Grazers extend blue carbon transfer by slowing sinking speeds of kelp detritus


Marine plant communities such as kelp forests produce significant amounts of detritus, most of which is exported to areas where it can constitute an important trophic subsidy or potentially be sequestered in marine sediments. Knowing the vertical transport speed of detrital particles is critical to understanding the potential magnitude and spatial extent of these linkages. We measured sinking speeds for Laminaria hyperborea detritus ranging from whole plants to small fragments and sea urchin faecal pellets, capturing the entire range of particulate organic matter produced by kelp forests. Under typical current conditions, we determined that this organic material can be transported 10 s of m to 10 s of km. We show how the conversion of kelp fragments to sea urchin faeces, one of the most pervasive processes in kelp forests globally, increases the dispersal potential of detritus by 1 to 2 orders of magnitude. Kelp detritus sinking speeds were also faster than equivalent phytoplankton, highlighting its potential for rapid delivery of carbon to deep areas. Our findings support arguments for a significant contribution from kelp forests to subsidizing deep sea communities and the global carbon sink.


Marine plants are among the most productive primary producers on Earth1, forming extensive habitats in the coastal zone2,3,4. The fate of primary production in these coastal habitats has been the focus of ecological studies for decades, and we know a sizeable proportion of their biomass is exported as detritus to adjacent and distant habitats5,6,7. Seminal studies have documented the role of marine plant detritus as a trophic subsidy to ecosystems with low or no primary production e.g.8,9,10,11. More recently, there has also been a growing interest in the possibility that this material is not consumed but sequestered out of the carbon cycle12,13.

Regardless of whether the ultimate fate is consumption or sequestration, important and largely unanswered questions remain concerning the magnitude and transport distances of detritus exported from marine plant communities13. These questions are critical because transport distances determine the potential magnitude and spatial extent of trophic subsidy and sequestration. While there have been many observations of deposits of marine plant detritus on the seafloor meters to hundreds of kilometers away from their likely point of origin14,15,16,17, a comprehensive understanding of detritus dispersal patterns is lacking13, at least in part, because transport depends on a complex interplay between waves, currents, topography, and physical characteristics of detrital ‘particles’18. With the increasing availability of hydrodynamic particle dispersal (Langrangian) models19, e.g.20, estimates of possible detritus dispersal pathways are now possible21. This enables mapping of carbon transfer pathways, uncovering source-sink dynamics, as well as understanding changes in trophic connectivity or sequestration rates under scenarios of changing ocean currents19,22,23 or changing primary production24,25,26. The accuracy of particle dispersal models depends largely on accurate estimates of ocean currents. But, in addition to valid oceanographic parameters, these models require realistic inputs of the speeds at which detrital particles sink (i.e., deposition rates under calm conditions). Accurate estimates of vertical movement are particularly important, because it determines how long particles remain suspended, and therefore how far they can be moved by horizontal currents before they reach the seafloor27. Vertical position is also important because of complex spatial and temporal variability in ocean currents. As sinking speeds depend largely on weight, buoyancy, and drag, which is influenced by a range of particle properties including size, shape, and material density e.g.27, they are difficult to estimate or calculate for complex structures such as plant detritus. One solution is to determine these empirically.

Kelp forests are highly productive seaweed ecosystems along temperate and Arctic rocky shores4. The rates of direct consumption by herbivores are generally low in most kelp forests and on average 80% of the primary production enters the detrital pool6, implying a substantial potential for export as a vector of trophic connectivity or sequestration13. It has been well documented that a range of processes including dislodgment, tattering and fragmentation by waves and shredding by herbivores generate kelp detrital particles ranging in size from whole plants to small fragments and biogenic pellets (Fig. 1)17,28,29,30. Nevertheless, to our knowledge there have been no published studies of sinking speeds for detritus originating from kelp forests.

Figure 1

Kelp detrital particles (Laminaria hyperborea) from Malangen, northern Norway. (a) Accumulation of sea urchin faeces in a small depression, (b) small resuspended fragments, (c) whole blade at the bottom of the fjord (400 m depth), (d) medium sized fragments on a sandy bottom, (e) accumulation of fragments attached to, and consumed by, sea urchins (Strongylocentrotus droebachiensis), and (f) a whole plant being shredded by sea urchins. (Photos: (c) K. Filbee-Dexter, all other T. Wernberg).

