GLORIA

GEOMAR Library Ocean Research Information Access

feed icon rss

Your email was sent successfully. Check your inbox.

An error occurred while sending the email. Please try again.

Proceed reservation?

Export
Filter
Document type
Keywords
Language
  • 1
    Type of Medium: Book
    Pages: 130 Bl , graph. Darst., Kt , 30 cm
    Series Statement: Berichte aus dem Institut für Meereskunde an der Christian-Albrechts-Universität Kiel 124
    Language: English
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 2
    Book
    Book
    Kiel : Institut für Meereskunde, Abt. Meereschemie
    Type of Medium: Book
    Pages: 38 Bl , Kt
    Series Statement: Berichte aus dem Institut für Meereskunde an der Christian-Albrechts-Universiät Kiel 66
    Language: German
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 3
    Type of Medium: Book
    Pages: getr. Zaehlg
    Language: Undetermined
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 4
    Type of Medium: Online Resource
    Pages: Online-Ressource (88 Seiten, 3,3 MB) , Diagramme, Karten
    Series Statement: Berichte aus dem Institut für Meereskunde an der Christian-Albrechts-Universität Kiel 238
    Language: English
    Note: Zusammenfassung in deutscher und englischer Sprache
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 5
    Type of Medium: Online Resource
    Pages: Online-Ressource (131 Seiten, 2,5 MB) , Diagramme
    Series Statement: Berichte aus dem Institut für Meereskunde an der Christian-Albrechts-Universität Kiel 124
    Language: English
    Note: Zusammenfassung in deutscher und englischer Sprache
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 6
    Type of Medium: Online Resource
    Pages: Online-Ressource (41 Seiten, 1,4 MB) , Illustration
    Series Statement: Berichte aus dem Institut für Meereskunde an der Christian-Albrechts-Universität Kiel 66
    Language: German
    Note: Zusammenfassung in deutscher und englischer Sprache
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 7
    Type of Medium: Online Resource
    Pages: Online-Ressource (94 Seiten, 7 MB) , Diagramme
    Series Statement: Berichte aus dem Institut für Meereskunde an der Christian-Albrechts-Universität Kiel 141
    Language: English
    Note: Zusammenfassung in deutscher und englischer Sprache
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 8
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Oceanography. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (634 pages)
    Edition: 3rd ed.
    ISBN: 9783527613991
    DDC: 551.4601
    Language: English
    Note: Intro -- Methods of Seawater Analysis -- Contents -- List of contributors -- 1 Sampling -- 1.1 Introduction -- 1.2 Sampling strategy -- 1.3 Sampling techniques -- 1.3.1 Surface water sampling -- 1.3.2 Water samplers for major hydrochemical variables -- 1.3.3 Water samplers for trace constituents -- 1.3.3.1 Trace elements -- 1.3.3.2 Trace organic compounds -- 1.3.4 Specific samplers -- 1.3.5 Collection of marine particles -- 1.3.5.1 Collection of suspended particulate matter (SPM) -- 1.3.5.2 Collection of sinking particulates -- 1.4 Sampling errors -- 1.5 Quality control -- 1.5.1 Precision -- 1.5.2 Accuracy -- 1.5.3 Limit of detection -- References to Chapter 1 -- 