991 resultados para Prawn Penaeus-japonicus


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本文研究了365nm波长紫外线辐射中国对虾精子对其顶体反应和受精能力的影响。结果表明,低剂量紫外线辐射促进精子发生顶体反应,大剂量辐射使精子丧失发生顶体反应的生理机能并死亡。人工诱导雌核发育的过程中,紫外线辐射精液稀释液5-8秒,可获得遗传物质失活的精子(激活源)。经透射电镜观察分析,紫外线对精子遗传物质的损伤是一种使染色质变性的化学作用。

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在过去的几十年间,利用线粒体基因组序列探讨后生动物深层次的系统发育关系已取得初步进展。这主要得益于,线粒体基因组与其它分子标记相比具备诸多优势。迄今为止,超过1,200个后生动物的线粒体基因组已被测定,然而所获得的数据分布极不均衡。 软甲纲历来是甲壳动物分类学和系统发育学研究的重要类群,在形态学特征和分子生物学各方面取得广泛的发展。尽管软甲纲本身作为单系群已得到大多数甲壳动物学家认可,但是软甲纲内部各个类群之间的系统发育关系迄今仍颇有争议。本文报道了凡纳滨对虾Litopenaeus vannamei、中国明对虾Fenneropenaeus chinensis、脊尾白虾Exopalaemon carinicauda、太平洋磷虾Euphausia pacifica和采自南极普里兹湾南极磷虾Euphausia superba的线粒体基因组,其长度分别为15,989 bp、16,004 bp、15,730 bp、16,898 bp和15,498 bp以上(部分非编码区没有测定)。 本研究发现凡纳滨对虾、中国明对虾、脊尾白虾和太平洋磷虾的线粒体基因组包含后生动物线粒体基因组典型的基因组成(13个蛋白质编码基因、22个转运RNA、2个核糖体RNA和一个非编码的AT富含区);然而,南极磷虾与后生动物线粒体基因组典型的基因组成相比,存在1个trnN基因的重复。与泛甲壳动物线粒体基因组的原始排列相比,凡纳滨对虾和中国明对虾线粒体基因组的基因排列完全一致;脊尾白虾的线粒体基因组发生罕见的trnP和trnH易位,从而说明在真虾下目中线粒体基因组的基因排列并不保守;太平洋磷虾线粒体基因组的基因排列出现3个转运RNA的重排 (trnL1、trnL2和trnW);南极磷虾线粒体基因组的基因排列除了出现太平洋磷虾具有的这3个转运RNA重排之外,还有1个trnN的重复和1个trnI基因的重排。另外,在太平洋磷虾线粒体基因组最大的非编码区中存在一个154 bp×4.7的串连重复区域,如此大片段的串联重复区域(>150 bp)在软甲纲动物线粒体基因组中是首次报道。 目前所获得的线粒体基因组数据强有力地支持口足目、对虾科、真虾下目和短尾下目为单系群。通过比较基因排列及蛋白质编码基因核苷酸和氨基酸序列的系统发育分析得知真虾类和龙虾类为腹胚亚目的原始类群,并支持“((Penaeus+Fenneropenaeus)+Litopenaeus)+Marsupenaeus”的系统发育关系。此外,线粒体基因组的数据也强有力地支持磷虾目为单系群。但对于磷虾目在软甲纲中的分类地位及与其它类群的系统发育关系存在一些分歧:基于蛋白质编码基因核苷酸和氨基酸数据的贝叶斯分析强有力地支持磷虾目和十足目近缘,这个结果和传统的分类系统完全一致;然而,基于核苷酸序列的邻接法、氨基酸序列的邻接法和最大似然法均强有力地支持磷虾类和对虾类亲缘关系较近,从而破坏了十足目的单系性,与传统的认识并不一致,但由于自展值的支持率非常高,所以深层次的分析需要进一步加强。 星虫动物属于海洋生物中的一个小门类,自1555年被记载以来,其在后生动物中的分类地位就备受争议。本研究测定了星虫动物门的第一条线粒体基因组:革囊星虫Phascolosoma esculenta的线粒体基因组,全长为15,494 bp,包含13个蛋白质编码基因、22个转运RNA、2个核糖体RNA和1个非编码的AT富含区,所有37个基因在同一条链上编码。与后生动物线粒体基因组的典型组成相比,存在一个trnR基因的缺失和一个trnM基因的重复。比较星虫动物和其它后生动物的线粒体基因组,可以得到以下结论:1)星虫动物和环节动物(包括螠虫动物)的线粒体基因组有相近的基因排列,而且所有基因都在同一链上编码;2)基于蛋白质编码基因的系统发育分析强有力地支持星虫动物和环节动物(包括螠虫动物)组成一个单系群,而将软体动物排除在外。因此,本研究认为以前许多星虫动物和软体动物“共享”的特征,包括发育特征和缺乏分节等,需要重新考虑。