Laminaria hyperborea is a dominant subtidal kelp throughout the northeast Atlantic that forms extensive forests between 0–25 m depth on rocky coasts from Portugal to northern Norway31,32,33. Approximately 22% of L. hyperborea detrital production occurs as distal erosion of small particles and 78% as dislodgment of whole thalli or seasonal loss of old blades (full blades grown over the previous year that are shed during spring)34. Large particles can reach deep habitats intact (Fig. 1c) or can be broken down to smaller fragments through abrasion or shredding by herbivores (Fig. 1). L. hyperborea does not have pneumatocysts or hollow parts so all its detritus sinks. Nevertheless, due to substantial phenological differences in biochemical composition and tissue properties between stipes, new blades, old blades and faeces35,36,37, the sinking speeds likely differ between detritus originating from different thallus origin, size and shape. Here we empirically determine sinking speeds and estimate transport distances for 8 different size and tissue characteristics of L. hyperborea ranging from sea urchin faeces and fragments to entire blades and plants (Fig. 1).


Detrital particles measured in this study displayed a broad range of characteristics that will influence their movement in the water column (Table 1). Mean particle area ranged from 0.6 mm2 to 0.18 m2 and mean biomass ranged from 0.1 mg to 0.65 kg wet weight, capturing the high variability in forms that kelp detritus takes (Fig. 1). Average density of blade material was 1064 ± 96 kg m−3 (n = 15) and stipe material was 1288 ± 246 kg m−3 (n = 10).

Table 1 Characteristics of detrital particles and their sinking speeds measured in this study (mean ± SD [min-max]).

Detrital kelp particles sank at a large range of speeds, from 0.002 m s−1 for the smallest particles to 0.5 m s−1 for whole plants and stipes (Table 1, Fig. 2). They tended to fall vertically and orient towards maximal downward-facing surface area in the water column (i.e. blades splayed and stipes perpendicular; Supplementary Video), but some particles did move horizontally despite little to no current, the farthest ending up ~20 m away from the drop release position after sinking 4 m depth.

Figure 2

Sinking speeds of different kelp detrital particles against (a) area and (b) biomass (log scales).

Sinking speed increased with kelp area (ANCOVA, F1,339 = 125, p < 0.001), but there was high variability with this relationship (Fig. 2), and it depended on the type of kelp material (ANCOVA, F5,339 = 125, p < 0.001). Stipes and whole plants sank faster compared to other particles (Tukeys posthoc; p < 0.001). There was no strong difference between sinking speeds of old blades, new blades, and blade fragments (Tukeys posthoc; p > 0.05), despite different average biomasses and areas of these particles (Table 1). Faeces sank slower than all other particles (Tukeys posthoc; p < 0.040), with small faeces sinking about half the speed of large and medium sized faeces (Table 1). The highest variabilities in speeds were recorded for whole blades and large and medium blade fragments, and ranged from 0.008 m s−1 to 0.25 m s−1 (Table 1).

Most particles that were measured multiple times did not vary in their sinking speeds among replicate runs (coefficient of variation <40%; Fig. 3). Stipes showed the least variability (apart from one outlier). Blades showed the most variability, with three particles experiencing a large range of sinking rates. This was likely due to their position at release and the extent they compacted, changed shape, and tumbled in the water column (Supplementary Video).

Figure 3

Coefficient of variation (CV) between sinking speeds measured for repeated drops (n = 3) of large particles. Boxes show the lower and upper quartile values and the thick line indicates the median (n = 10 for whole plants and old blades, n = 20 for stipes and blades). The whiskers correspond to 1.5 interquartile range (IQR ~ the 95% confidence interval) and the black dots represent observations outside this range.

Potential export distances for detrital particles over the range of sinking speeds measured in this study varied from 2 to 940 m if the particle settled at 10 m depth, and from 166 m to 94 km if the particle settled at 1000 m depth (under constant currents, but see38). Stipes and whole plants stayed relatively close to their release point, whereas most whole blades and blade fragments settled within 10 s of m to several km from their release point. Sea urchin faeces moved up to a km when settling at 10 m depth and reached 10 s of km when settling at 1000 m depth. Thus export distances of kelp detritus should be greatest in areas with many sea urchins, where currents are strong, or where the sea floor grades quickly to deep depths.


