Radiöoekologie der Gewasser, Hamburg, and the crew of the RV “Walther Herwig” and the Instituto Hidrográfico, Lisbon, and the crew of the RV “A. Carvalho” for collaboration with sample collection. References Brunnegård, J., Grandel, S., Ståhl, H., Tengberg, A., and Hall, P. O. J. 2004. Nitrogen cycling in deep-sea sediments of the Porcupine Abyssal Plain, NE Atlantic. Progress in Oceanography, 63: 159– 181. Carvalho, F. P., and Oliveira, J. M. 2007. Alpha emitters from uranium mining in the environment. Journal of Radioanalytical and Nuclear Chemistry, 274: 167– 174. Carvalho, F. P., Oliveira, J. M., Libânio, A., Lopes, I., Ferrador, G., and Madruga, M. J. 2005. Radioactivity in public water supplies in the uranium mining regions in Portugal. In Proceedings of an International Workshop on Environmental Contamination from Uranium Production Facilities and Remediation Measures, Lisbon, 11 – 13 February 2004, pp. 41– 51. International Atomic Energy Agency, Vienna. Carvalho, F. P., and Ramos, L. A. 1990. Lead-210 chronology in marine sediments from the northern continental margin of Portugal. In Proceedings of the Second National Conference on Environmental Quality, 1, pp. 143 –151. Universidade Nova de Lisboa, Lisbon. De Master, D. J., and Cochran, J. K. 1982. Particle mixing rates in deep sea sediments determined from excess 210Pb and 32Si profiles. Earth and Planetary Science Letters, 61: 257– 271. Erlenkeuser, H. 1980. 14C age and vertical mixing of deep-sea sediments. Earth and Planetary Science Letters, 47: 319– 326. Fabiano, M., Pusceddu, A., Dell’Anno, A., Armeni, M., Vanucci, S., Lampitt, R. S., Wolff, G. A., et al. 2001. Fluxes of phytopigments and labile organic matter to the deep ocean in the NE Atlantic Ocean. Progress in Oceanography, 50: 89– 104. Fowler, S. W., and Knauer, G. A. 1986. Role of large particles in the transport of elements and organic compounds through the oceanic water column. Progress in Oceanography, 16: 147 – 194. Heip, C. H. R., Duineveld, G., Flach, E., Graf, G., Helder, W., Herman, P. M. J., Lavaleye, M., et al. 2001. The role of the benthic biota in sedimentary metabolism and sediment-water exchange processes in the Goban Spur area (NE Atlantic). Deep-Sea Research II: Topical Studies in Oceanography, 48: 3223 – 3243. Ivanovich, M., and Harmon, R. S. 1992. Uranium Series Disequilibrium. Applications to Earth, Marine, and Environmental Sciences, 2nd edn. Clarendon Press, Oxford. Kershaw, P. J. 1985. 14C and 210Pb in NE Atlantic sediments: evidence of biological reworking in the context of radioactive waste disposal. Journal of Environmental Radioactivity, 2: 115 – 134. Kershaw, P. J., Smith, J. N., and Noshkin, V. E. 1986. Bioturbation. In Etat des Connaissances Océanographiques Relatifs au Site d’ Immersion de Déchets Radioactifs de Faible Activité dans F. P. Carvalho et al. ĺAtlantique Nord-Est, 2, pp. 67 –71. Nuclear Energy Agency, OECD, Paris. Lalou, C. 1982. Sediments and sedimentation processes. In Uranium Series Disequilibrium: Applications to Environmental Problems, pp. 431 – 458. Ed. by M. Ivanovich, and R. S. Harmon. Clarendon Press, Oxford. Lampitt, R. S., Boorman, B., Brown, L., Lucas, M., Salter, I., Sanders, R., Sew, K., et al. 2008. Particle export from the euphotic zone: estimates using a novel drifting sediment trap, 234Th and new production. Deep-Sea Research I: Oceanographic Research Papers, 55: 1484– 1502. Livingston, H. D., and Povinec, P. P. 2000. Anthropogenic marine radioactivity. Ocean and Coastal Management, 43: 689 – 712. NEA/OECD. 1984. Interim Oceanographic Description of the Northeast Atlantic Site for Disposal of Low-Level Radioactive Waste, 2. Nuclear Energy Agency, OECD, Paris. Povinec, P. P., Oregioni, B., Jull, A. J. T., Kieser, W. E., and