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讨论了网箱养殖、工厂化养殖和野生褐牙鲆的外观差异,对比分析了不同生长环境下褐牙鲆的肌肉营养成分和营养学价值。结果显示:网箱养殖的褐牙鲆体形、体色更接近野生褐牙鲆,即有眼侧呈深褐色,无眼侧呈白色;工厂化养殖褐牙鲆有眼侧体色较暗,无眼侧有黑斑。网箱养殖褐牙鲆脂肪含量(2.5%)远低于工厂化养殖的褐牙鲆(4.2%),而接近于野生的褐牙鲆(1.4%);网箱养殖褐牙鲆水分含量比工厂化养殖的高,也更接近野生的褐牙鲆。3种生长环境的褐牙鲆,氨基酸组成是一致的,而且各项比值也都符合FAO/WHO的标准。对比分析必需氨基酸指数(EAAI)和EPA+DPA、SFA、MUFA、PUFA等指标,网箱养殖褐牙鲆均要高于工厂化养殖褐牙鲆,接近而又优于野生的褐牙鲆。在矿物质含量方面,3种生长环境下的褐牙鲆差异不明显。综合各项指标分析,在褐牙鲆的3种生长环境中,网箱养殖的褐牙鲆要优于工厂化养殖的褐牙鲆,而更接近于野生的褐牙鲆。 相似文献
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福建沿海牙鲆池塘养殖试验 总被引:3,自引:0,他引:3
牙鲆 (ParalichthysolivaceusT.&S.)属鲽形目 ,鲆科 ,牙鲆属。南方俗称左口鱼、皇帝鱼、比目鱼 ,其肉质鲜美 ,营养丰富 ,为大型名贵海产鱼类 ,经济价值很高 ,是我国主要养殖品种之一。近几年牙鲆养殖在福建方兴未艾 ,但还存在许多问题 ,如夏季水温过高难以度夏 ,而利用地下水进行工厂化养殖投资大、成本高 ,经济效益不理想。因此 ,作者于1998年利用深水沙质底池塘进行牙鲆养殖试验 ,成功解决度夏问题 ,取得了满意结果。1材料与方法1.1池塘条件选择福建省莆田县南日岛垦区内池塘一个 ,面积6.7ha ,南北… 相似文献
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褐牙鲆(Paralichthys
olivaceus)受精卵及仔稚鱼生理生态学研究进展 总被引:2,自引:0,他引:2
作者综述近年来国内外在褐牙鲆受精卵及仔稚鱼的发育、行为及理化环境对其生理生态的影响等方面的研究进展。着重介绍在人工养殖环境中,水温、盐度、水质、光照等环境因素的变化对褐牙鲆卵的孵化及仔稚鱼的发育和行为所产生的影响,以及褐牙鲆仔稚鱼不同发育阶段对各种理化环境的耐受范围和阈值。探讨人工种苗和天然种苗在形态发育及行为等方面的差异,对今后褐牙鲆的集约化健康养殖提出了几点建议。 相似文献
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报道了墨西哥湾扇贝在广东省南澳试养的过程和结果,试验证明该贝能够在汕头市进行人工养殖,成活率达92.9%,每公顷产量23368.5kg。 相似文献
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Soil-sized particulates have been collected on board ship by a mesh technique from the lower troposphere of the North, Equatorial and South Atlantic Ocean, northern and southern Indian Ocean, South and East China Sea and various coastal localities.Spectrographic analysis reveals that, on average, the particulates have concentrations of Mn, Ni, Co, Ga, Cr, V, Ba, and Sr which are of the same order of magnitude as those in average crustal material. In contrast, the average concentrations of Pb, Sn, and Zn are one order of magnitude higher than those in average crustal material.Within this “world-wide” average there are significant geographical variations in the distributions of Pb, Sn, and Zn which may be related to anthropogenic sources.On the basis of trace-element distributions lower tropospheric soil-sized marine particulates have been divided into four genetic components; local, zonal, inter-zonal, and global. The proportions of these components vary geographically, and each component may have both a natural and an anthropogenic fraction. 相似文献
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Tautog, Tautoga onitis, is an abundant species of fish in estuaries of the northeastern United States. Planktonic tautog larvae are abundant in summer in these estuaries, but there is little information on rates of growth of tautog larvae feeding on natural assemblages of food in the plankton. We examined abundance and growth of larval tautog and environmental factors during weekly sampling at three sites along a nearshore‐to‐offshore transect in Buzzards Bay, Massachusetts, USA during summer 1994. This is the first study of a robust sample size (336 larvae) to estimate growth rates of field‐caught planktonic tautog larvae feeding on natural diets, using the otolith daily‐growth‐increment method. The study was over the entire summer period when tautog larvae were in the plankton. The sampling sites contrasted in several environmental variables including temperature, dissolved oxygen (DO), and chlorophyll a concentration. There was a temporal progression in the abundance of tautog larvae over the summer, in relation to location and temperature. Tautog larvae were first present nearshore, with a pronounced peak in abundance occurring at the nearshore sites during the last 2 weeks in June. Larvae were absent at this time further offshore. From late June through August, larval abundance progressively decreased nearshore, but increased offshore although never approaching the abundance levels observed at the nearshore sites. The distribution and abundance of tautog larvae appeared to be related to a nearshore‐to‐offshore seasonal warming trend and a nearshore decrease in DO. Otoliths from 336 larvae ranging from 2.3 to 7.7 mm standard length had otolith increment counts ranging from 0 to 19 increments. Growth of larval tautog was estimated at 0.23 mm·day?1, and length of larvae prior to first increment formation was estimated at 2.8 mm indicating that first increment formation occurs 3–4 days after hatching at 2.2 mm. Despite spatial and temporal differences in environmental factors, there were no significant differences in growth rates at any of three given sites over time, or between sites. Because larval presence only occurred at a narrow range of temperature (17–23.5 °C) and DO (6.5–9.3 mg·l?1), in situ differences in growth did not appear to be because of differences in larval distribution and abundance patterns relative to these parameters. 相似文献