Significant amounts of biogenic carbon are exported from marine plant communities, such as kelp forests, in the form of detritus6. How this detritus participates in the global carbon cycle depends on where it ends up (i.e., export distance)12. We found a wide range of sinking speeds for kelp particles, showing that the type of particle and the extent of fragmentation or consumption can strongly impact their ultimate fate. Under minimal to moderate current conditions, most blades, stipes, and whole plants will reach the seafloor within a short distance of the kelp forest, whereas small particles and sea urchin faeces can travel substantial distances. This suggests that under these conditions as much as 22%34 of kelp-derived carbon could reach the continental shelf and deep sea. These estimates represent lower bounds of maximal potential export distances as they do not account for post-deposition movement or transformation of the detritus (i.e., fragmentation by shredders), nor do they include tidal currents or other locally strong horizontal water movement. In addition, the outlying ‘slow drops’ of blades measured in this study suggest a small portion of large particles has potential to be exported further.

Sea urchin trapping and grazing of large kelp detritus is a pervasive process in kelp forests globally25. A large proportion of the kelp consumed by sea urchins is released as faeces of fresh algal material that has not been digested35. Our study demonstrates that sea urchins play a major role in mobilizing kelp detritus by consuming or shredding large particles into small fragments and faeces that sink 20 times slower than whole plants (Table 1). This transformation extends the average detritus dispersal distance 30–50 times (Fig. 4), and so the amount of consumption has implications for the spatial extent of this carbon transfer. Sea urchin grazing intensity on kelp forests has changed dramatically in many regions due to climate change39,40,41,42. The implied change in consumption rate is likely to have substantially altered the amount of detritus moving through different export pathways, and thus the magnitude and location of detrital deposits.

Figure 4

Export distances for detrital particles over the range of sinking speeds measured in this study (slowest sea urchin faeces to fastest stipe), and under different horizontal current speeds. Black lines are average ± SD for faeces, whole blades, and stipes (Table 1). Note: whole thalli have similar sinking speeds as stipes (Table 1).

Detrital kelp particles that are exported large distances can pass into deep depressions, canyons, or cross the continental shelf, eventually reaching the deep sea. In these recipient habitats they may be buried in sediments and contribute to carbon sequestration12 or be assimilated by deep benthic communities with little to no in situ source of primary production15,43. The sinking speeds of small particles in our study of 0.008–0.014 ms−1 are 5–10 times higher than the sinking speeds of 0.0013–0.0028 ms−1 of similar-sized aggregates of phytoplankton (Skeletonema costatum and Emiliania Huxleyi, 2.2–4.9 mm2)44 and were within range of reported sinking speeds of faeces from copepods, macrocrustaceans, tunicates, shrimps, and polychaetes (0.001–0.06 ms−145). Faeces tend to sink slower and change chemical composition as they degrade and undergo microbial mineralization45. The much faster deposition of sea urchin faeces implies less remineralization of the carbon in transit and therefore a greater potential contribution to deep benthic food webs or sequestration relative to phytoplankton derived organic material13. Kelps also contain organic molecules that are not easily broken down, which further slows remineralization46. Notably, kelp forests often occur in high energy environments4 and therefore have a high potential for long distance export that is further extended in areas with many grazers or that grade quickly to deep depths. Our findings are consistent with arguments for a significant contribution from these underwater forests to subsidizing deep sea communities and the global carbon sink.


We measured the sinking speeds of 340 kelp (Laminaria hyperborea) detrital particles ranging in size from pellets of sea urchin faeces to small blade fragments and whole plants (Table 1). Kelps were collected from Norway (Malangen fjord; 69.63°N 18.01°E) in May 2018 (new blades), cut into pieces matching in size and shape to detritus collected in the field, and photographed and measured for area (Fig. 1) 17. To obtain sea urchin faeces, we collected adult green sea urchins (Strongylocentrotus droebachiensis) that were directly consuming L. hyperborea, held them for 24 hours in seawater with unlimited access to L. hyperborea, and collected fresh faecal pellets with a filter.

