Gabor Varbiro

Dr. Gabor Varbiro

GINOP Sustainable Ecosystems Group, DRI Department of Tisza Research, MTA Centre for Ecological Research, Hungary
orcid

Research Focus & Metrics

Academic Career Length

24Years (2003-Present)

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

Representative Publications

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1 August 2019 in Science of The Total Environment
Verified
Journal Article
Open access
HWHannah Weigand
Hannah Weigand
ABArne J. Beermann
Arne J. Beermann
FČFedor Čiampor
Fedor Čiampor
Filipe CostaFilipe Costa
Filipe Costa
ZCZoltán Csabai
Zoltán Csabai
TETorbjørn Ekrem
Torbjørn Ekrem
Effective identification of species using short DNA fragments (DNA barcoding and DNA metabarcoding) requires reliable sequence reference libraries of known taxa. Both taxonomically comprehensive coverage and content quality are important for sufficient accuracy. For aquatic ecosystems in Europe, reliable barcode reference libraries are particularly important if molecular identification tools are to be implemented in biomonitoring and reports in the context of the EU Water Framework Directive (WFD) and the Marine Strategy Framework Directive (MSFD). We analysed gaps in the two most important reference databases, Barcode of Life Data Systems (BOLD) and NCBI GenBank, with a focus on the taxa most frequently used in WFD and MSFD. Our analyses show that coverage varies strongly among taxonomic groups, and among geographic regions. In general, groups that were actively targeted in barcode projects (e.g. fish, true bugs, caddisflies and vascular plants) are well represented in the barcode libraries, while others have fewer records (e.g. marine molluscs, ascidians, and freshwater diatoms). We also found that species monitored in several countries often are represented by barcodes in reference libraries, while species monitored in a single country frequently lack sequence records. A large proportion of species (up to 50%) in several taxonomic groups are only represented by private data in BOLD. Our results have implications for the future strategy to fill existing gaps in barcode libraries, especially if DNA metabarcoding is to be used in the monitoring of European aquatic biota under the WFD and MSFD. For example, missing species relevant to monitoring in multiple countries should be prioritized for future collaborative programs. We also discuss why a strategy for quality control and quality assurance of barcode reference libraries is needed and recommend future steps to ensure full utilisation of metabarcoding in aquatic biomonitoring.

9 August 2023 in Nature
Verified
Journal Article
Open access
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PHPeter Haase
Peter Haase
DBDiana E. Bowler
Diana E. Bowler
NBNathan Jay Baker
Nathan Jay Baker
NBNúria Bonada
Núria Bonada
SDSami Domisch
Sami Domisch
EWEllen A. R. Welti
Ellen A. R. Welti
Owing to a long history of anthropogenic pressures, freshwater ecosystems are among the most vulnerable to biodiversity loss1. Mitigation measures, including wastewater treatment and hydromorphological restoration, have aimed to improve environmental quality and foster the recovery of freshwater biodiversity2. Here, using 1,816 time series of freshwater invertebrate communities collected across 22 European countries between 1968 and 2020, we quantified temporal trends in taxonomic and functional diversity and their responses to environmental pressures and gradients. We observed overall increases in taxon richness (0.73% per year), functional richness (2.4% per year) and abundance (1.17% per year). However, these increases primarily occurred before the 2010s, and have since plateaued. Freshwater communities downstream of dams, urban areas and cropland were less likely to experience recovery. Communities at sites with faster rates of warming had fewer gains in taxon richness, functional richness and abundance. Although biodiversity gains in the 1990s and 2000s probably reflect the effectiveness of water-quality improvements and restoration projects, the decelerating trajectory in the 2010s suggests that the current measures offer diminishing returns. Given new and persistent pressures on freshwater ecosystems, including emerging pollutants, climate change and the spread of invasive species, we call for additional mitigation to revive the recovery of freshwater biodiversity.

1 October 2016 in Environmental Science & Policy
Verified
Journal Article
Closed access
DCDeborah V. Chapman
Deborah V. Chapman
CBChris Bradley
Chris Bradley
GGGretchen M. Gettel
Gretchen M. Gettel
István Gábor HatvaniIstván Gábor Hatvani
István Gábor Hatvani
Thomas HeinThomas Hein
Thomas Hein
Gabor VarbiroGabor Varbiro
Gabor Varbiro

1 July 2014 in Soil Biology and Biochemistry
Verified
Journal Article
Closed access
IFIstván Fekete
István Fekete
KZKotroczó Zsolt
Kotroczó Zsolt
CVCsaba Varga
Csaba Varga
PNPéter Tamás Nagy
Péter Tamás Nagy
Gabor VarbiroGabor Varbiro
Gabor Varbiro
KLKate Lajtha
Kate Lajtha

15 May 2022 in Global Change Biology
Verified
Journal Article
Open access
PHPhillip J. Haubrock
Phillip J. Haubrock
DADanish Ali Ahmed
Danish Ali Ahmed
RCRoss Cuthbert
Ross Cuthbert
RSRachel Stubbington
Rachel Stubbington
SDSami Domisch
Sami Domisch
PHPeter Haase
Peter Haase
Globalization has led to the introduction of thousands of alien species worldwide. With growing impacts by invasive species, understanding the invasion process remains critical for predicting adverse effects and informing efficient management. Theoretically, invasion dynamics have been assumed to follow an “invasion curve” (S‐shaped curve of available area invaded over time), but this dynamic has lacked empirical testing using large‐scale data and neglects to consider invader abundances. We propose an “impact curve” describing the impacts generated by invasive species over time based on cumulative abundances. To test this curve's large‐scale applicability, we used the data‐rich New Zealand mud snailPotamopyrgus antipodarum, one of the most damaging freshwater invaders that has invaded almost all of Europe. Using long‐term (1979–2020) abundance and environmental data collected across 306 European sites, we observed thatP. antipodarumabundance generally increased through time, with slower population growth at higher latitudes and with lower runoff depth. Fifty‐nine percent of these populations followed the impact curve, characterized by first occurrence, exponential growth, then long‐term saturation. This behaviour is consistent with boom‐bust dynamics, as saturation occurs due to a rapid decline in abundance over time. Across sites, we estimated that impact peaked approximately two decades after first detection, but the rate of progression along the invasion process was influenced by local abiotic conditions. The S‐shaped impact curve may be common among many invasive species that undergo complex invasion dynamics. This provides a potentially unifying approach to advance understanding of large‐scale invasion dynamics and could inform timely management actions to mitigate impacts on ecosystems and economies.

1 February 2021 in Ecological Indicators
Verified
Journal Article
Open access
Sandra PoikaneSandra Poikane
Sandra Poikane
Gabor VarbiroGabor Varbiro
Gabor Varbiro
MKMartyn G. Kelly
Martyn G. Kelly
Sebastian BirkSebastian Birk
Sebastian Birk
GPGeoff Phillips
Geoff Phillips