Daryl Burdon

Daryl Burdon

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Daryl Burdon

Institute of Estuarine & Coastal Studies, University of Hull, Hull HU6 7RX, UK

Research Focus & Metrics

Academic Career Length

21Years (2006-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 February 2011 in Marine Pollution Bulletin
Verified
Journal Article
Closed access
JAJonathan P. Atkins
Jonathan P. Atkins
DBDaryl Burdon
Daryl Burdon
MEMichael Elliott
Michael Elliott
AGAmanda J. Gregory
Amanda J. Gregory

1 March 2007 in Marine Pollution Bulletin
Verified
Journal Article
Closed access
NBNicola Beaumont
Nicola Beaumont
MAMelanie Austen
Melanie Austen
JAJ.P. Atkins
J.P. Atkins
DBD. Burdon
D. Burdon
SDS. Degraer
S. Degraer
TZT. Zarzycki
T. Zarzycki

1 September 2007 in Estuarine, Coastal and Shelf Science
Verified
Journal Article
Closed access
MEMichael Elliott
Michael Elliott
DBDaryl Burdon
Daryl Burdon
KHKrystal L. Hemingway
Krystal L. Hemingway
SASabine E. Apitz
Sabine E. Apitz

1 May 2017 in Marine Pollution Bulletin
Verified
Journal Article
Open access
MEMichael Elliott
Michael Elliott
DBD. Burdon
D. Burdon
JAJ.P. Atkins
J.P. Atkins
BABorja Angel
Borja Angel
RCR. Cormier
R. Cormier
RTR.K. Turner
R.K. Turner
The marine environment is a complex system formed by interactions between ecological structure and functioning, physico-chemical processes and socio-economic systems. An increase in competing marine uses and users requires a holistic approach to marine management which considers the environmental, economic and societal impacts of all activities. If managed sustainably, the marine environment will deliver a range of ecosystem services which lead to benefits for society. In order to understand the complexity of the system, the DPSIR (Driver-Pressure-State-Impact-Response) approach has long been a valuable problem-structuring framework used to assess the causes, consequences and responses to change in a holistic way. Despite DPSIR being used for a long time, there is still confusion over the definition of its terms and so to be appropriate for current marine management, we contend that this confusion needs to be addressed. Our viewpoint advocates that DPSIR should be extended to DAPSI(W)R(M) (pronounced dap-see-worm) in which Drivers of basic human needs require Activities which lead to Pressures. The Pressures are the mechanisms of State change on the natural system which then leads to Impacts (on human Welfare). Those then require Responses (as Measures). Furthermore, because of the complexity of any managed sea area in terms of multiple Activities, there is the need for a linked-DAPSI(W)R(M) framework, and then the connectivity between marine ecosystems and ecosystems in the catchment and further at sea, requires an interlinked, nested-DAPSI(W)R(M) framework to reflect the continuum between adjacent ecosystems. Finally, the unifying framework for integrated marine management is completed by encompassing ecosystem structure and functioning, ecosystem services and societal benefits. Hence, DAPSI(W)R(M) links the socio-ecological system of the effects of changes to the natural system on the human uses and benefits of the marine system. However, to deliver these sustainably in the light of human activities requires a Risk Assessment and Risk Management framework; the ISO-compliant Bow-Tie method is used here as an example. Finally, to secure ecosystem health and economic benefits such as Blue Growth, successful, adaptive and sustainable marine management Responses (as Measures) are delivered using the 10-tenets, a set of facets covering all management disciplines and approaches.

1 February 2015 in Ecological Indicators
Verified
Journal Article
Open access
CHCaroline Hattam
Caroline Hattam
JAJonathan P. Atkins
Jonathan P. Atkins
NBNicola Beaumont
Nicola Beaumont
TBTobias Bӧrger
Tobias Bӧrger
ABAnne Bӧhnke-Henrichs
Anne Bӧhnke-Henrichs
MAMelanie Austen
Melanie Austen
15 pages, 1 figure, 4 tablesThere is a multitude of ecosystem service classifications available within the literature, each with its own advantages and drawbacks. Elements of them have been used to tailor a generic ecosystem service classification for the marine environment and then for a case study site within the North Sea: the Dogger Bank. Indicators for each of the ecosystem services, deemed relevant to the case study site, were identified. Each indicator was then assessed against a set of agreed criteria to ensure its relevance and applicability to environmental management. This paper identifies the need to distinguish between indicators of ecosystem services that are entirely ecological in nature (and largely reveal the potential of an ecosystem to provide ecosystem services), indicators for the ecological processes contributing to the delivery of these services, and indicators of benefits that reveal the realized human use or enjoyment of an ecosystem service. It highlights some of the difficulties faced in selecting meaningful indicators, such as problems of specificity, spatial disconnect and the considerable uncertainty about marine species, habitats and the processes, functions and services they contribute to. © 2014 Elsevier Ltd. All rights reservedThe research leading to these results has received funding from the European Community’s Seventh Framework Programme (FP7/2007–2013) within the Ocean of Tomorrow call under Grant Agreement No. 266445 for the project Vectors of Change in Oceans and Seas Marine Life, Impact on Economic Sectors (VECTORS). This paper is based on the outputs of a workshop held in Rome 2012 as part of the VECTORS project involving researchers from multiple disciplines (including natural and social sciences and economics) and from subsequent refinementsPeer Reviewe

1 February 2014 in Marine Policy
Verified
Journal Article
Closed access
TPTavis Potts
Tavis Potts
DBDaryl Burdon
Daryl Burdon
EJEmma Jackson
Emma Jackson
JAJonathan Atkins
Jonathan Atkins
JSJustine Saunders
Justine Saunders
OLOlivia Langmead
Olivia Langmead