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Groundwater ecosystems
Research from England Tim Besien and Tim Johns 5 October 2015
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Talk summary Why? Species & communities Distribution & drivers
Habitat preferences Food webs Hypogean Crustacea Recording Scheme
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Why? Recital 20 in the Groundwater Directive 2006
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Species & communities Only 8 species of GW macro Crustacea reported in England These are obligate GW animals termed - stygobites Majority limited to southern England – glacial legacy? Niphargus glenniei – endemic to SW England Microniphargus leruthi – first record in England 2010 Hypogean Custacea Recording Scheme (Lee Knight) Photo by Chris Proctor Environment Agency N glenniei, UK Biological Action Plan species Robertson, A. L., et al. "The distribution and diversity of stygobites in Great Britain: an analysis to inform groundwater management." Quarterly Journal of Engineering Geology and Hydrogeology 42.3 (2009):
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Molecular study – interesting!
UK Niphargid populations have a distinct lineage Divergence from continental Europe N. kochianus 2.9 Ma N. aquilex Ma N. fontanus 0.8 Ma N. glenniei, the most ancient endemic British fauna, 19.5Ma Important biodiversity element, resilience to climate change BUT vulnerable to other human pressures McInerney et al., Molecular Ecology McInerney, Caitríona E., et al. "The ancient Britons: groundwater fauna survived extreme climate change over tens of millions of years across NW Europe." Molecular ecology 23.5 (2014):
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Regional-scale drivers
Study of ~200 wells & BHs in SW England – presence/absence & abundance of species recorded with geology and WQ data GW fauna recorded in all geological ‘hydro-units’ examined BUT significantly more likely in carbonate & igneous/metamorphic rocks than mudstones and sandstones CCA & variance portioning indicated geology (hydro-units) relatively more important than WQ in explaining GW community observed. Distinct distribution of species observed – geological barrier may explain this & absence of N. glenniei west of Devon Johns et al, 2014 Regional-scale drivers of groundwater faunal distributions Johns, Tim, et al. "Regional-scale drivers of groundwater faunal distributions."Freshwater Science 34.1 (2015):
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Invertebrate fauna of Chalk GW
Samples from BHs in Chalk – recovered using a plankton net Stygobites present in ~ 70 % BHs. N. kochinanus most common species recorded GW fauna present in deep & shallow BHs (100m BGL & at least 70m BWT) No stygobites recorded from confined Chalk (limited samples) Maurice et al (in press) The invertebrate ecology of Chalk groundwater Maurice et al (in press) The invertebrate ecology of Chalk groundwater, Hydrogeology Journal
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The Chalk habitat Packer tests on 3 fractures identified in chalk BH in southern England 5000 litres (2l/s) - water chemistry tested & fauna recovered Water chemistry remained similar, GW fauna ubiquitous Suggests suitable habitat but population estimations difficult CCTV used to provide supporting evidence 82m bgl Sorensen et al , Using boreholes as windows into groundwater ecosystems Sorensen, James PR, et al. "Using boreholes as windows into groundwater ecosystems." PloS one 8.7 (2013): e70264.
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Ecology studies Hypogean Crustacea Recording Scheme Few studies on auto-ecology of Niphargus species in Britain Phototactic & temperature responses investigated for N aquilex & N glenniei in experimental aquarium in a Devon cave Both species tolerant to wide temperature range (1-26oc). Entered torpor ~2-4oc Negative phototactic response suggested by other studies not obvious, N aquilex showed weak response, most strongly to UV light Study supported by grant from British Cave Research Association Knight Lee RFD & Johns T “Auto-ecological studies on Niphargus aquilex (Schiödte, 1855) and Niphargus glenniei (Spooner, 1952) (Crustacea: Amphipoda: Niphargidae)” Cave & Karst Science 42.2(2015):63-77
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GW community response to flooding
Tracked changes in GW community (bacterial, protozoan, micrometazoan & macrofauna) following significant flooding event (2014) Two spatially separated chalk aquifers, 4 BHs in each, sampled every 2 weeks for 7 months DOC concentrations & bacterial abundance – higher just after recharge event, then declined Macrofaunal abundance increased with time but biomass lower (more juvenilies) GW communities showed strong size structure, indicative of stable environment Robertson et al (in preparation) Groundwater Flooding: groundwater community recovery following an extreme recharge event.
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Groundwater food webs – ongoing PhD
Dissolved Organic Carbon (DOC) Particulate Organic Matter (POM) Bacteria Protozoa (e.g. ciliates, flagellates, amoebae) Meiofauna (e.g. copepods, nematodes) Macrofauna (e.g. crustaceans, cave fish) Low complexity, truncated ecosystems Stygobites are top level predators Effects of these predators on protozoans have not been explored to date Ideal for study of example ecological networks – focus of current PhD Flow of Energy / Biomass through trophic levels Return of Energy / Biomass through bacterial degradation of all trophic levels Weitowitz, D.; Reiss, J.; Robertson, A. University of Roehampton
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Summary UK is working on the research requirements set out in the GWD
Still lots of unknowns Further work needed, particularly on the impacts of anthropogenic pressures Research networks - Paul Wood, Loughborough University has set up an EU-wide group to seek consensus on research directions
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Key contributors to recent studies
Lee Knight – Hypogean Crustacea Recording Scheme (UK) Tim Johns – Environment Agency Anne Robertson – Roehampton University Damiano Weitowitz – Roehampton University Lou Maurice – British Geological Survey Paul Wood – Loughborough University Bernd Hänfling – Hull Univeristy Caitriona McInerney – Hull University Studies listed
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