2 Filtration and storage -- 2.1 Filtration -- 2.1.1 General remarks -- 2.1.2 Filters -- 2.1.3 Filtration techniques -- 2.1.3.1 Vacuum filtration -- 2.1.3.2 Pressure filtration -- 2.1.3.3 In situ filtration -- 2.1.3.4 Centrifugation -- 2.2 Storage -- 2.2.1 General remarks -- 2.2.2 Storage for the determination of major compounds -- 2.2.3 Storage for the determination of nutrients -- 2.2.3.1 General remarks -- 2.2.3.2 Refrigeration -- 2.2.3.3 Poisoning -- 2.2.4 Storage for the determination of trace elements -- References to Chapter 2 -- 3 Determination of salinity -- 3.1 Introduction -- 3.2 Symbols and abbreviations -- 3.3 Definition of salinity -- 3.3.1 Early concepts -- 3.3.2 The practical salinity scale of 1978 (PSS78) -- 3.4 Measurement of the conductivity ratio -- 3.5 Salinity from bench salinometers -- 3.5.1 Purpose -- 3.5.2 Standard seawater -- 3.5.3 Sampling -- 3.5.4 The Guildline AUTOSAL Model 8400 B -- 3.5.5 The Beckman Model RS1O -- 3.5.6 Data logging -- 3.5.7 Substandards -- 3.6 Salinity from in situ measurements: CTD profilers -- 3.6.1 Principles -- 3.6.2 Operation of CTD-rosette sampler systems -- 3.6.3 Calibration -- 3.6.4 Data processing -- References to Chapter 3. , 4 Determination of oxygen -- 4.1 Introduction -- 4.2 Principle of the determination -- 4.3 Error sources and interferences -- 4.4 Reagents -- 4.5 Instruments -- 4.6 Procedure -- 4.6.1 Standardization of the thiosulphate solution -- 4.6.2 Subsampling and fixation of dissolved oxygen -- 4.6.3 Storage -- 4.6.4 Titration -- 4.6.5 Determination of the reagent blank -- 4.6.6 Calculation of the result -- 4.6.7 Accuracy and precision -- References to Chapter 4 -- 5 Determination of hydrogen sulphide -- 5.1 Introduction -- 5.2 Units -- 5.3 Analytical methods -- 5.3.1 Method by Fonselius -- 5.3.1.1 Reagents -- 5.3.1.2 Special apparatus -- 5.3.1.3 Sampling -- 5.3.1.4 Preservation of samples -- 5.3.1.5 Procedure -- 5.3.1.6 Analysis -- 5.3.1.7 Dilution of samples -- 5.3.1.8 Standardization of the method -- 5.3.1.9 Calibration of the method -- 5.3.2 Method by Cline -- 5.3.2.1 Reagents -- 5.3.2.2 Special apparatus -- 5.3.2.3 Sampling -- 5.3.2.4 Procedure -- 5.3.2.5 Analysis -- 5.3.2.6 Standardization and calibration of the method -- 5.3.3 Titration methods -- 5.3.4 Methods using mercury compounds -- References to Chapter 5 -- 6 Determination of thiosulphate and sulphur -- 6.1 Introduction -- 6.2 Principle of the determination of thiosulphate -- 6.2.1 Apparatus -- 6.2.2 Reagents -- 6.2.3 Sampling and storage -- 6.2.4 Procedure -- 6.2.4.1 Standardization of the thiosulphate solution -- 6.2.4.2 Titration of the sample -- 6.2.5 Calculation of the thiosulphate content of the sample -- 6.2.6 Interferences -- 6.3 Principle of the determination of sulphur -- 6.3.1 Apparatus -- 6.3.2 Reagents -- 6.3.3 Sampling and storage -- 6.3.4 Procedure -- 6.3.5 Calculations -- 6.3.6 Interferences -- 6.4 Other methods -- References to Chapter 6 -- 7 Determination of pH -- 7.1 Introduction -- 7.2 List of symbols -- 7.3 Definition of pH -- 7.4 pH scales in seawater. , 7.5 Measurement of pH -- 7.5.1 Potentiometry -- 7.5.1.1 Theory -- 7.5.1.2 Tris buffers -- 7.5.1.3 Practical considerations -- 7.5.2 Spectrophotometry -- 7.5.2.1 Theory -- 7.5.2.2 Indicator pK values