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该文首先对中国对虾血细胞体外短时培养条件进行了摸索,以期为后来在体外研究中国对虾血细胞吞噬活动中ROS的产生建立基础.在上在实验的基础上,该文利用化学发光法对中国对虾血细胞体外吞噬过程中ROS的产生进行了研究,试图了解血细胞吞噬活动中的化学发光现象.最后利用NBT还原法研究了中国对虾血细胞体外吞噬过程中O<'-><,2>的产生化及一些环境污染物如重金属离子和农药对其吞噬活动中O<'-><,2>的产生影响.

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在浅海养殖系统中,生源要素的形态和动态对滤食性贝类生长有着重要影响,与此同时,滤食性贝类对系统中的生源要素的动态也具有重要作用,国外学者对此研究的比较多,但在我国研究甚少。在本论文中利用室内模拟实验和海上调查的方法,研究滤食性贝类的生物过滤、生物沉积及排泄作用对浅海养殖系统中生源要素动态的影响。室内模拟实验部分:1998年4月至6月间,在烟台利用室内规格相同的水池,建立了栉孔贝扇(Chlamys farreri)不同养殖密度单养、栉孔扇贝和海带(Laminaria japonica)混养、栉孔扇贝和海带、刺参(Apostichopus japonicus)多元化养殖等三种养殖模式,九个养殖系统和一个对照系统,实验中各池的温度、光照、盐度和换水量基本一致,定期测定实验池中颗粒有机碳(POC)、颗粒氮(PN)和水体及沉积物中营养盐的含量。实验结果表明:1 栉孔扇贝大量滤食水体中的颗粒物质,导致水体中颗粒物质浓度的降低,水体中POC和PN的现存量与栉孔扇贝的放养密度负相关,水体中颗粒物的缺乏会限制栉孔扇贝的生长,当POC、PN的现存量分别降低到0.09mg/L、0.015mg/L时,就会限制栉孔扇贝的生长。2 栉孔扇贝排泄代谢产物增加了水体中无机营养盐的浓度,栉孔扇贝排泄的氮以NH_4~+-N为主,占三氮的93.5%;海带可为栉孔扇贝生长提供一部分饵料。3 实验期间硅浓度低于或近于2umol/L,限制了硅藻的生长,实验后期水体中氮盐浓度降低,氮磷比小于10,可能限制了浮游植物的生长,减少了栉孔扇贝的饵料生物,从而抑制了栉孔扇贝的生长。4 在栉孔扇贝单养和贝藻参混养系列中,沉积物中有机物、有机碳、有机氮、有机磷及总磷的含量随栉孔扇贝放养密度的增大而减少。5 在贝藻混养系列中的栉孔扇贝生长好于单养系列,在贝藻参混养系列中的海带生长速度快于贝藻混养系列;单养和贝藻参混养模式中栉栉孔扇贝的日产量均以放养密度中等的(20个/m~2)养殖系统较高。海上调查部分:于1997年冬季、1998年春季和夏季,在烟台四十里湾海区进行了三次野外调查,分别在养殖海区和非养殖海区取得沉积物柱状样,测定沉积物中有机质和间隙水中无机营养盐的含量。实验结果表明:6 养殖区沉积物中有机质的含量大于非养殖区,平均高约22%。7 养殖海区沉积物间隙水中营养盐的浓度大于非养殖海区,其中养殖区NH_4~+-N、PO_4~(3-)-P 的浓度分别高于非养殖区50%和200%-400%,NO_3~--N, NO_2~--N 的浓度差别不明显;沉积物间隙水中营养盐浓度冬季较小,而春夏季浓度较高;氮盐以NH_4~+-N 为主,占90%以上。8 养殖海区沉积物-海水界面间营养盐扩散通量大于非养殖海区,烟台四十里湾沉积物-海水界面间NH_4~+-N, PO_4~(3-)-P, NO_3~--N, NO_2~--N 冬、春、夏三季平均扩散通分别为249.99 umol/m~2/d、3.78 umol/m~2/d、5.24 umol/m~2/d、0.83mol/m~2/d。

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Matrix-bound phosphine was determined in the Jiaozhou Bay coastal sediment, in prawn-pond bottom soil, in the eutrophic lake Wulonglan, in the sewage sludge and in paddy soil as well. Results showed that matrix-bound phosphine levels in freshwater and coastal sediment, as well as in sewage sludge, are significantly higher than that in paddy soil. The correlation between matrix bound phosphine concentrations and organic phosphorus contents in sediment samples is discussed.