Sinking speeds were measured within 24 hours of collection by filming (GoPro Hero3) individual particles of detritus falling through seawater next to a ruler and subsequently calculating sinking distance over video time. Whole plants, blades, stipes and large fragments were measured in situ inside a protected marina with no currents by gently releasing them off a jetty next to a 2-m ruler, while small fragments and sea urchin faeces were released through a 20 cm clear pvc pipe (5 cm diameter). Any epiphytes on the kelps were left intact, however, there were no epiphytes on the blades and most stipe epiphytes were almost entirely low-profile encrusting species. Faecal pellets were rinsed in clean seawater to prevent compaction according to methods of Sauchyn and Scheibling35. To measure the consistency of sinking rates of large pieces (blades, stipes and whole thalli), we tagged these detrital particles with unique numbers and dropped them off the jetty 3 times (4 times for whole thalli). We dropped a total of 10 whole plants, 20 stipes, 20 new blades and 10 old blades.

To measure particle area and weight, all detrital particles were laid out and photographed against a ruler on a light background and their area (A) measured in Image-J 1.52a ( Whole thalli, stipes and blades were all weighed individually to 0.1 g wet weight (WW). For blade fragments, a subset (n = 15) were weighed. There was a strong linear relationship between blade fragment area and biomass (WW(g) = 0.001 × A(mm2) – 1.1814; Pearson’s r2 = 0.924, n = 15), so we applied a linear regression to all remaining fragments to determine their biomass.

Material density was determined for a subset of stipes (10) and new blades (15). Stipe density was calculated using wet weight × volume−1, using displacement volume measured in water. Average stipe volumes were 0.42 ± 0.08 L. Blade density was determined using wet weight × (area × average thickness)−1, using thickness measured at the base (1.29 ± 0.74 mm) and distal ends (0.56 ± 0.13 mm) with venier calipers (mean ± SD).

Sea urchin faeces were classified as small, medium or large size fractions, based on video observations. Faeces that were just large enough to be resolved in the video were classified into the smallest size fraction, faeces with diameters approximately an order of magnitude larger than most were grouped into the largest size fraction, and all others were classified as medium sized. A subset (n = 48) of faeces from across these 3 size categories were photographed on white paper to determine area. To obtain a coarse estimate of biomass (which was challenging with a 0.001 g scale), we weighed all 48 faeces at once, and portioned out the total weight using the relative areas of each fragment. Faeces used to measure sinking speeds were assigned a particle area by randomly selecting an area from the distribution of measures for each size class (assuming a normal distribution). This enabled us to visualize the variability in biomass and area for this size category of detritus, and corresponded well with the size classes of S. droebachiensis faeces reported by Sauchyn and Scheibling47.

We used an ANCOVA to test the effect of different particle types on sinking speed, using particle area as a covariate. Data met assumptions of normality and heteroscedasticity. Posthoc comparisons were performed with Tukeys HSD test. Analyses were performed in R version 3.5.0.

To investigate the implications of the observed sinking speeds on the transport of detrital kelp particles, dispersal distances for deposition to different depths were simulated under different current speeds for detritus with different sinking speeds. We calculated the time a particle would spend in the water column if it had 10 m vertical distance to sink (i.e. within the kelp forests) or 1000 m vertical distance to sink (i.e., transported off the shelf), which encapsulated the range of depths observations of kelp detritus17,48. We multiplied this timespan by horizontal water movement speeds of 0.05, 0.1 and 0.2 m s−1, which captures normally prevailing currents along the Norwegian coast (Norwegian Meteorological Institute, and corresponded to the range of current speeds (0 to 0.5 m s−1 at 10 m depth) used by Gaylord et al.27 in their kelp spore dispersal model. These calculations do not reflect actual export, for that you need hydrographic models, but demonstrate expected export distances over a range of conditions.

Data Availability

The data sets generated during the current study are available from the corresponding author on reasonable request.


  1. 1.

    Mann, K. H. Seaweeds: their productivity and strategy for growth. Science 182, 975–981, (1973).

    ADS  CAS  Article  Google Scholar 

  2. 2.

    James, H., Andrea, M., Ruth, S., Andrew, B. & Mark, S. Predicting Global Patterns in Mangrove Forest Biomass. Conservation Letters 7, 233–240, (2014).

    Article  Google Scholar 

  3. 3.

    Fourqurean, J. W. et al. Seagrass ecosystems as a globally significant carbon stock. Nature Geoscience 5, 505–509, (2012).

