Porewater and microbial community properties of permeable riverbed sediments across the south of England, 2018
This dataset contains in-stream measurements of sediment porewater nutrients, nitrification rates (and the fraction which is either fully oxidised to nitrate or reduced to N2 gas), and the abundance of microbial 16S rRNA and specific N-cycling genes and transcripts. Sediments were sampled in winter (February 2018) and summer (July 2018), from 12 UK rivers with permeable beds (sand or chalk geology) and a gradient of P concentrations, in the Hampshire Avon catchment, Kent, and Essex. Methods included measurements of porewater nutrients using Skalar SAN++AutoAnalyser, nitrification rates from in-situ ‘push-pull’ injections of 15N-labelled ammonia and -nitrite, and sediment microbial gene and transcript abundance by DNA extraction and qPCR. The work was supported by the Natural Environment Research Council (Grants NE/P01142X/1, NE/P011624/1; A new dynamic for Phosphorus in RIverbed Nitrogen Cycling - PRINCe Full details about this dataset can be found at https://doi.org/10.5285/d432d96c-7aff-45a5-9d4b-37e4065afdd7
dataset
https://data-package.ceh.ac.uk/data/d432d96c-7aff-45a5-9d4b-37e4065afdd7
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https://data-package.ceh.ac.uk/sd/d432d96c-7aff-45a5-9d4b-37e4065afdd7.zip
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https://catalogue.ceh.ac.uk/id/d432d96c-7aff-45a5-9d4b-37e4065afdd7
doi:
eng
inlandWaters
Environmental Monitoring Facilities
publication
2008-06-01
Rivers
Chalk
Nitrogen cycle
ammonium
nitrite
nitrate
phosphate
nitrogen
15N
nitrification
Comammox
Anammox
NirS
nosZ
amoA
hzo
hzs
nirK
nirS
nrxB
ureC
ammonia oxidising
AOA
AOB
Lambourn
Cray
Ash
Darent
Wylye
Rib
Plant
Stour
Ebble
Marden
Medway
Broadstone
Nadder
Bacteria
Greensand
Archaea
16S rRNA
-2.2
0.96
52
51.02
2018-02-01
2018-07-31
publication
2022-02-08
Two field campaigns were conducted in 2018 in winter [February] and summer [2018] seasons) to measure in situ rates of nitrogen transformations, porewater chemistry and microbial gene abundance and transcripts in 12 rivers with permeable beds and varying concentrations of phosphorous in the Hampshire Avon catchment, Kent, and Essex. Nitrogen transformations were measured and porewater samples collected with a “push-pull” technique. Briefly, 15 bespoke stainless steel probes were installed in the riverbed at two depths (7 at 5cm and 8 at 10cm) to cover three unvegetated sediment patches. Porewater samples were obtained by a syringe connected to the porewater probe and applying a slight vacuum (by hand). From each probe, the O2 and pH content of the porewater was first determined and a newly collected porewater sample was preserved for gas analysis. Porewater Temperature and pH were measured with a Hach multi-meter and O2 concentrations were measured with a fast response microelectrode. Finally, another freshly collected porewater sample was passed through a 0.45 micron polypropylene filter and frozen for later nutrient (ammonium, nitrite, nitrate phosphate) analysis on a Skalar SAN++ auto analyser. To measure rates of nitrogen transformations, 15N-labelled ammonium or nitrate was injected into riverbed and porewater samples for gas and nutrient/chloride analysis were recovered from the same probe over time. The tracer was 300 microM, 98 atom % 15N-ammonium or nitrate in a synthetic river water matrix with additional KCl (approx. 150 mg per L). Each experiment used 25mL of tracer, consisted of 4-time points (immediately following the injection plus 3 others) and lasted for no more than 60 minutes in total. For each sediment patch, a single 2cm sediment core was taken (before push-pull analyses) and subsampled at 5 and 10cm depths for molecular analyses. The core was positioned no less than 20cm from a push-pull probe to avoid surface water intrusion into the porespace. Subsamples were then cryopreserved in liquid N2. 16S rRNA and N-cycle functional genes and transcripts were quantified by qPCR and RT-qPCR on a on a BioRad CFX384 following extraction of RNA and DNA with PowerSoil DNA or RNA Isolation kits (Qiagen). Genes were also amplified via PCR, indexed using Nextera XT indices (Illumina) and sequenced using MiSeq Reagent Kits v3 (600-cycle)on an Illumina MiSeq sequencer in 4 sequencing runs.
publication
2010-12-08
Comma-separated values (CSV)
If you reuse this data, you should cite: Clark, D.R., Greenwood, B.N., Ma, C., Si, Y., Thomas, G.E., Laissue, P., Whitby, C., McKew, B.A., Trimmer, M. (2022). Porewater and microbial community properties of permeable riverbed sediments across the south of England, 2018. NERC EDS Environmental Information Data Centre https://doi.org/10.5285/d432d96c-7aff-45a5-9d4b-37e4065afdd7
University of Essex
author
University of Essex
author
Queen Mary University of London
author
Queen Mary University of London
author
University of Essex
author
University of Essex
author
University of Essex
author
University of Essex
author
Queen Mary University of London
author
University of Essex
pointOfContact
NERC EDS Environmental Information Data Centre
custodian
NERC EDS Environmental Information Data Centre
publisher
University of Essex
owner
Queen Mary University of London
owner
Environmental Information Data Centre
Lancaster Environment Centre, Library Avenue, Bailrigg
Lancaster
LA1 4AP
UK
pointOfContact
2023-01-05T16:43:23