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Stomach contents were examined of 4527 adult individuals of 12 flatfish species collected during the 1982 - 1983 Bohai Sea Fisheries Resources Investigation. Their food habits, diet diversity, similarity of prey taxa, trophic niche breadth and diet overlap were systematically analysed. Ninety-seven prey species belonging to the Coelenterata, Nemertinea, Polychaeta, Mollusca, Crustacea, Echinodermata, Hemichordata and fish were found and five of them were considered to be principal prey for flatfishes: Alpheus japonicus, Oratosquilla oratoria, Alpheus distinguendus, Loligo japonicus and Crangon affinis. Among the flatfishes, Paralichthys olivaceus was piscivorous, whereas Pseodopleuronectes yokohamae and Pseudopleuronectes herzensteini both had polychaetes and molluscs as their main prey groups. Pleuronichthys cornutus was classified as a polychaete-mollusc eater, with a strong preference for crustaceans. Verasper variegatus, Cynoglossus semilaevis, Eopsetta grigorjewi and Cleisthenes herzensteini ate crustaceans. Kareius bicoloratus was classified as a mollusc-crustacean eater: Cynoglossus abbreviatus, Cynoglossus joyneri and Zebrias zebra were grouped as crustacean-fish eaters. However, Z. zebra also took polychaetes and C. abbreviatus and C. joyneri preyed on some molluscs. Trophic relationships among the flatfishes were complicated, but they occupied distinctive microhabitats in different seasons and selected their specific prey items, which was favourable to the stability of the flatfish community in the Bohai Sea.

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Objective To study the transfer of paralytic shellfish toxins (PST) using four simulated marine food chains: dinoflagellate Alexandrium tamarense -> Arterriia Artemia salina -> Mysid shrimp Neomysis awatschensis; A. tamarense-N. awatschensis: A. taniarense A. salina -> Perch Lateolabrax japonicus; and A. tamarense -> L. japonicus. Methods The ingestion of A. tamarense, a producer of PST, by L. japonicus, N. awatschensis, and A. salina was first confirmed by microscopic observation of A. tamarense cells in the intestine samples of the three different organisms, and by the analysis of Chl.a levels iii the samples. Toxin accumulation in L. japonicus and N. awatschensis directly from the feeding on A. tamarense or indirectly ibrough the vector of A. salina was then studied. The toxicity of samples was measured using the AOAC mouse bioassay method, and the toxin content and profile of A. tamarense were analyzed by the HPLC method. Results Both A. salina and N. awatschensis could ingest A. tamarense cells. However, the ingestion capability of A. salina exceeded that of N. awatschensis. After the exposure to the culture of A. tamarense (2 000 cells(.)mL(-1)) for 70 minutes, the content of ChLa in A. salina and N. awatschensis reached 0.87 and 0.024 mu g-mg(-1), respectively. Besides, A. tamarense cells existed in the intestines of L. japonicus, N. awatschensis and A. salina by microscopic observation. Therefore, the three organisms could ingest A. tamarense cells directly. A. salina could accumulate high content of PST, and the toxicity of A. salina in samples collected on days 1, 4, and 5 of the experiment was 2.18, 2.6, and 2.1 MU(.)g(-1), respectively. All extracts from the samples could lead to death of tested mice within 7 minutes, and the toxin content in arternia sample collected on the 1st day was estimated to be 1.65x10(-5) pg STX equa Vindividual. Toxin accumulation in L. japonicus and N. awatschensis directly from the feeding on A. tamarense or indirectly froin the vector of A. salina was also studied. The mice injected with extracts from L. japonicus and N. awatschensis samples that accumulated PST either directly or indirectly showed PST intoxication symptoms, indicating that low levels of PST existed in these samples. Conclusion Paralytic shellfish toxins can be transferred to L. japonicus, N. awatschensis, and A. salina from A. taniarense directly or indirectly via the food chains.

