Quantification and prediction of the impact of fishing on epifaunal communities

The loss of emergent epifaunal biomass due to fishing impacts has not been quantified at the scale of an entire fishery. Here, based on an analysis of the impacts of the scallop dredge fleet around the Isle of Man, Irish Sea, we show how fishing and the physicalenvironment act to determine the biomass and size composition of emergent epifauna. The epifauna create habitat structure that is used by juvenile scallops and other species, thus providing an important ecosystem service. Epifauna were identified and quantified basedon photographs taken during an extensive survey of the territorial waters of the Isle of Man. On hard substrata, the effect of tidal velocity on total biomass (g m -2) and the maximum size (g) of the largest organism encountered in each taxon was positive while wave stress and fishing frequency had a negative impact. We used the results to predict the distribution of biomass and maximum size and to quantify the total effects of fishing. Fishing frequency was the most important factor that affected maximum size of the epifauna, resulting in a mean decrease in size of 17% (range 0 to 66%). Total biomass was predominantly affected by wave stress and tidal velocity while fishing caused a mean biomass decrease of 8% (range 0 to 34%), equivalent to 1.8 g wet weight m-2. The results have implications for management because they provide an assessment of the overall impact of fishing at the scale of an entire fleet and inform the identification of areas where seabed habitatsare most vulnerable to fishing.

[1]  William N. Venables,et al.  Modern Applied Statistics with S , 2010 .

[2]  Jean-Pierre Rossi,et al.  Towards indicators of butterfly biodiversity based on a multiscale landscape description , 2010 .

[3]  Yixin Zhang,et al.  Catchment-scale effects of forestry practices on benthic invertebrate communities in Pacific coastal streams. , 2009 .

[4]  S. Neill,et al.  Context dependency of relationships between biodiversity and ecosystem functioning is different for multiple ecosystem functions , 2009 .

[5]  R. O’Connor,et al.  A comparison of relative growth in Cerastoderma (=Cardium) edule, Modiolus modiolus, and Mytilus edulis (Mollusca: Bivalvia) , 2009 .

[6]  Theunis Piersma,et al.  Patchiness of macrobenthic invertebrates in homogenized intertidal habitats: hidden spatial structure at a landscape scale , 2009 .

[7]  L. Carrascal,et al.  Partial least squares regression as an alternative to current regression methods used in ecology , 2009 .

[8]  Kevin McGarigal,et al.  Parsimony in landscape metrics: Strength, universality, and consistency , 2008 .

[9]  W. Sanderson,et al.  Small-scale variation within a Modiolus modiolus (Mollusca: Bivalvia) reef in the Irish Sea. II. Epifauna recorded by divers and cameras , 2008, Journal of the Marine Biological Association of the United Kingdom.

[10]  D. Moore,et al.  Chapter 5. Macrofauna Techniques , 2007 .

[11]  Corinne Martin,et al.  Modelling species distributions using regression quantiles , 2007 .

[12]  Michel J. Kaiser,et al.  Assessing and predicting the relative ecological impacts of disturbance on habitats with different sensitivities , 2007 .

[13]  Ron Wehrens,et al.  The pls Package: Principal Component and Partial Least Squares Regression in R , 2007 .

[14]  R. Koenker,et al.  Regression Quantiles , 2007 .

[15]  J. Manderson,et al.  The effects of seafloor habitat complexity on survival of juvenile fishes : Species-specific interactions with structural refuge , 2006 .

[16]  Paul J. Somerfield,et al.  Global analysis of response and recovery of benthic biota to fishing , 2006 .

[17]  Michel J. Kaiser,et al.  Cumulative impacts of seabed trawl disturbance on benthic biomass, production, and species richness in different habitats , 2006 .

[18]  Michel J. Kaiser,et al.  Distribution and behaviour of Common Scoter Melanitta nigra relative to prey resources and environmental parameters , 2006 .

[19]  Michael P. Lesser,et al.  Benthic-pelagic coupling on coral reefs : Feeding and growth of Caribbean sponges , 2006 .

[20]  L. Henry,et al.  Impacts of otter trawling on colonial epifaunal assemblages on a cobble bottom ecosystem on Western Bank (northwest Atlantic) , 2006 .

[21]  M. Kendall,et al.  Benthic Mapping Using Sonar, Video Transects, and an Innovative Approach to Accuracy Assessment: A Characterization of Bottom Features in the Georgia Bight , 2005 .

[22]  C. Jun,et al.  Performance of some variable selection methods when multicollinearity is present , 2005 .

[23]  Michel J. Kaiser,et al.  Are marine protected areas a red herring or fisheries panacea , 2005 .

[24]  A. Rowden,et al.  Macrofaunal assemblages of benthic habitat of different complexity and the proposition of a model of biogenic reef habitat regeneration in Foveaux Strait, New Zealand , 2004 .

[25]  K. Sebens,et al.  Effects of water movement on prey capture and distribution of reef corals , 1991, Hydrobiologia.

[26]  M. Jones,et al.  Detecting two-dimensional spatial structure in biological data , 1977, Oecologia.

[27]  C. Bradshaw,et al.  The effect of scallop dredging on Irish Sea benthos: experiments using a closed area , 2001, Hydrobiologia.