    ADS  CAS  Article  Google Scholar 

  4. 4.

    Wernberg, T., Krumhansl, K., Filbee-Dexter, K. & Pedersen, M. In World Seas: An Environmental Evaluation Vol. III: Ecological Issues and Environmental Impacts (ed C. Sheppard) 57–78, (Elsevier, 2019).

  5. 5.

    Cebrian, J. Patterns in the fate of production in plant communities. Am Nat 154, 449–468, (1999).

    Article  PubMed  Google Scholar 

  6. 6.

    Krumhansl, K. & Scheibling, R. Production and fate of kelp detritus. Marine Ecology Progress Series 467, 281–302, (2012).

    ADS  Article  Google Scholar 

  7. 7.

    Duggin, D., Simenstad, C. & Estes, J. Magnification of secondary production by kelp detritus in coastal marine ecosystems. Science 245, 170–173, (1989).

    ADS  Article  Google Scholar 

  8. 8.

    Bustamante, R. H., Branch, G. M. & Eekhout, S. Maintenance of an exceptional intertidal grazer biomass in South Africa: Subsidy by subtidal kelps. Ecology 76, 2314–2329, (1995).

    Article  Google Scholar 

  9. 9.

    Vetter, E. W. Detritus-based patches of high secondary production in the nearshore benthos. Marine Ecology Progress Series 120, 251–262, (1995).

    ADS  Article  Google Scholar 

  10. 10.

    Wernberg, T., Vanderklift, M. A., How, J. & Lavery, P. S. Export of detached macroalgae from reefs to adjacent seagrass beds. Oecologia 147, 692–701, (2006).

    ADS  Article  PubMed  Google Scholar 

  11. 11.

    Filbee‐Dexter, K. & Scheibling, R. E. The present is the key to the past: linking regime shifts in kelp beds to the distribution of deep‐living sea urchins. Ecology 98, 253–264, (2017).

    Article  PubMed  Google Scholar 

  12. 12.

    Krause-Jensen, D. & Duarte, C. M. Substantial role of macroalgae in marine carbon sequestration. Nature Geoscience 9, 737,, (2016).

    ADS  CAS  Article  Google Scholar 

  13. 13.

    Krause-Jensen, D. et al. Sequestration of macroalgal carbon: the elephant in the Blue Carbon room. B iology Letters 14, 20180236, (2018).

    Article  Google Scholar 

  14. 14.

    Vanderklift, M. & Wernberg, T. Detached kelps from distant sources are a food subsidy for sea urchins. Oecologia 157, 327–335, (2008).

    ADS  Article  PubMed  Google Scholar 

  15. 15.

    Vetter, E. W. & Dayton, P. K. Organic enrichment by macrophyte detritus, and abundance patterns of megafaunal populations in submarine canyons. Marine Ecology Progress Series 186, 137–148, (1999).

    ADS  Article  Google Scholar 

  16. 16.

    Filbee-Dexter, K. & Scheibling, R. E. Detrital kelp subsidy supports high reproductive condition of deep-living sea urchins in a sedimentary basin. Aquatic Biology 23, 71–86, (2014).

    Article  Google Scholar 

  17. 17.

    Filbee-Dexter, K., Wernberg, T., Norderhaug, K. M., Ramirez-Llodra, E. & Pedersen, M. F. Movement of pulsed resource subsidies from kelp forests to deep fjords. Oecologia 187, 291–304, (2018).

    ADS  Article  PubMed  Google Scholar 

  18. 18.

    Gaylord, B., Reed, D. C., Raimondi, P. T. & Washburn, L. Macroalgal spore dispersal in coastal environments: mechanistic insights revealed by theory and experiment. Ecological Monographs 76, 481–502,[0481:MSDICE]2.0.CO;2 (2006).

    Article  Google Scholar 

  19. 19.

    Coleman, M. A. et al. Anticipating changes to future connectivity within a network of marine protected areas. Global Change Biology 23, 3533–3542, (2017).

    ADS  Article  PubMed  Google Scholar 

  20. 20.

    Mitarai, S., Watanabe, H., Nakajima, Y., Shchepetkin, A. F. & McWilliams, J. C. Quantifying dispersal from hydrothermal vent fields in the western Pacific Ocean. Proceedings of the National Academy of Sciences 113, 2976–2981, (2016).

