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  • 2015-2019  (265)
  • 1985-1989  (50)
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  • 1
    Monograph available for loan
    Monograph available for loan
    Oxford : North Oxford Acad. Press
    Call number: G 8836
    Type of Medium: Monograph available for loan
    Pages: XI, 190 S. : graph. Darst.
    ISBN: 0946536503
    Series Statement: Studies in geology
    Uniform Title: Les Granites des complexes annulaires
    Language: English
    Location: Upper compact magazine
    Branch Library: GFZ Library
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  • 2
    Call number: 9780191079993 (e-book)
    Type of Medium: 12
    Pages: 1 online resource (254 pages)
    Edition: First edition
    ISBN: 9780191079993 (e-book)
    Language: English
    Note: Contents Acknowledgments 1 Introduction to environmental DNA (eDNA) 1.1 Definitions 1.2 A brief history of eDNA analysis 1.3 Constraints when working with eDNA 1.4 Workflow in eDNA studies and main methods used 1.5 Environmental DNA as a monitoring tool 2 DNA metabarcode choice and design 2.1 Which DNA metabarcode? 2.2 Properties of the ideal DNA metabarcode 2.3 In silica primer design and testing 2.3.1 Prerequisites 2.3.2 Reference sequences: description, filtering, and formatting for ecoPrimers 2.3.3 In silica primer design with ecoPrimers 2.3.3.1 'Ihe ecoPrimers output 2.3.4 In silica primer testing with ecoPCR 2.3.4.1 The ecoPCR output 2.3.4.2 Filtering of the ecoPCR output 2.3.4.3 Evaluation of primer conservation 2.3.4.4 Taxonomic resolution and Bs index 2.4 Examples of primer pairs available for DNA metabarcoding 3 Reference databases 3.1 Extracting reference databases from EMBL/GenBank/DDBJ 3.1.1 Downloading a local copy of EMBL 3.1.2 Identifying sequences corresponding to the relevant metabarcode 3.2 Marker-specific reference databases 3.2.1 Nuclear rRNA gene reference databases 3.2.2 Eukaryote-specific databases 3.3 Building a local reference database 3.3.1 PCR-based local reference database 3.3.2 Shotgun-based local reference database 3.4 Current challenges and future directions 4 Sampling 4.1 The cycle of eDNA in the environment 4.1.1 State and origin 4.1.2 Fate 4.1.3 Transport 4.2 Sampling design 4.2.1 Focusing on the appropriate DNA population 4.2.2 Defining the sampling strategy 4.3 Sample preservation 5 DNA extraction 5.1 From soil samples 5.2 From sediment 5.3 From litter 5.4 From fecal samples 5.5 From water samples 6 DNA amplification and multiplexing 6.1 Principle of the PCR 6.2 Which polymerase to choose? 6.3 The standard PCR reaction 6.4 The importance of including appropriate controls 6.4.1 Extraction negative controls 6.4.2 PCR negative controls 6.4.3 PCR positive controls 6.4.4 Tagging system controls 6.4.5 Internal controls 6.5 PCR optimization 6.6 How to limit the risk of contamination? 6.7 Blocking oligonucleotides for reducing the amplification of undesirable sequences 6.8 How many PCR replicates? 6.9 Multiplexing several metabarcodes within the same PCR 6.10 Multiplexing many samples on the same sequencing lane 6.10.1 Overview of the problem 6.10.2 Strategy 1: single-step PCR with Illumina adapters 6.10.3 Strategy 2: two-step PCR with Illumina adapters 6.10.4 Strategy 3: single-step PCR with tagged primers 7 DNA sequencing 7.1 Overview of the first, second, and third generations of sequencing technologies 7.2 The Illumina technology 7.2.1 Library preparation 7.2.2 Flow cell, bridge PCR, and clusters 7.2.3 Sequencing by synthesis 7.2.4 Quality scores of the sequence reads 8 DNA metabarcoding data analysis 8.1 Basic sequence handling and curation 8.1.1 Sequencing quality 8.1.1.1 The pros and cons of read quality-based filtering 8.1.1.2 Quality trimming software 8.1.2 Paired-end read pairing 8.1.3 Sequence demultiplexing 8.1.4 Sequence dereplication 8.1.5 Rough sequence curation 8.2 Sequence classification 8.2.1 Taxonomic classification 8.2.2 Unsupervised classification 8.2.3 Chimera identification 8.3 Taking advantages of experimental controls 8.3.1 Filtering out potential contaminants 8.3.2 Removing dysfunctional PCRs 8.4 General considerations on ecological analyses 8.4.1 Sampling effort and representativeness 8.4.1.1 Evaluating representativeness of the sequencing per PCR 8.4.1.2 Evaluating representativeness at the sampling unit or site level 8.4.2 Handling samples with varying sequencing depth 8.4.3 Going further and adapting the ecological models to metabarcoding 9 Single-species detection 9.1 Principle of the quantitative PCR (qPCR) 9.1.1 Recording amplicon accumulation in real time via fluorescence measurement 9.1.2 The typical amplification curve 9.1.3 Quantification of