Comparison of phosphorus and nitrogen in sediments, the water column, corals and algae at Davies Reef, Great Barrier Reef
Water, sediment, algae and coral samples were collected between July 1980 and March 1981, over a wide range of sites at Davies Reef in the central Great Barrier Reef for phosphorus and nitrogen analyses.Water column samples were collected in 4 liter Niskin bottles. Subsamples for phosphorus (as soluble reactive P), nitrate, nitrite and ammonium analyses were filtered through a 20 µm plankton net into 100 ml acid-washed polythene bottles and stored at -20°C until analysis using a Technicon AutoAnalyzer II system. Samples for arsenic analysis were collected in bottles containing As-free HCl and stored at 3°C until analysis using a Varian model AA6 atomic absorption spectrophotometer.Sediment samples from the deeper waters outside the reef were collected with a van Veen grab. Inside the reef, surface sediment samples, to a maximum depth of 10 cm, were collected in labelled plastic bags by SCUBA divers. Deep cores, to 5 m, were taken from the large lagoon in a polyvinyl chloride casing tipped with a stainless steel corer and driven hydraulically. Samples of young, calcified Halimeda tips as well as young growing coral tips were collected from various locations and either immediately bleached or frozen in dry ice for transport to the laboratory.Sediment, coral and Halimeda samples were dried and ground to pass through a 50 µm sieve. Duplicate 0.5 g subsamples were analyzed for total phosphorus, after digestion, using a standard colorimetric method. For arsenic determination, 0.5 g of sediment was dissolved in 10 ml of Merck 318 HCl, heated at 80°C for 5 minutes and diluted to 50 ml. 5 ml aliquots were then analyzed as described for water analyses.Redox potential of the sediments at a large number of sites was measured in situ using a Pt/SCE combination electrode connected to a millivoltmeter sealed in a waterproof housing. Samples of sediment water were collected using aquarium stones, buried beneath the sediment surface and connected via Tygon tubing to 50-ml polythene syringes. Water samples were also obtained by extracting freshly collected small sediment cores, which were collected by inserting 50 ml syringes, with one end removed, into the sediment and manipulating the plunger to draw sediment into the tube. The syringes were excavated and sealed before final removal from the sediment. Extraction with 10 ml of seawater was carried out within 1 hour. The sediment and seawater mixture was shaken for 1 minute, centrifuged, and the cleared water decanted and stored frozen until analysis. All sediment water samples were analyzed for inorganic nitrogen and phosphorus by the methods described for water analyses.Algal samples were collected from the reef front and crest. The types of algae collected were: calcifying algae (Halimeda sp. dominant), other macroalgae, blue-green algal mats and turf algae. The samples were sorted at the reef and frozen in sealed containers until analysis. Duplicate 3 mg subsamples of finely ground algal material were analyzed for total C and N in a Perkin-Elmer model 240 elemental analyzer.
This research was undertaken to determine whether any significant differences in the phosphorus and nitrogen content of water or sediments could be detected over a range of varying conditions such as water depth, water residence times, types and abundances of benthic organisms, and composition of sediment.
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- 2024-10-17T00:00:00
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- AIMS Web Site
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- Entsch, Barrie, Dr (Principal Investigator)
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- Completed
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- Region 1
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- 1980-07-01
- Time position
- 1981-03-31
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Phosphorus and nitrogen in coral reef sediments: Entsch B, Boto KG, Sim RG and Wellington JT (1983) Phosphorus and nitrogen in coral reef sediments. Limnology and Oceanography 28: 465-476.
Phosphorus and nitrogen in coral reef sediments: Entsch B, Boto KG, Sim RG and Wellington JT (1983) Phosphorus and nitrogen in coral reef sediments. Limnology and Oceanography 28: 465-476.
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- Statement: Water samples:Phosphorus (as soluble reactive P), nitrate, nitrite, and ammonium were measured with a Technicon AutoAnalyzer II system, following the methods described in:Ryle VD, Muller HR and Gentien P (1981) Automated analysis of nutrients in tropical sea waters. Aust. Inst. Mar. Sci. Tech. Bull. AIMS-OS-81-2.These methods used corrections for effects of refractive index changes in samples (or standards) similar to those described in:Froelich PN and Pilson ME (1978) Systematic absorbance errors with Technicon AutoAnalyzer II calorimeters. Water Res. 12: 599-603.Arsenic was measured with a Varian model AA6 atomic absorption spectrophotometer with a model 65 vapor generator accessory and an arsenic electrodeless discharge lamp. The method was based on the reduction of any arsenate to arsenite with KI/HCl, followed by reduction of total arsenite to arsine gas using NaBH4 as described in:Arbab-Zavar MH and Howard AG (1980) Automated procedure for the determination of soluble arsenic using hydride generation atomic-absorption spectroscopy. Analyst 105: 744-750.Hinners TA (1980) Arsenic speciation: Limitations with direct hydride analysis. Analyst 105: 751-755. Multiple replicates (usually 5), including standard additions, were run on each sample. The detection limit (based on 3 x SD of the blank signal) was 4 nM of As in seawater.Sediment, Halimeda and coral samples:The most successful bleaching agent for Halimeda and coral samples was a saturated solution of calcium hypochlorite in Davies Reef water at room temperature. After several hours bleaching, the samples were thoroughly washed with distilled water and dried. The calcium hypochlorite contained about 12 µg P/g. Calculations, based on the usual amounts used per weight of sample bleached, showed that contamination from this procedure would be insignificant.Total phosphorus was analysed using a strong oxidizing acid digestion method and a standard calorimetric phosphate determination of the digest solution as described in:Allen SE, Grimshaw HM, Parkinson JA and Quarmby C (1974) Chemical analysis of ecological materials. Wiley.To minimize any effect of the high calcium matrix on the calorimetric determination, standards were prepared by adding standard KH2PO4 solutions to 0.5 g of Merck AR CaCO3. A mixture of 0.1 g of NBS orchard leaves (0.20 ± 0.01% P) and 0.5 g of CaCO3 was used as a reference standard. Blanks contained 0.5 g of CaCO3 only. All standards and blanks were digested and analyzed like the samples. A further modification of the standard method involved a final digestion stage of 4 h at 220°C to remove completely all traces of nitric acid, which was found to seriously affect the color development.Arsenic was determined by dissolving 0.5 g of sediment in 10 ml of water and 5 ml of Merck 318 HCl, then heating at 80°C for 5 min. After dilution to 50 ml, 5ml aliquots were analyzed as described for water analyses. NBS coal fly ash was used as a reference standard (145 µg As/g).Redox potential of the sediments was measured using a Pt/SCE combination electrode connected to a millivoltmeter sealed in a waterproof housing. The measurements were corrected to be relative to the standard hydrogen electrode (EH).Algal samples:Algal samples usually contained large amounts of tightly bound calcareous sediment which was mostly removed by suspension of a dried, coarsely ground sample in water, allowing the lower density algal material to float free. The weight of any remaining sand was estimated by separate analyses for calcium and magnesium with the atomic absorption spectrophotometer.A correction for carbonate-C was calculated from the calcium and magnesium determinations. Total P was measured as described for sediments. These values were corrected for the phosphorus in the sand by assuming a uniform value of 300 ppm in the sand, except for the Halimeda samples where the sediment is an integral part of the structure of the organism.
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- 68bfd4ab-fee1-425e-a205-c896ed37d73d
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- English
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- UTF8
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- Date info (Creation)
- 2010-04-21T00:00:00
- Date info (Revision)
- 2017-11-20T00:00:00
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- ISO 19115-3:2018
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