for seawater -- 7.5.2.3 Measurement procedures -- 7.5.3 Comparison of the various techniques -- 7.5.4 Correction of pH to in situ conditions -- 7.5.4.1 Empirical equations for correction to in situ temperature -- 7.5.4.2 Empirical equations for correction to in situ pressure -- References to Chapter 7 -- 8 Determination of total alkalinity and total dissolved inorganic carbon -- 8.1 Introduction -- 8.2 List of symbols -- 8.3 Sampling and reference materials -- 8.3.1 Sampling -- 8.3.2 Standard reference materials -- 8.4 Total alkalinity -- 8.4.1 Definition -- 8.4.2 Potentiometric titrations -- 8.4.2.1 Instrumentation -- 8.4.2.2 Analytical procedure -- 8.4.2.3 Evaluation procedures -- 8.4.3 Back titration method -- 8.4.3.1 Reagents -- 8.4.3.2 Analytical procedure -- 8.4.3.3 Calculation of results -- 8.4.3.4 Precision and accuracy -- 8.5 Total dissolved inorganic carbon -- 8.5.1 Potentiometric titrations -- 8.5.2 Coulometric determination technique -- 8.5.2.1 Instrumentation -- 8.5.2.2 Analytical procedure -- 8.5.2.3 Calculation and expression of results -- 8.6 Thermodynamic calculations of the C02 system in seawater -- 8.6.1 Equations describing the C02 system in seawater -- 8.6.2 Selection of stability constants -- 8.6.3 Calculations with two measured C02 parameters -- 8.6.3.1 Calculations with pH and AT measured -- 8.6.3.2 Calculations with pH and f(C02) measured -- 8.6.3.3 Calculations with pH and CT measured -- 8.6.3.4 Calculations with AT and CT measured -- 8.6.3.5 Calculations with AT and f(C02) measured -- 8.6.3.6 Calculations with CT and f(C02) measured -- 8.6.4 Errors arising from the calculations -- References to Chapter 8 -- Appendix 8A. , 9 Determination of carbon dioxide partial pressure (p(CO2)) -- 9.1 Introduction -- 9.2 Principle of the measurement -- 9.3 Apparatus for continuous mode of operation -- 9.3.1 The equilibrator -- 9.3.2 The analytical system -- 9.4 Reagents -- 9.4.1 Calibration gases -- 9.4.2 Gas purification reagents -- 9.5 Calculation of results -- 9.6 Accuracy -- References to Chapter 9 -- 10 Determination of nutrients -- 10.1 Introduction -- 10.1.1 Oceanic distributions of nutrients -- 10.1.2 Chemistry of nutrients in the marine environment -- 10.2 Analytical methods -- 10.2.1 Pretreatment of samples -- 10.2.2 The matrix -- 10.2.3 References and standard materials -- 10.2.4 Calibration, blank determination and calculation procedures -- 10.2.5 Determination of dissolved inorganic phosphate -- 10.2.5.1 Principle of the method -- 10.2.5.2 Range and precision -- 10.2.5.3 Interferences -- 10.2.5.4 Reagents -- 10.2.5.5 Analytical procedures -- 10.2.6 Determination of dissolved inorganic phosphate in the presence of arsenic -- 10.2.6.1 Principle of the method -- 10.2.6.2 Reagents -- 10.2.6.3 Analytical procedures -- 10.2.7 Determination of dissolved inorganic phosphate by an extraction procedure (high-sensitivity method) -- 10.2.7.1 Principle of the method -- 10.2.7.2 Range and precision -- 10.2.7.3 Interferences -- 10.2.7.4 Reagents -- 10.2.7.5 Analytical procedure -- 10.2.8 Determination of nitrite -- 10.2.8.1 Principle of the method -- 10.2.8.2 Range and precision -- 10.2.8.3 Interferences -- 10.2.8.4 Reagents -- 10.2.8.5 Analytical procedures -- 10.2.9 Determination of