[28]  B. Cade,et al.  A gentle introduction to quantile regression for ecologists , 2003 .

[29]  C. Bradshaw,et al.  To what extent does upright sessile epifauna affect benthic biodiversity and community composition? , 2003 .

[30]  Walter Krämer,et al.  Review of Modern applied statistics with S, 4th ed. by W.N. Venables and B.D. Ripley. Springer-Verlag 2002 , 2003 .

[31]  Jeremy S. Collie,et al.  Modification of marine habitats by trawling activities: prognosis and solutions , 2002 .

[32]  G. J. Piet,et al.  Diversity and community structure of epibenthic invertebrates and fish in the North Sea , 2002 .

[33]  S. Wold,et al.  PLS-regression: a basic tool of chemometrics , 2001 .

[34]  S. Jenkins,et al.  Impact of scallop dredging on benthic megafauna: a comparison of damage levels in captured and non-captured organisms , 2001 .

[35]  S. Jennings,et al.  Trawling disturbance can modify benthic production processes , 2001 .

[36]  Thomas Brey,et al.  Population dynamics in benthic invertebrates. A virtual handbook , 2001 .

[37]  D. Barnes,et al.  The influences of bathymetry and flow regime upon the morphology of sublittoral sponge communities , 2000, Journal of the Marine Biological Association of the United Kingdom.

[38]  J. Collie,et al.  Photographic evaluation of the impacts of bottom fishing on benthic epifauna , 2000 .

[39]  A. S. Hill,et al.  Changes in Irish Sea Benthos: Possible Effects of 40 years of Dredging , 1999 .

[40]  John Cotter,et al.  Distribution, diversity and abundance of epibenthic fauna in the North Sea , 1999, Journal of the Marine Biological Association of the United Kingdom.

[41]  D. Limpenny,et al.  A comparison of benthic biodiversity in the North Sea, English Channel, and Celtic Seas , 1999 .

[42]  M. Kaiser,et al.  Fishing effects in northeast Atlantic shelf seas : patterns in fishing effort, diversity and community structure VII. The effects of trawling disturbance on the fauna associated with the tubeheads of serpulid worms , 1999 .

[43]  B. Cade,et al.  Estimating effects of limiting factors with regression quantiles , 1999 .

[44]  M. Ribes,et al.  Growth in a modular colonial marine invertebrate , 1998 .

[45]  Simon F. Thrush,et al.  DISTURBANCE OF THE MARINE BENTHIC HABITAT BY COMMERCIAL FISHING: IMPACTS AT THE SCALE OF THE FISHERY , 1998 .

[46]  J. Collie,et al.  Effects of bottom fishing on the benthic megafauna of Georges Bank , 1997 .

[47]  D. Kristmanson,et al.  Benthic suspension feeders and flow , 1997 .

[48]  P. Auster,et al.  The impacts of mobile fishing gear on seafloor habitats in the gulf of Maine (Northwest Atlantic): Implications for conservation of fish populations , 1996 .

[49]  S. Thrush,et al.  The impact of habitat disturbance by scallop dredging on marine benthic communities:what can be predicted from the results of experiments? , 1995 .

[50]  R. G. Hughes,et al.  The ecology of marine benthic hydroids , 1995 .

[51]  E. Allison Seasonal growth models for great scallops (Pecten maximus (L.)) and queen scallops (Aequipecten opercularis (L.) , 1994 .

[52]  S. J. Hall Physical disturbance and marine benthic communities: life in unconsolidated sediments , 1994 .

[53]  A. Eleftheriou,et al.  The effects of experimental scallop dredging on the fauna and physical environment of a shallow sandy community , 1992 .

[54]  Joe N. Perry,et al.  A method of estimating the slope of upper bounds of plots of body size and abundance in natural animal assemblages , 1992 .

[55]  C. Emerson Wind stress limitation of benthic secondary production in shallow soft sediment communities , 1989 .

[56]  B. Okamura PARTICLE SIZE AND FLOW VELOCITY INDUCE AN INFERRED SWITCH IN BRYOZOAN SUSPENSION-FEEDING BEHAVIOR. , 1987, The Biological bulletin.

[57]  N. Nicholson,et al.  Effects of a research trawl on a hard-bottom assemblage of sponges and corals , 1987 .

[58]  H. Asmus Secondary production of an intertidal mussel bed community related to its storage and turnover compartments , 1987 .

[59]  M. Labarbera Feeding Currents and Particle Capture Mechanisms in Suspension Feeding Animals , 1984 .

[60]  P. Tett,et al.  Mixing and phytoplankton growth around an island in a stratified sea , 1982 .

[61]  J. Paul NATURAL SETTLEMENT AND EARLY GROWTH OF SPAT OF THE QUEEN SCALLOP CHLAMYS OPERCULARIS (L.), WITH REFERENCE TO THE FORMATION OF THE FIRST GROWTH RING , 1981 .

[62]  J. Oliver,et al.  RELATIONSHIPS BETWEEN WAVE DISTURBANCE AND ZONATION OF BENTHIC INVERTEBRATE COMMUNITIES ALONG A SUBTIDAL HIGH-ENERGY BEACH IN MONTEREY BAY, CALIFORNIA , 1980 .