Kenneth Irvine

Prof. Dr. Kenneth Irvine

Aquatic Ecosystems Group, IHE Delft Institute of Water Education, POB 3015, NL-2601 DA Delft, The Netherlands
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Research Focus & Metrics

Academic Career Length

41Years (1986-Present)

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

Representative Publications

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13 August 2018 in Aquatic Conservation: Marine and Freshwater Ecosystems
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WDWilliam Darwall
William Darwall
VBVanessa Bremerich
Vanessa Bremerich
AWAaike De Wever
Aaike De Wever
ADAnthony I. Dell
Anthony I. Dell
JFJörg Freyhof
Jörg Freyhof
OWOlaf Weyl
Olaf Weyl

31 March 2003 in Aquatic Conservation: Marine and Freshwater Ecosystems
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BMBrian Moss
Brian Moss
DSDeborah Stephen
Deborah Stephen
CACristina Alvarez
Cristina Alvarez
EBEloy Becares
Eloy Becares
WBWouter Van De Bund
Wouter Van De Bund
DWDavid Wilson
David Wilson
The European Water Framework Directive requires the determination of ecological status in European fresh and saline waters. This is to be through the establishment of a typology of surface water bodies, the determination of reference (high status) conditions in each element (ecotype) of the typology and of lower grades of status (good, moderate, poor and bad) for each ecotype. It then requires classification of the status of the water bodies and their restoration to at least ‘good status’ in a specified period. Though there are many methods for assessing water quality, none has the scope of that defined in the Directive. The provisions of the Directive require a wide range of variables to be measured and give only general guidance as to how systems of classification should be established. This raises issues of comparability across States and of the costs of making the determinations. Using expert workshops and subsequent field testing, a practicable pan‐European typology and classification system has been developed for shallow lakes, which can easily be extended to all lakes. It is parsimonious in its choice of determinands, but based on current limnological understanding and therefore as cost‐effective as possible. A core typology is described, which can be expanded easily in particular States to meet local conditions. The core includes 48 ecotypes across the entire European climate gradient and incorporates climate, lake area, geology of the catchment and conductivity. The classification system is founded on a liberal interpretation of Annexes in the Directive and uses variables that are inexpensive to measure and ecologically relevant. The need for taxonomic expertise is minimized. The scheme has been through eight iterations, two of which were tested in the field on tranches of 66 lakes. The final version, Version 8, is offered for operational testing and further refinement by statutory authorities. Copyright © 2003 John Wiley & Sons, Ltd.

1 December 2009 in Ecology
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IDIan Donohue
Ian Donohue
AJAndrew L. Jackson
Andrew L. Jackson
MPMartin T. Pusch
Martin T. Pusch
Kenneth IrvineKenneth Irvine
Kenneth Irvine
The compositional heterogeneity of biotic assemblages among sites, or β‐diversity, regulates the relationship between local and regional species diversity across scales. Recent work has suggested that increased harshness of environmental conditions tends to reduce β‐diversity by decreasing the importance of stochastic processes in structuring assemblages. We investigated the effect of nutrient enrichment on the compositional heterogeneity of lake benthic invertebrate assemblages in Ireland at both local (within‐lake) and regional (among‐lake) scales. At local scales, we found that the compositional heterogeneity of benthic assemblages was related inversely to the extent of nutrient enrichment (as indicated by measurements of water column total phosphorus, total nitrogen, and chlorophyll a), after effects of lake morphology (i.e., surface area, connectivity, and depth of sampling) and alkalinity were accounted for. At regional scales, we found that nutrient‐rich lakes had significantly more homogenous benthic assemblages than nutrient‐poor lakes, over and above the effect of alkalinity and across a similar range of lake morphologies. These findings have profound implications for global aquatic biodiversity, as the homogenization of benthic assemblages at both local and regional scales may have important and unpredictable effects on whole aquatic ecosystems, with potentially considerable ecological and evolutionary consequences.

18 November 2005 in Limnology and Oceanography
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MGM. Gyllström
M. Gyllström
LHLars-Anders Hansson
Lars-Anders Hansson
Erik JeppesenErik Jeppesen
Erik Jeppesen
FCF. García Criado
F. García Criado
EGElisabeth M. Gross
Elisabeth M. Gross
BMB. Moss
B. Moss
We analyzed data from 81 shallow European lakes, which were sampled with standardized methods, for combined effects of climatic, physical, and chemical features of food‐web interactions, with a specific focus on zooplankton biomass and community structure. multiple‐regression analysis showed that total phosphorus (TP) generally was the most important predictor of zooplankton biomass and community structure. Climate was the next most important predictor and acted mainly through its effect on pelagic zooplankton taxa. Benthic and plant‐associated taxa (typically almost half the total zooplankton biomass) were, however, affected mainly by macrophyte coverage. Neither climate nor TP affected the relation between small and large taxa, and we found only a weak trend with increasing TP of increasing mean crustacean body mass. Dividing the data set into three climate zones revealed a pronounced difference in response to lake productivity between cold lakes, with long periods of ice cover, and the two warmer lake types. These ÂÂice lakes differed from the others with respect to the effect of TP on chlorophyll a, the zooplankton : chlorophyll a ratio, the chlorophyll a :TP ratio, and the proportion of cyclopoids in the copepod community. Our data suggest that bottom‐up forces, such as nutrient concentration, are the most important predictors of zooplankton biomass. In addition, climate contributes significantly—possibly by affecting top‐down regulation by fish—and may interact with productivity in determining the zooplankton standing biomass and community composition. Hence, the present study suggests that food‐web dynamics are closely linked to climatic features.

19 April 2016 in Water
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NJNicolas W. Jager
Nicolas W. Jager
ECEdward Challies
Edward Challies
EKElisa Kochskämper
Elisa Kochskämper
JNJens Newig
Jens Newig
David BensonDavid Benson
David Benson
YKYorck Von Korff
Yorck Von Korff
The European Union (EU) Water Framework Directive (WFD) requires EU member states to produce and implement river basin management plans, which are to be designed and updated via participatory processes that inform, consult with, and actively involve all interested stakeholders. The assumption of the European Commission is that stakeholder participation, and institutional adaptation and procedural innovation to facilitate it, are essential to the effectiveness of river basin planning and, ultimately, the environmental impact of the Directive. We analyzed official documents and the WFD literature to compare implementation of the Directive in EU member states in the initial WFD planning phase (2000–2009). Examining the development of participatory approaches to river basin management planning, we consider the extent of transformation in EU water governance over the period. Employing a mixed quantitative and qualitative approach, we map the implementation “trajectories” of 13 member states, and then provide a detailed examination of shifts in river basin planning and participation in four member states (Germany, Sweden, Poland and France) to illustrate the diversity of institutional approaches observed. We identify a general tendency towards increased, yet circumscribed, stakeholder participation in river basin management in the member states examined, alongside clear continuities in terms of their respective pre-WFD institutional and procedural arrangements. Overall, the WFD has driven a highly uneven shift to river basin-level planning among the member states, and instigated a range of efforts to institutionalize stakeholder involvement—often through the establishment of advisory groups to bring organized stakeholders into the planning process.

1 June 2014 in Freshwater Science
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Frank MaseseFrank Masese
Frank Masese
NKNzula Kitaka
Nzula Kitaka
JKJulius Kipkemboi
Julius Kipkemboi
GGGretchen M. Gettel
Gretchen M. Gettel
Kenneth IrvineKenneth Irvine
Kenneth Irvine
MMMichael E. McClain
Michael E. McClain