nitrate -- 10.2.9.1 Principle of the method -- 10.2.9.2 Range and precision -- 10.2.9.3 Interferences -- 10.2.9.4 Reagents -- 10.2.9.5 Preparation of the reductor -- 10.2.9.6 Analytical procedures -- 10.2.10 Determination of ammonia -- 10.2.10.1 Principle of the method -- 10.2.10.2 Range and precision. , 10.2.10.3 Interferences -- 10.2.10.4 Reagents -- 10.2.10.5 Analytical procedures -- 10.2.1 1 Determination of dissolved inorganic silicate -- 10.2.11.1 Principle of the method -- 10.2.11.2 Range and precision -- 10.2.11.3 Interferences -- 10.2.11.4 Reagents -- 10.2.11.5 Analytical procedures -- 10.2.12 Determination of nitrogen, phosphorus and silicon in particulate and dissolved organic matter -- 10.2.12.1 Equipment -- 10.2.12.2 Calibration and calculation of total and organic nutrients -- 10.2.13 Determination of total and organic phosphorus by acid persulphate oxidation -- 10.2.13.1 Reagents -- 10.2.13.2 Analytical procedure -- 10.2.14 Determination of total and organic phosphorus by alkaline persulphate oxidation -- 10.2.14.1 Reagents -- 10.2.14.2 Analytical procedure -- 10.2.14.3 Dilution factors (see Section 10.2.12.2) -- 10.2.15 Determination of polyphosphates -- 10.2.15.1 Analytical procedure -- 10.2.16 Determination of total and organic nitrogen after persulphate oxidation -- 10.2.16.1 Range and precision of the method -- 10.2.16.2 Reagents -- 10.2.16.3 Analytical procedure -- 10.2.17 Simultaneous oxidation of nitrogen and phosphorus compounds with persulphate -- 10.2.17.1 Range and precision of the method -- 10.2.17.2 Oxidizing reagent -- 10.2.17.3 Analytical procedure -- 10.2.18 Determination of total silicon -- 10.2.18.1 Principle of the method -- 10.2.18.2 Reagents -- 10.2.18.3 Analytical procedure -- 10.2.19 Determination of total silicon by carbonate fusion -- 10.2.19.1 Reagents -- 10.2.19.2 Analytical procedure -- 10.3 Automated nutrient analysis -- 10.3.1 Principle of automated analysis -- 10.3.2 The sampler -- 10.3.3 The proportioning pump -- 10.3.4 The analytical manifold -- 10.3.4.1 Standard manifold components -- 10.3.4.2 Heating and cooling -- 10.3.4.3 Special devices -- 10.3.4.4 The flow-through spectrophotometer. , 10.3.5 Data acquisition.
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 9
    Electronic Resource
    Electronic Resource
    Springer
    European food research and technology 163 (1977), S. 87-91 
    ISSN: 1438-2385
    Source: Springer Online Journal Archives 1860-2000
    Topics: Process Engineering, Biotechnology, Nutrition Technology
    Description / Table of Contents: Summary Some important environmental poisons, e.g. the element cadmium, are rather volatile during flameless AAS determination. This causes difficulties the in case of matrices consisting of large amounts of salts and organic materials. Therefore, as an example in the case of cadmium, a detailed method has been developed. The following method is now used for determinations in large series of samples. Its main advantages are: the sample size must not exceed the mg to μg range; the digestion takes place in small polypropylene tubes and in the graphite tube itself; to obtain high accuracy, a special device for the flamless AAS is used. An intercalibration exercise will be described elsewhere.