Zhao, X. 2000. AMS measurements of 14C and 129I in seawater around radioactive waste dump sites. Nuclear Instruments and Methods in Physics Research, Section B: Beam Interactions with Materials and Atoms, 172: 672 – 678. Rabouille, C., Ståhl, H., Bassinot, F., Tengberg, A., Brunnegård, J., Hall, P., Kiriakoulakis, K., et al. 2001. Imbalance in the carbonate budget of surficial sediments in the North Atlantic Ocean: variations over the last millennium? Progress in Oceanography, 50: 201– 221. Rouch, P. 1987. Relations entre suspensions et sédiments actuels dans l’Atlantique NE (458– 498N, 168 – 228W). Minéralogie et géochimie des sédiments depuis 13 000ans. Thèse de Doctorat, Université de Neuchâtel. 150 pp. (in French). Smart, C. W. 2008. Abyssal NE Atlantic benthic foraminifera during the last 15 kyr: relation to variations in seasonality of productivity. Marine Micropaleontology, 69: 193– 211. Smith, J. N., Boudreau, B. P., and Noshkin, V. 1986. Plutonium and 210 Pb distributions in the Northeast Atlantic sediments: subsurface anomalies caused by non-local mixing. Earth and Planetary Science Letters, 81: 15 – 28. Soares, A. M. M. 1989. O Efeito de Reservatório Oceânico nas Águas Costeiras de Portugal Continental. ICEN/INETI, Sacavém (in Portuguese). Soares, A. M. M. 2005. Variabilidade do “Upwelling” Costeiro durante o Holocénico nas Margens Atlânticas Ocidental e Meridional da Penı́nsula Ibérica. PhD thesis, Faculdade de Ciências do Mar e do Ambiente, Universidade do Algarve, Faro (in Portuguese). Soto, E. H., Paterson, G. L. J., Billett, D. S. M., Hawkins, L. E., Galéron, J., and Sibuet, M. 2010. Temporal variability in polychaete assemblages of the abyssal NE Atlantic Ocean. Deep-Sea Research II: Topical Studies in Oceanography, 57: 1396 –1405. Ståhl, H., Tengberg, A., Brunnegård, J., and Hall, P. O. J. 2004. Recycling and burial of organic carbon in sediments of the Porcupine Abyssal Plain, NE Atlantic. Deep-Sea Research I: Oceanographic Research Papers, 51: 777– 791. Strickland, J. D. H., and Parsons, T. R. 1968. A Practical Handbook of Seawater Analysis. Bulletin of the Fisheries Research Board of Canada, 167. Stuiver, M., and Polach, H.A. 1977. Discussion. Reporting of 14C Data. Radiocarbon, 19: 355 – 363. Thomson, J., Brown, L., Nixon, S., Cook, G. T., and MacKenzie, A. B. 2000. Bioturbation and Holocene sediment accumulation fluxes in the north-east Atlantic Ocean (benthic boundary layer experiment sites). Marine Geology, 169: 21– 39. Thomson, J., Colley, S., Anderson, R., Cook, G. T., Mackenzie, A. B., and Harkness, D. D. 1993. Holocene sediment fluxes in the Sediment accumulation and bioturbation rates in the deep NE Atlantic Northeast Atlantic from 230Th excess and radiocarbon measurements. Paleoceanography, 8: 631 – 650. Thomson, J., Green, D. R. H., van Calsteren, P., Richter, T. O., and van Weering, T. C. E. 2006. Holocene sediment deposition on a NE Atlantic transect including Feni Drift quantified by radiocarbon and 230Th excess methods. Earth and Planetary Science Letters, 242: 170 – 185. Turekian, K. K., Cochran, J. K., and De Master, D. J. 1978. Bioturbation in deep-sea deposits: rates and consequences. Oceanus, 21: 34– 41. 435 van der Loeff, M. M. R., and Lavalaye, M. S. S. 1984. Geochemical and biological research at the NEA dumpsite for low level radioactive waste. Interim Report, Netherlands Institute for Sea Research, Texel, The Netherlands. 52 pp. Vanucci, S., Dell’Anno, A., Pusceddu, A., Fabiano, M., Lampitt, R. S., and Danovaro, R. 2001. Microbial assemblages associated with sinking particles in the Porcupine Abyssal Plain (NE Atlantic Ocean). Progress in Oceanography, 50: 105– 121.
© Copyright 2026 Paperzz