    ADS  CAS  Article  Google Scholar 

  21. 21.

    Griffa, A., Piterbarg, L. & Özgökmen, T. Predictability of Lagrangian particle trajectories: Effects of smoothing of the underlying Eulerian flow. Journal of Marine Research 62, 1–35, (2004).

    Article  Google Scholar 

  22. 22.

    Ridgway, K. R. Long-term trend and decadal variability of the southward penetration of the East Australian Current. Geophysical Research Letters 34, L13613, (2007).

    Google Scholar 

  23. 23.

    Snyder, M. A., Sloan, L. C., Diffenbaugh, N. S. & Bell, J. L. Future climate change and upwelling in the California Current. Geophysical Research Letters 30, 1823, (2003).

  24. 24.

    Filbee-Dexter, K. & Wernberg, T. Rise of turfs: a new battlefront for globally declining kelp forests. BioScience 68, 64–76, (2018).

    Article  Google Scholar 

  25. 25.

    Filbee-Dexter, K. & Scheibling, R. E. Sea urchin barrens as alternative stable states of collapsed kelp ecosystems. Marine Ecology Progress Series 495, 1–25, (2014).

    ADS  Article  Google Scholar 

  26. 26.

    Krumhansl, K. A. et al. Global patterns of kelp forest change over the past half-century. Proceedings of the National Academy of Sciences 113, 13785–13790, (2016).

    CAS  Article  Google Scholar 

  27. 27.

    Gaylord, B., Reed, D. C., Raimondi, P. T., Washburn, L. & McLean, S. R. A physically based model of macroalgal spore dispersal in the wave and current-dominated nearshore. Ecology 83, 1239–1251, (2002).

    Article  Google Scholar 

  28. 28.

    de Bettignies, T., Thomsen, M. & Wernberg, T. Wounded kelps: patterns and susceptibility to breakage. Aquatic Biology 17, 223–233, (2012).

    Article  Google Scholar 

  29. 29.

    Krumhansl, K. A., Lee, J. M. & Scheibling, R. E. Grazing damage and encrustation by an invasive bryozoan reduce the ability of kelps to withstand breakage by waves. Journal of Experimental Marine Biology and Ecology 407, 12–18, (2011).

    Article  Google Scholar 

  30. 30.

    Sauchyn, L. K., Lauzon-Guay, J. S. & Scheibling, R. E. Sea urchin fecal production and accumulation in a rocky subtidal ecosystem. Aquatic Biology 13, 215–223, (2011).

    Article  Google Scholar 

  31. 31.

    Tuya, F. et al. Patterns of landscape and assemblage structure along a latitudinal gradient in ocean climate. Marine Ecology Progress Series 466, 9–19, (2012).

    ADS  Article  Google Scholar 

  32. 32.

    Smale, D. A., Wernberg, T., Yunnie, A. L. E. & Vance, T. The rise of Laminaria ochroleuca in the Western English Channel (UK) and comparisons with its competitor and assemblage dominant Laminaria hyperborea. Marine Ecology 36, 1033–1044, (2015).

    ADS  Article  Google Scholar 

  33. 33.

    Sjøtun, K., Fredriksen, S., Lein, T. E., Rueness, J. & Sivertsen, K. Population studies of Laminaria hyperborea from its northern range of distribution in Norway. Hydrobiologia 260/261, 215–221, (1993).

    Article  Google Scholar 

  34. 34.

    Pessarrodona, A., Moore, P. J., Sayer, M. D. J. & Smale, D. A. Carbon assimilation and transfer through kelp forests in the NE Atlantic is diminished under a warmer ocean climate. Global Change Biology (2018), (2018).

    ADS  Article  Google Scholar 

  35. 35.

    Sauchyn, L. K. & Scheibling, R. E. Degradation of sea urchin feces in a rocky subtidal ecosystem: implications for nutrient cycling and energy flow. Aquatic Biology 6, 99–108, (2009).

    Article  Google Scholar 

  36. 36.

    Smith, B. D. & Foreman, R. E. An assessment of seaweed decomposition within a southern Strait of Georgia seaweed community. Marine Biology 84, 197–205 (1984).

    Article  Google Scholar 

  37. 37.