    Notes: Zusammenfassung Einige wichtige Umweltgifte, wie z. B. das Cadmium, sind bei der Bestimmung mit Hilfe der flammenlosen AAS relativ leichtflüchtig. Dies führt z. B. bei biologischem Material und Seewasser zur Schwierigkeiten, wenn die aus Salzen und organischem Material bestehende Matrix in großem Überschuß vorhanden ist. Die Entwicklung einer Bestimmungsmethode setzt daher ins einzelne gehende Untersuchungen voraus. Dies ist am Beispiel des Cadmiums geschehen. Die im folgenden beschriebene Methode wird jetzt routinemäßig für größere Probenserien eingesetzt. Ihre Haupteigenschaften sind: Zur Durchführung genügen wenige Milligramm bzw. Mikrogramm Probenmaterial; der Säureaufschluß geschieht in kleinen Polypropylenampullen und im Graphitrohr. Zur Verbesserung der Reproduzierbarkeit der AAS-Meßwerte wird eine spezielle Ausrüstung zur flammenlosen Atomisierung eingesetzt. — Über eine Intercalibrierung soll extra berichtet werden.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 10
    Electronic Resource
    Electronic Resource
    Springer
    Ocean dynamics 40 (1987), S. 103-114 
    ISSN: 1616-7228
    Source: Springer Online Journal Archives 1860-2000
    Topics: Geosciences , Physics
    Description / Table of Contents: Zusammenfassung Im Juli 1984 sind auf einer Expedition in die zentrale Nordsee insgesamt 48 Wasserproben (von 8 Stationen) genommen worden. Dabei ergaben sich in der horizontalen Verteilung zwischen den Wässern mit relativ niedrigem Salzgehalt (S≈34) und den Proben aus der nördlichen zentralen Nordsee (S〉35,0) die größten Unterschiede schiede für Co und Mn (mit Konzentrationsverhältnissen von ≥10), während die Werte für Cd, Cu und Ni sich mit steigendem Salzgehalz um mehr als die Hälfte erniedrigten. Bis auf Cd folgen alle Metallwerte einer Verdünnungskurve, die mitP〈0,001 hochsignifikant ist, was — zumindest für die Elemente Co, Cu, Ni und Mn — auf die Flüsse als Haupteintragsquellen hindeutet. Vertikale Konzentrationsgradienten konnten unter den Meßbedingungen dieser Reise — trotz der starken Schichtung — nicht nachgewiesen werden, was sehr wahrscheinlich auf die relativ hohen “background”-Konzentrationen, die geringen Wassertiefen in der Nordsee sowie auf die relativ kurzen Aufenthaltszeiten der Tiefenwässer zurückgeführt werden muß. Zur Abschätzung von saisonalen Einflüssen auf die Verteilung gelöster Spurenelemente sollte deshalb eine Winteraufnahme durchgeführt werden.
    Abstract: Résumé 48 échantillons d'eau (par 8 stations) étant pris pendant une cruise dans la Mer du Nord centrale en juillet 1984, ont été analysés pour les métaux de trace Cd, Co, Cu, Mn et Ni. Les gradients horizontaux entre les eaux avec des salinités basses (S≈34) et l'eau centrale (S〉35,0) étaient plus grands pour Co et Mn (avec relations ≥10); les valeurs étaient plus faibles pour Cd, Cu et Ni (≥2). Cd étant une exception, les concentrations étaient ratachées linéairement avec salinité (significant au niveauP〈0,001), indiquant que les fleuves sont les sources dominantes pour Co, Cu, Ni et Mn en solution. Des gradients importants à travers de la thermocline n'ont pas été trouvés avec les procédures appliquées, la raison étant probablement les niveaux “background” plus forts, les profondeurs basses et l'échange vertical de l'eau rapide. Une cruise en hiver est nécessaire pour établir les variations saisonales de la distribution des métaux dissolus dans la région complète.
    Notes: Summary In July 1984, a total of 48 water samples (from 8 stations) were collected on a cruise across the central North Sea. Horizontal gradients for dissolved metals between the low salinity water masses (S≈34) and the northern central North Sea stations (S〉35.0) were highest for Co and Mn (with factors of ≥10), whereas the Cd, Cu and Ni gradients varied by factors of ≥2. With the exception of Cd, the data fall along the salinity mixing line (significant at theP〈0.001 level) indicating that the dissolved Co, Cu, Ni and Mn distributions throughout the water column can be largely explained on the basis of fresh water inputs. An important result of the cruise is that significant concentration gradients across the thermocline were not observed with the procedures applied here, probably due the relatively high “background” levels, the shallow depths and relatively rapid turn-over of the water column. A winter season cruise is required to assess the seasonal variations throughout the area on the distribution of dissolved metal concentrations.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
Close ⊗
This website uses cookies and the analysis tool Matomo. More information can be found here...