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  • 1
    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.
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  • 2
    Electronic Resource
    Electronic Resource
    Springer
    Bulletin of mathematical biology 45 (1983), S. 579-590 
    ISSN: 1522-9602
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology , Mathematics
    Notes: Abstract In this paper we are concerned with problems of the long-term behavior for nonlinear systems in random environment. The general model is assumed to be given by an ordinary differential equation with random parameters or random input. The disturbance process can be taken from a fairly general class of Markov processes having a bounded state space. In terms of the system’s dynamics we give sufficient conditions for the existence and uniqueness of invariant probabilities. Finally, we apply these results to the two-dimensional biochemical model which is known as the Brusselator.
    Type of Medium: Electronic Resource
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  • 3
    Electronic Resource
    Electronic Resource
    Springer
    Fresenius' Zeitschrift für analytische Chemie 352 (1995), S. 357-363 
    ISSN: 1618-2650
    Source: Springer Online Journal Archives 1860-2000
    Topics: Chemistry and Pharmacology
    Notes: Abstract Methylcyclohexane dissolved in and forming a thin film on purified seawater with traces of anthraquinone added as triplet sensitizer was exposed to natural sunlight in a quartz flask. The water was circulated through a glass cartridge filled with Amberlite XAD-2 for the concentration of reaction products which were identified by GC/MS after elution and silica gel chromatography. They included isomeric methylcyclohexanols as the principal components, primary hydroperoxides, a tentatively identified secondary peroxide, methylcyclohexanones, and acyclic ketones. Mass spectra and mechanisms are discussed as well as possible biological consequences of the formation of these compounds.
    Type of Medium: Electronic Resource
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  • 4
    Electronic Resource
    Electronic Resource
    Springer
    Fresenius' Zeitschrift für analytische Chemie 339 (1991), S. 772-776 
    ISSN: 1618-2650
    Source: Springer Online Journal Archives 1860-2000
    Topics: Chemistry and Pharmacology
    Notes: Summary Anthraquinone has been found to be a compound occuring frequently in seawater. Excited by solar radiation it acts as one of many natural and man-made photosensitizers and can thus be used as a model substance for the study of sensitized photochemical reactions of environmental chemicals. Experimentally it has been shown to mediate the oxidative photochemical decomposition of aliphatic hydrocarbons which, lacking absorption bands in the solar UV range at sea level, are by themselves photochemically inert. Formaldehyde, smaller amounts of acetaldehyde and acetone as well as a still unidentified carbonyl compound are the principal low molecular weight products generated in the anthraquinone-sensitized photooxidation, with natural as well as artificial sunlight, of straight chain saturated hydrocarbons accommodated in high purity water. Qualitatively the same results were obtained in natural seawater as reaction medium from which particles were removed by glass fiber filtration and organic compounds by adsorption on activated charcoal. The concomittant generation of homologous series of methylketones and terminal alkenes suggest a decomposition mechanism involving cyclic electron rearrangement in a 6-membered transition state. Based on HPLC analysis of their 2,4-dinitrophenylhydrazones, the rates of volatile carbonyl generation in the sensitized photo-oxidation of n-tetradecane was determined in the liquid phase. Also determined was the rate of formaldehyde formation in the gas phase from n-tetradecane and from two Brazilian crude oils. The rates of generation of acetaldehyde and acetone could not be determined in the experiments with crude oils because of irregular changes of concentrations with time. The rate of concentration increase of formaldehyde in the vapour phase over the hydrocarbon surface film was similar to that in the water underneath. The artifical light source was a high pressure xenon lamp whose emission spectrum closely resembles that of natural sunlight at sea level. It was calibrated against the intensity of natural sunlight using pnitroacetophenone/pyridine as binary chemical actinometer.
    Type of Medium: Electronic Resource
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  • 5
    ISSN: 0009-2940
    Keywords: Chemistry ; Inorganic Chemistry
    Source: Wiley InterScience Backfile Collection 1832-2000
    Topics: Chemistry and Pharmacology
    Notes: Die Eigenschaften und Reaktionen des Brom-keto-lactams VI werden beschrieben. Während eine direkte Bromwasserstoff-Abspaltung zum Enol V nicht gelingt, führt die Einwirkung von Lithiumchlorid in Dimethylformamid nach HOLYSZ zu dem chlorhaltigen Enol XX, aus dem durch freiwillige Dehydrierung und Ringaufspaltung das partiell hydrierte 7H-Dibenz[d.f]azonin-Derivat XXX entsteht. Zum Strukturbeweis wird die Verbindung in die PRELOG-Base II umgewandelt.
    Type of Medium: Electronic Resource
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  • 6
    Publication Date: 2022-06-23
    Description: Pelagic tar has been collected daily on a transsect from off Prtugal to south of the Canary Islands in January/February 1975. A new neuston sampler was used which may be towed at speeds between 7 and 10 knots (DERENBACH & EHRHARDT 1975). A total of 22 samples was taken. Dimensions of tar balls ranged from potatoe-size to small specks approximately 1 mm in diameter. Concentrations were found to vary between 20.5 and 0.007 mg/m2, except for one instance of an extremely high tar concentration of 2270 mg/m2. 49 GC analyses were made. 61% showed bimodal peak distributions characteristic of crude oil sludges. The composition of tar balls was independent of their size suggesting diffusion controlled degradation.