    Dethier, M. N. et al. Degrading detritus: Changes in food quality of aging kelp tissue varies with species. Journal of Experimental Marine Biology and Ecology 460, 72–79, (2014).

    Article  Google Scholar 

  38. 38.

    Largier, J. L. Considerations in estimating larval dispersal distances from oceanographic data. Ecological Applications 13, 71–89,[0071:CIELDD]2.0.CO;2 (2003).

    Article  Google Scholar 

  39. 39.

    Norderhaug, K. et al. Effects of climate and eutrophication on the diversity of hard bottom communities on the Skagerrak coast 1990–2010. Marine Ecology Progress Series 530, 29–46, (2015).

    ADS  CAS  Article  Google Scholar 

  40. 40.

    Feehan, C., Scheibling, R. E. & Lauzon-Guay, J. S. An outbreak of sea urchin disease associated with a recent hurricane: Support for the “killer storm hypothesis” on a local scale. Journal of Experimental Marine Biology and Ecology 413, 159–168, (2012).

    Article  Google Scholar 

  41. 41.

    Catton, C., Rogers-Bennett, L. & Amrhein, A. Source: CDF Marine Management News. (accessed 30 March 2017; “Perfect Storm” Decimates Northern California Kelp Forests, 2016.

  42. 42.

    Ling, S. D., Johnson, C. R., Frusher, S. D. & Ridgway, K. R. Overfishing reduces resilience of kelp beds to climate-driven catastrophic phase shift. Proceedings of the National Academy of Sciences of the United States of America 106, 22341–22345, (2009).

    ADS  Article  PubMed  PubMed Central  Google Scholar 

  43. 43.

    Ramirez-Llodra, E. et al. A snap shot of the short-term response of crustaceans to macrophyte detritus in the deep Oslofjord. Scientific Reports 6, 23800,, (2016).

  44. 44.

    Iversen, M. H. & Ploug, H. Ballast minerals and the sinking carbon flux in the ocean: carbon-specific respiration rates and sinking velocity of marine snow aggregates. Biogeosciences 7, 2613–2624, (2010).

    ADS  CAS  Article  Google Scholar 

  45. 45.

    Wotton, R. S. & Malmqvist, B. Feces in Aquatic Ecosystems: Feeding animals transform organic matter into fecal pellets, which sink or are transported horizontally by currents; these fluxes relocate organic matter in aquatic ecosystems. BioScience 51, 537–544,[0537:FIAE]2.0.CO;2 (2001).

    Article  Google Scholar 

  46. 46.

    Trevathan-Tackett, S. M. et al. Comparison of marine macrophytes for their contributions to blue carbon sequestration. Ecology 96, 3043–3057, (2015).

    Article  PubMed  Google Scholar 

  47. 47.

    Sauchyn, L. K. & Scheibling, R. E. Fecal production by sea urchins in native and invaded algal beds. Marine Ecology Progress Series 396, 35–48, (2009).

    ADS  CAS  Article  Google Scholar 

  48. 48.

    Filbee-Dexter, K. & Scheibling, R. E. Spatial patterns and predictors of drift algal subsidy in deep subtidal environments. Estuaries and Coasts 39, 1724–1734, (2016).

    Article  Google Scholar 

Download references


This work was funded by the Norwegian Research Council (KELPEX 255085/E40) and the Norwegian Blue Forest Network (KelpFloat, KFD). Additional funding was received from the Australian Research Council (DP160100114, TW). Stein Fredriksen, Kjell Magnus Norderhaug, Morten Pedersen, Eli Rinde, Kasper Hancke, Eva Ramirez-Llodra and Trond Kristiansen assisted with measurements and discussions.

Author information




T.W. and K.F.D. co-led this paper and contributed equally to all parts of this work.

Corresponding author

Correspondence to Thomas Wernberg.

Ethics declarations

Competing Interests

The authors declare no competing interests.

Additional information

Publisher’s note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Electronic supplementary material

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Wernberg, T., Filbee-Dexter, K. Grazers extend blue carbon transfer by slowing sinking speeds of kelp detritus. Sci Rep 8, 17180 (2018).

Download citation


  • Kelp Detritus
  • Sinking Speed
  • Kelp Forests
  • Marine Plant Communities
  • Trophic Subsidy

Further reading


By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.