target sequences with the Ct method 9.2 Design and testing of qPCR barcodes targeting a single species 9.2.1 1he problem of specificity 9.2.2 qPCR primers and probe 9.2.3 Candidate qPCR barcodes 9.3 Additional experimental considerations 9.3.1 General issues associated with sampling, extraction, and PCR amplification 9.3.2 The particular concerns of contamination and inhibition 10 Environmental DNA for functional diversity 10.1 Functional diversity from DNA metabarcoding 10.1.1 Functional inferences 10.1.2 Targeting active populations 10.2 Metagenomics and metatranscriptomics: sequencing more than a barcode 10.2.1 General sampling constraints 10.2.1.1 Optimization of the number of samples 10.2.1.2 Enrichment in target organisms 10.2.1.3 Enrichment in functional information 10.2.2 General molecular constraints 10.2.3 From sequences to functions 10.2.3.1 Assembling (or not) a metagenome 10.2.3.2 Sorting contigs or reads in broad categories 10.2.3.3 Extracting functional information via taxonomic inferences 10.2.3.4 Functional annotation of metagenomes 11 Some early landmark studies 11.1 Emergence of the concept of eDNA and first results on microorganisms 11.2 Examining metagenomes to explore the functional information carried by eDNA 11.3 Extension to macroorganisms 12 Freshwater ecosystems 12.1 Production, persistence, transport, and delectability of eDNA in freshwater ecosystems 12.1.1 Production 12.1.2 Persistence 12.1.3 Transport/ diffusion distance 12.1.4 Detectability 12.2 Macroinvertebrates 12.3 Diatoms and microeukaryotes 12.4 Aquatic plants 12.5 Fish, amphibians, and other vertebrates 12.5.1 Species detection 12.5.2 Biomass estimates 12.6 Are rivers conveyer belts of biodiversity information? 13 Marine environments 13.1 Environmental DNA cycle and transport in marine ecosystems 13.2 Marine microbial diversity 13.3 Environmental DNA for marine macroorganisms 14 Terrestrial ecosystems 14.1 Delectability, persistence, and mobility of eDNA in soil 14.2 Plant community characterization 14.3 Earthworm community characterization 14.4 Bacterial community or metagenome characterization 14.5 Multitaxa diversity surveys 1 5 Paleoenvironments 15.1 Lake sediments 15.1.1 Pollen, macrofossils, and DNA metabarcoding 15.1.2 Plants and mammals from Lake Anteme 15.1.3 Viability in the ice-free corridor in North America 15.2 Permafrost 15.2.1 Overview of the emergence of permafrost as a source of eDNA 15.2.2 Large-scale analysis of permafrost samples for reconstructing past plant communities 15.3 Archaeological midden material 15.3.1 Bulk archaeological fish bones from Madagascar 15.3.2 Midden from Greenland to assess past human diet 16 Host-associated microbiota 16.1 DNA dynamics 16.2 Early molecular-based works 16.3 Post-holobiont works 17 Diet analysis 17.1 Some seminal diet studies 17.1.1 Proof of concept-analyzing herbivore diet using next-generation sequencing 17.1.2 Assessing the efficiency of conservation actions in Bialowieza forest 17.1.3 Characterizing carnivore diet, or how to disentangle predator and prey eDNA 17.1.4 Analyzing an omnivorous diet, or integrating several diets in a single one 17.2 Methodological and experimental specificities of eDNA diet analyses 17.2.1 eDNAsources 17.2.1.1 Feces 17.2.1.2 Gut content 17.2.1.3 Whole body 17.2.2 Quantitative aspects 17.2.2.1 Relationship between the amount of ingested food and DNA quantity in the sample 17.2.2.2 Quantifying DNA with PCR and next-generation sequencing 17.2.2.3 Empirical correction of abundances 17.2.3 Diet as a sample of the existing biodiversity 17.2.4 Problematic diets 18 Analysis of bulk samples 18.1 What is a bulk sample? 18.2 Case studies 18.2.1 Bulk insect samples for biodiversity monitoring 18.2.2 Nematode diversity in tropical rainforest 18.2.3 Marine metawan diversity in benthic ecosystems 18.3 Metabarcoding markers for bulk samples 18.4 Alternative strategies 19 The future of eDNA metabarcoding 19.1 PCR-based approaches 19.1.1 Singl
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  • 3
    ISSN: 1420-9055
    Keywords: Nutrient limitation ; primary production ; ocean, mediterranean ; micronanoplankton ; ultraplankton
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Enrichment experiments were carried out on seawater samples from the Israeli coast to characterise the nature of nutrient limitation. Phytoplankton chlorophyll, ATP, PC, PN, PP and bicarbonate and orthophosphate uptake rates indicate that phosphorus limitation is more extreme than that of nitrogen. A large increase in total nitrogen observed with P enrichment suggests that a substantial nitrogen fixation is mediated by picocyanobacteria in this kind of oligotrophic mediterranean waters.
