Patrik Henriksson

Mr. Patrik Henriksson


Research Focus & Metrics

Academic Career Length

19Years (2008-Present)

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

Representative Publications

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15 September 2021 in Nature
Verified
Journal Article
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JGJessica A. Gephart
Jessica A. Gephart
PHPatrik Henriksson
Patrik Henriksson
RPRobert W. R. Parker
Robert W. R. Parker
ASAlon Shepon
Alon Shepon
KGKelvin D. Gorospe
Kelvin D. Gorospe
MTMax Troell
Max Troell

9 January 2015 in Science
Verified
Journal Article
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LCLing Cao
Ling Cao
RNRosamond Lee Naylor
Rosamond Lee Naylor
PHPatrik Henriksson
Patrik Henriksson
DLDuncan Leadbitter
Duncan Leadbitter
MMMarc Metian
Marc Metian
WZWenbo Zhang
Wenbo Zhang
China is the world's largest producer, consumer, processor, and exporter of finfish and shellfish (defined here as “fish”), and its fish imports are steadily rising (1–3). China produces more than one-third of the global fish supply, largely from its ever-expanding aquaculture sector, as most of its domestic fisheries are overexploited (3–6). Aquaculture accounts for ∼72% of its reported domestic fish production, and China alone contributes >60% of global aquaculture volume and roughly half of global aquaculture value (1, 3).

1 November 2013 in Aquaculture
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Journal Article
Closed access
Andreu RicoAndreu Rico
Andreu Rico
MTMinh Phu Tran
Minh Phu Tran
KSKriengkrai Satapornvanit
Kriengkrai Satapornvanit
JMJiang Min
Jiang Min
ASA.M. Shahabuddin
A.M. Shahabuddin
PBPaul J. Van Den Brink
Paul J. Van Den Brink

21 November 2011 in Annual Review of Environment and Resources
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Journal Article
Closed access
NPNathan Pelletier
Nathan Pelletier
EAEric Audsley
Eric Audsley
SBSonja Brodt
Sonja Brodt
TGTara Garnett
Tara Garnett
PHPatrik Henriksson
Patrik Henriksson
MTMax Troell
Max Troell
The relationships between energy use in food systems, food system productivity, and energy resource constraints are complex. Moreover, ongoing changes in food production and consumption norms concurrent with urbanization, globalization, and demographic changes underscore the importance of energy use in food systems as a food security concern. Here, we review the current state of knowledge with respect to the energy intensity of agriculture and food systems. We highlight key drivers and trends in food system energy use along with opportunities for and constraints on improved efficiencies. In particular, we point toward a current dearth of research with respect to the energy performance of food systems in developing countries and provide a cautionary note vis-à-vis increasing food system energy dependencies in the light of energy price volatility and concerns as to long-term fossil energy availabilities.

18 November 2017 in Sustainability Science
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Journal Article
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PHPatrik Henriksson
Patrik Henriksson
Andreu RicoAndreu Rico
Andreu Rico
MTMax Troell
Max Troell
DKDane H. Klinger
Dane H. Klinger
ABAlejandro H. Buschmann
Alejandro H. Buschmann
WZWenbo Zhang
Wenbo Zhang
Global seafood provides almost 20% of all animal protein in diets, and aquaculture is, despite weakening trends, the fastest growing food sector worldwide. Recent increases in production have largely been achieved through intensification of existing farming systems, resulting in higher risks of disease outbreaks. This has led to increased use of antimicrobials (AMs) and consequent antimicrobial resistance (AMR) in many farming sectors, which may compromise the treatment of bacterial infections in the aquaculture species itself and increase the risks of AMR in humans through zoonotic diseases or through the transfer of AMR genes to human bacteria. Multiple stakeholders have, as a result, criticized the aquaculture industry, resulting in consequent regulations in some countries. AM use in aquaculture differs from that in livestock farming due to aquaculture’s greater diversity of species and farming systems, alternative means of AM application, and less consolidated farming practices in many regions. This, together with less research on AM use in aquaculture in general, suggests that large data gaps persist with regards to its overall use, breakdowns by species and system, and how AMs become distributed in, and impact on, the overall social-ecological systems in which they are embedded. This paper identifies the main factors (and challenges) behind application rates, which enables discussion of mitigation pathways. From a set of identified key mechanisms for AM usage, six proximate factors are identified: vulnerability to bacterial disease, AM access, disease diagnostic capacity, AMR, target markets and food safety regulations, and certification. Building upon these can enable local governments to reduce AM use through farmer training, spatial planning, assistance with disease identification, and stricter regulations. National governments and international organizations could, in turn, assist with disease-free juveniles and vaccines, enforce rigid monitoring of the quantity and quality of AMs used by farmers and the AM residues in the farmed species and in the environment, and promote measures to reduce potential human health risks associated with AMR.

24 December 2011 in The International Journal of Life Cycle Assessment
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Journal Article
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PHPatrik Henriksson
Patrik Henriksson
JGJeroen B. Guinée
Jeroen B. Guinée
RKRené Kleijn
René Kleijn
GSGeert R. de Snoo
Geert R. de Snoo
Purpose As capture fishery production has reached its limits and global demand for aquatic products is still increasing, aquaculture has become the world’s fastest growing animal production sector. In attempts to evaluate the environmental consequences of this rapid expansion, life cycle assessment (LCA) has become a frequently used method. The present review of current peer-reviewed literature focusing on LCA of aquaculture systems is intended to clarify the methodological choices made, identify possible data gaps, and provide recommendations for future development within this field of research. The results of this review will also serve as a start-up activity of the EU FP7 SEAT (Sustaining Ethical Aquaculture Trade) project, which aims to perform several LCA studies on aquaculture systems in Asia over the next few years. Methods From a full analysis of methodology in LCA, six phases were identified to differ the most amongst ten peer-reviewed articles and two PhD theses (functional unit, system boundaries, data and data quality, allocation, impact assessment methods, interpretation methods). Each phase is discussed with regards to differences amongst the studies, current LCA literature followed by recommendations where appropriate. The conclusions and recommendations section reflects on aquaculture-specific scenarios as well as on some more general issues in LCA. Results Aquaculture LCAs often require large system boundaries, including fisheries, agriculture, and livestock production systems from around the globe. The reviewed studies offered limited coverage of production in developing countries, low-intensity farming practices, and non-finfish species, although most farmed aquatic products originate from a wide range of farming practices in Asia. Apart from different choices of functional unit, system boundaries and impact assessment methods, the studies also differed in their choice of allocation factors and data sourcing. Interpretation of results also differed amongst the studies, and a number of methodological choices were identified influencing the outcomes. Conclusions and recommendations Efforts should be made to increase transparency to allow the results to be reproduced, and to construct aquaculture related database(s). More extensive data reporting, including environmental flows, within the greater field of LCA could be achieved, without compromising the focus of studies, by providing supporting information to articles and/or reporting only ID numbers from background databases. More research is needed into aquaculture in Asia based on the latest progress made by the LCA community.