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Lars-Göran Danielsson 《Marine Chemistry》1980,8(3):199-215
Results of trace-metal analyses of water samples obtained during a cruise with the Soviet R.V. “Akademik Kurchatov” in the Indian Ocean are presented. The determinations were performed on board with atomic absorption spectrophotometry after a two-stage dithiocarbamate—Freon extraction procedure. Trace-metal concentrations found are in the same range as those found recently for similar open-ocean areas by other workers. The values for lead and zinc are probably high due to contamination. Vertical profiles indicate biogenic processes as controlling factors for the increase of cadmium, copper and nickel concentrations with depth. Iron shows an irregular depth distribution as a result of large random variations in concentration. 相似文献
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Klaus Kremling 《Marine Chemistry》1983,13(2):87-108
In June 1981, dissolved Zn, Cd, Cu, Ni, Co, Fe, and Mn were determined from two detailed profiles in anoxic Baltic waters (with extra data for Fe and Mn from August 1979). Dramatic changes across the O2H2S interface occur in the abundances of Cu, Co, Fe, and Mn (by factors of ?100). The concentrations of Zn, Cd, and Ni at the redox front decrease by factors between 3 to 5.Equilibrium calculations are presented for varying concentrations of hydrogen sulfide and compared with the field data. The study strongly supports the assumption that the solubility of Zn, Cd, Cu, and Ni is greatly enhanced and controlled by the formation of bisulfide and(or) polysulfide complexes. Differences between predicted and measured concentrations of these elements are mainly evident at lower ΣH2S concentrations.Cobalt proved to be very mobile in anoxic regions, and the results indicate that the concentrations are limited by CoS precipitation. The iron (Fe2+) and manganese (Mn2+) distribution in sulfide-containing waters is controlled by total flux from sediment-water interfaces rather than by equilibrium concentrations of their solid phases (FeS and MnCO3). The concentrations of these metals are therefore expected to increase with prolonged stagnation periods in the basin. 相似文献
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P.N. Froelich L.W. Kaul J.T. Byrd M.O. Andreae K.K. Roe 《Estuarine, Coastal and Shelf Science》1985,20(3):239-264
Concentrations of dissolved nutrients (NO3, PO4, Si), germanium species, arsenic species, tin, barium, dimethylsulfide and related parameters were measured along the salinity gradient in Charlotte Harbor. Phosphate enrichment from the phosphate industry on the Peace River promotes a productive diatom bloom near the river mouth where NO3 and Si are completely consumed. Inorganic germanium is completely depleted in this bloom by uptake into biogenic opal. The ratio taken up by diatoms is about 0·7 × 10?6, the same as that provided by the river flux, confirming that siliceous organisms incorporate germanium as an accidental trace replacement for silica. Monomethylgermanium and dimethylgermanium concentrations are undetectable in the Peace River, and increase linearly with increasing salinity to the seawater end of the bay, suggesting that these organogermanium species behave conservatively in estuaries, and are neither produced nor consumed during estuarine biogenic opal formation or dissolution. Inorganic arsenic displays slight removal in the bloom. Monomethylarsenic is produced both in the bloom and in mid-estuary, while dimethylarsenic is conservative in the bloom but produced in mid-estuary. The total production of methylarsenicals within the bay approximately balances the removal of inorganic arsenic, suggesting that most biological arsenic uptake in the estuary is biomethylated and released to the water column. Dimethylsulfide increases with increasing salinity in the estuary and shows evidence of removal, probably both by degassing and by microbial consumption. An input of DMS is observed in the central estuary. The behavior of total dissolvable tin shows no biological activity in the bloom or in mid-estuary, but does display a low-salinity input signal that parallels dissolved organic material, perhaps suggesting an association between tin and DOM. Barium displays dramatic input behavior at mid-salinities, probably due to slow release from clays deposited in the harbor after catastrophic phosphate slime spills into the Peace River. 相似文献