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Coastal marine sediments, particularly those in estuarine environments, are home to a wide range of benthic organisms including small invertebrates, marine plants, and flatfish species. This type of seafloor maintains a delicate balance that can be easily disturbed by human activity such as shipping traffic, bottom trawling, and dredging.


Resuspension and deposition of sediment due to water movement (Webster et al.2003)

Once disturbed, fine sediments can become resuspended in the water column creating many problems for marine life. These problems include: eutrophication, alteration of sediment structure, burial and smothering, increased turbidity, and chemical disturbance (OSPAR, 2011). Chemical disturbance refers to the remobilisation of toxic materials, such as heavy metals (e.g. Lead (Pb) and mercury (Hg)) which can have adverse effects on marine creatures. Tributyl tin (TBT) for example poses a particular risk to molluscan species like the dogwhelk (Nucella lapillus).


Group of dogwhelk (Nucella lapillus) on the barnacles they eat (WWW1)

This whelk takes in TBT with its prey and results in a build-up of the toxin leading to reproductive abnormalities which can in turn prevent successful production of larvae (Murphy et al., unpublished). Increases in turbidity (cloudiness of water) can limit the amount of light that can penetrate the water column, posing a threat to light dependent organisms like marine plants and photosynthetic phytoplankton. Without light, these organisms eventually die, removing a food source for any herbivorous creatures, and subsequently leading to eutrophication and hypoxic dead zones due to the breakdown of dead organisms.


Water turbidity scale (WWW2)

Large levels of sedimentation, caused predominantly by dredging or dumping, can also crush and smother many delicate marine flora and fauna. Between the year 2009 and 2013 almost 3 million tonnes of sediments were dumped into the sea, with up to 56 tonnes of this being comprised of purely toxic metals (OSPAR, 2013). Coastal developments such as harbour expansions may exascerbate this. Although harbour expansion related sedimentation is usually a temporary, localised issue, it could still have profound long term effects for species such as the brittle star (Ophiurida spp.) and banded venus (Clausinella fasciata) which live in the muddy sand around marina macroenvironments (MERC Contractors, 2007). Shipping traffic in busy fishing areas may pose long term issues, as the sediment disturbance is continuous and can only be stopped with the halting of shipping traffic, which in turn would cause countless issues for any businesses relying on this traffic.

Seán & Orla-Peach


Darwin, J. (2008) Poison in the Well: Radioactive Waste in the Oceans at the Dawn of the Nuclear Age. Rutgers University Press.

Hoch, M. (2001) Organotin compounds in the environment – An overview. Applied Geochemistry, 16(7-8), 719–743.

Krause, J. C., vonNordheim, H., & Bräger, S. (2006) Marine Nature Conservation in Europe 2006. Procedings of the Symposium, (May 2006), 107–116.

MERC. (2007) Surveys of sensitive subtidal benthic communities in Roaringwater Bay and Islands, Lough Hyne Nature Reserve and Environs, Valentia Harbour and Portmagee Channel, Broadhaven Bay.

Murphy, R.J., Tuthill, R.E., Casey, D., & O’Riordan, R. (unpublished) Abundances of Nucella lapillus (L) and Littorina littorea (L) as indicators of TBT levels in Cork Harbour and Bantry Bay, Ireland. Master’s Thesis, University College Cork.

OSPAR Commission (2011) Annual OSPAR report on dumping of wastes or other matter at sea in 2009.

Webster, I.T., Ford, P.W., Robson, B., Margvelashvili, N., & Parslow, J.S. (2003) Conceptual Models of the Hydrodynamics, Fine-Sediment Dynamics, Biogeochemistry, and Primary Production in the Fitzroy Estuary. Cooperative Research Centre for Coastal Zone, Estuary & Waterway Management Technical Report #8.

WWW1 – Group of dogwhelk (Nucella lapillus) on the barnacles they 

WWW2 –   Water Turbidity Scale