    Type of Medium: Electronic Resource
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  • 4
  • 5
    Electronic Resource
    Electronic Resource
    College Park, Md. : American Institute of Physics (AIP)
    The Journal of Chemical Physics 89 (1988), S. 1358-1363 
    ISSN: 1089-7690
    Source: AIP Digital Archive
    Topics: Physics , Chemistry and Pharmacology
    Notes: This is a study of the deexcitation mechanisms of the metastable 5 2D3/2 state of Ba+ in about 1 atm He buffer gas in the temperature range of 500–650 °C. The ions were produced by three-photon ionization with light tuned to a resonance between two excited states of Ba, enabling the electron density to be varied independently of the temperature and pressure. The deexcitation is dominated by superelastic scattering of electrons with a cross section of σse =45±20 A(ring)2 (corresponding to an electron-impact excitation cross section of 11 A(ring)2) and quenching by Ba atoms with a cross section of σBa =130±25 A(ring)2. No dependence of the deexcitation rate on He density was detected, and we infer an upper limit on the cross section of σHe ≤9×10−22 cm2.
    Type of Medium: Electronic Resource
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  • 6
    Electronic Resource
    Electronic Resource
    College Park, Md. : American Institute of Physics (AIP)
    The Journal of Chemical Physics 87 (1987), S. 660-663 
    ISSN: 1089-7690
    Source: AIP Digital Archive
    Topics: Physics , Chemistry and Pharmacology
    Notes: The diffusion coefficient of Ba (6s5d 3DJ) in noble gases was measured with a modulation/lock-in technique. This technique relies on a cylindrically symmetric source for the metastable state, and is independent of cell geometry. It is readily generalizable to other systems where the creation rate of a long-lived state can be modulated.
    Type of Medium: Electronic Resource
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  • 7
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Publishing Ltd
    FEMS microbiology letters 48 (1987), S. 0 
    ISSN: 1574-6968
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology
    Notes: Abstract The two key enzymes of denitrification, the nitrate and nitrate reductases, were studied in a marine organism, Pseudomonas nautica, strain 617. Both enzymes were grown under anaerobic conditions with either nitrate or nitrous oxide as electron acceptor. The effect of sodium on these enzymes was studied. Only sodium activated the membranous and purified nitrate reductase, and none of the salts affected nitrite reductase.
    Type of Medium: Electronic Resource
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  • 8
    Electronic Resource
    Electronic Resource
    Woodbury, NY : American Institute of Physics (AIP)
    Applied Physics Letters 54 (1989), S. 2296-2298 
    ISSN: 1077-3118
    Source: AIP Digital Archive
    Topics: Physics
    Notes: We report a new technique for producing focused beams of neutrals, ions, and clusters using two-stage laser ablation. We have produced a collimated beam and beams which were focused in one and two dimensions. The on-axis density is 5×1015 atoms/cm3 for a barium beam focused in two dimensions over a distance of 10.7 cm. For a collimated beam the density is 1015 atoms/cm3 at the same distance.
    Type of Medium: Electronic Resource
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  • 9
    Electronic Resource
    Electronic Resource
    s.l. : American Chemical Society
    The @journal of organic chemistry 52 (1987), S. 382-385 
    ISSN: 1520-6904
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology
    Type of Medium: Electronic Resource
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  • 10
    ISSN: 1434-601X
    Keywords: 24.50+ ; 24.75+ ; 25.60.C ; 25.70.B ; 25.85.J ; 21.60E
    Source: Springer Online Journal Archives 1860-2000
    Topics: Physics
    Notes: Abstract The excitation function of the fission probability P E E x) for238U has been measured in the reaction238U(α, α′ f) at 480 MeV bombarding energy. The reaction mechanism of this reaction is discussed for excitation energies belowB nf , the threshold for second chance fission, and aboveB nf up toE x =37 MeV. In comparing with results from fission induced by photons and by particle transfer reactions the (α, α′f) reaction gives too low values for the fission probabilityP f at excitation energies well aboveB nE . The role of the quasi-elastic knock-out process in this reaction is discussed.
    Type of Medium: Electronic Resource
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