    Type: Article , PeerReviewed
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  • 7
    Publication Date: 2022-06-20
    Type: Article , PeerReviewed
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  • 8
    Publication Date: 2018-03-07
    Description: As part of the NOAA/ROPME/MSRC sponsored assessment of the coast of Saudi Arabia, heavily impacted by the large oil spills of the 1991 Gulf War, we measured benthic community respiration (R) and primary production (P) rates in shallow subtidal basins near heavily oiled coastlines. Study sites were located in zones predicted to be basins of maximum deposition of any oiled sediments likely to wash off the adjacent coast and in reference bays predicted to be clean and unaffected. We measured oxygen exchange using in situ benthic respirometers and analysed petroleum hydrocarbon (PHC) levels in the near surface sediments at five stations. We concentrated our efforts in mud habitats to complement related studies in seagrass habitats. Measured community R rates ranged from a low of 700 μM m2 h−1 in coarse sand sediments with total organic carbon content (TOC) of only 0.16% of dry wt to the highest rate of 2184 μm m−2 h−1 in finer mud-sand habitats with 0.39% TOC. All measured rates were in the range of literature values for shallow marine sediments at temperatures of 17 to 19°C. Sediment oil content was 13–540 μg g−1 dry wt by ultraviolet fluorescence (UVF) analysis and 0.5–103 μg g−1 by gas chromatography (GC). Benthic P rates, calculated as light minus dark changes in dissolved oxygen, ranged from a low of 1162 μm m−2 h−1 at the most heavily oiled site to a high of 5216 μm m−2 h−1 at less oiled sites. While a weak inverse relationship between benthic P and sediment oil content was not significant statistically due to the small number of samples, a significant inverse relationship was found between the ratio of production to respiration (P/R) and the total petroleum content of the sediments by UVF. The effect appears to be driven more by differences in production than an effect on respiration which showed little relationship with either oil content or productivity. We conclude that within 1 year after the oil grounded on the intertidal sands of Saudi Arabia, the levels of oil in subtidal benthic sediments had decreased in most habitats to levels that did not show community stress by our oxygen measurements. Rather, long term damage to benthic subtidal habitats was limited only to enclosed bays adjacent to the most heavily oiled coastlines. Preliminary estimates of yearly P converted to carbon units indicates that the shallow mud sediments of the Gulf are at least as productive as most oligotrophic water columns. Since benthic habitats covered by seagrass, algae beds or coral reefs are likely to have even higher production rates, we conclude that benthic processes contribute significantly to the overall carbon flux in the Gulf ecosystem.
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  • 9
    Publication Date: 2018-03-07
    Description: Gas chromatography-mass spectrometry (GC-MS) analyses of organic concentrates from eastern Mediterranean surface water show that dissolved fossil fuel residues are dominated by unsubstituted aromatic hydrocarbons and heterocyclic aromatics and thus resemble products of incomplete combustion. Deviating from this interpretation, preferential photochemical oxidation of alkyl-substituted aromatics is suggested as the principal causative mechanism, although, especially near land-based sources. the influence of combustion-derived unsubstituted aromatics is not defined. Total concentrations of dissolved aromatics as determined by GC-FID (flame ionization detection) and GC-MS from a limited data subset were in reasonable agreement with UV fluorescence measurements of dissolved/dispersed oil residues. The same preponderance of unsubstituted aromatics over their alkyl derivatives was found in extracts of the particulate phase, but concentrations were small relative to alkanes and/or alkenes of recent marine biosynthetic origin. CPI (carbon preference index) values of higher molecular weight n-alkanes indicated varying contributions of plant waxes to the particulate hydrocarbon pool. CPI values of corresponding dissolved n-alkanes were found to be near unity, indicating fossil fuel origin. Despite differences in higher molecular weight n-alkane CPI values and the predominance of recent biosynthetic aliphatics, the similarity of dissolved and particulate aromatic fractions suggests limited adsorption by particles of fossil fuel derived hydrocarbons and heterocyclics.
    Type: Article , PeerReviewed
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  • 10
    Publication Date: 2018-03-07
    Description: Saudi Arabian coastal waters near sandy beaches, severely contaminated with crude oil released in Kuwait during the 1991 Gulf War, as well as underlying sediments and a few bivalves, were analysed to assess concentrations and composition of petrogenic hydrocarbon mixtures and structurally related oxidation products. Concentrations of dissolved oil residues determined by UV spectrofluorometry (UVF) near oil deposits on beaches did not exceed 3.5 μg l−1; concentrations dropped to approximately 1/10th of this value a few miles offshore. Gravimetric concentrations of unfractionated lipophilic material extracted from large volumes of seawater at the same stations were up to 10 times those determined by UVF. After chromatography on silica gel, individual petroleum hydrocarbons in the low polarity fractions and oxidation products in the polar fractions were characterized by their spectra (GC/MS) and quantitated by Selected Ion Monitoring (SIM) GC/MS. Concentrations of oxidation products (ketones, aldehydes, alcohols) of aromatic hydrocarbons exceeded those of their parent compounds by more than an order of magnitude. Significant concentrations were also found of the presumably pyrogenic triplett sensitizer anthraquinone. Contributions to polar fractions of water extracts by biosynthesized lipids were negligible. UVF determinations appear to underestimate concentrations of dissolved oil residues, because many oxidation products have lower fluorescence quantum yields than the respective parent hydrocarbons. Their ecotoxicological properties are unknown. Concentrations measured in sediments by UVF ranged from 13 to 540 μg g−1 dry wt and 0.5 to 103 μg g−1 as measured by gas chromatography with flame ionization detection (FID GC). Bivalves ranged from 0.8 to 1.5 μg mg−1 extractable organic matter (EOM) by UVF, and 0.1 to 0.3 μg mg−1 EOM by GC analysis. PAHs were identified in sediment and bivalve extracts by GC/MS and quantitated by SIM GC/MS. None of the relatively water soluble alkylbenzene photo-oxidation products found in water samples nor any higher molecular weight quinones could be detected in sediment extracts. However, ion chromatograms strongly suggest the presence of numerous high molecular weight aromatics in that matrix.
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