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The residues of enrofloxacin and its metabolite in Nile tilapia (Oreochromis niloticus) were studied after oral dose of 50 mg/kg for 7 days. To find the differences between Nile tilapia and Chinese shrimp (Penaeus chinensis), the residues of enrofloxacin in P chinensis were also studied under the same conditions. The results showed that enrofloxacin metabolized into ciprofloxacin in both Nile tilapia and P chinensis, the maximal concentration of enrofloxacin in muscle, liver and plasma of Nile tilapia were 3.61 mu g/g, 5.96 mu g/g, 1.25 mu g/ml respectively, and ciprofloxacin in muscle was 0.22 mu g/g. The maximal concentration of enrofloxacin and ciprofloxacin in P chinensis were 1.68 mu g/g and 0.07 mu g/g respectively. The predicted withdrawal time for Nile tilapia was 22 days, and P. chinensis was 12 days under our experiment conditions. The residues of fitrazolidone [3-(5-nitrofurfurylidenamino)-2-oxazolidinone] and its main metabolite 3-amina-2-oxazolidinone (AOZ) in Nile tilapia were first determined by HPLC/MS. Results showed that after oral dose of 30 mg/kg for 7 days, the maximum concentration of farazolidone in Nile tilapia was 413 mu g/kg after 6 h, whereas AOZ residue reached its maximum (31 mu g/kg) right after stopping treatment. In contrast to the high metabolic rate of furazolidone, AOZ was very difficult to eliminate in vivo, thus the withdrawal time of furazolidone in Nile tilapia was 22 days at least. (c) 2005 Elsevier B.V. All rights reserved.

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通过对贵州花江峡谷喀斯特石漠化区4种典型石漠化植物群落中11种常见植物种叶片的δ^13C值测定,研究了各植物种对影响植物碳同位素分馏的主要环境因子(土壤储水量、大气相对湿度、光照强度、土壤厚度)的响应,分析了石漠化梯度中不同土层土壤储水量、大气相对湿度、土壤有机质、年均气温、光照强度等环境因子梯度变化与植物叶片δ^13C值的关系。结果表明,大部分物种的δ^13C值对环境因子的变化趋势表现为随环境水分好转呈下降趋势,即水分利用效率下降;也有部分物种呈稳定不变或逆势上升趋势。相关性分析表明,清香木(Pistacia weinmannifolia)、石岩枫(Mallotus repandus)、红背山麻杆(Alchornea trewioides)的主导因子是土层储水量;肾蕨(Nephrolepis cordifolia)、野桐(Mallotus japonicus var。floccosus)的主导因子是土壤厚度;肾蕨、八角枫(Alangium chinense)、构树(Broussonetia papyrifera)的主导因子是光照强度;而广西密花树(Rapanea kwangsiensis)、圆叶乌桕(Sapium rot undifolium)和灰毛浆果楝(Cipadessa cinerascens)则分辨不出主导因子,即环境影响因素更为综合。总体而言,叶片高δ^13C值是对低水分、高光、低资源环境的适应.

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W niniejszym artykule autor przedstawił sposób odtworzenia normy prawnej zawierającej prawo do ochrony zdrowia na podstawie przepisu prawnego art. 68 ust. 1 Konstytucji RP. Przełożenie przepisu prawnego na normę prawną odbyło się zgodnie z założeniami derywacyjnej koncepcji wykładni, której istotą jest uzyskanie równoznaczności pomiędzy przepisem a odtworzoną z niego normą. W tym celu konieczne było przeprowadzenie wszystkich trzech faz wykładni: porządkującej, rekonstrukcyjnej i percepcyjnej. Niniejszy artykuł ukazuje, jak przebiegają poszczególne czynności interpretacyjne podejmowane w oparciu o dyrektywy derywacyjnej koncepcji wykładni. Pozwala to zobaczyć w szczegółowy sposób przebieg procesu przekształcania przepisu prawnego w normę prawną. Rezultatem przeprowadzonej wykładni było uzyskanie dostatecznie jednoznacznej normy prawnej. Na tej podstawie wykazano, że prawo do ochrony zdrowia jest zasadą prawa, ponieważ możliwe było odniesienie treści normy prawnej do określonych kryteriów. Ponadto, norma prawna odtworzona na podstawie przepisu konstytucyjnego zawiera wszystkie elementy, przede wszystkim określa adresata i nakazane zachowanie. Pozwala to wskazać sytuacje prawne, jakie wyznacza odtworzona w toku wykładni norma prawna, czyli obowiązek, uprawnienie i prawo podmiotowe. Postrzeganie konstytucyjnego prawa do ochrony zdrowia jako normy prawnej umożliwia także znacznie szersze i głębsze rozpatrzenie aspektów jego obowiązywania. W tym kontekście szczególnie przydatna jest derywacyjna koncepcja wykładni prawa.

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Wydział Prawa i Administracji

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Human activities within the marine environment give rise to a number of pressures on seabed habitats. Improved understanding of the sensitivity of subtidal sedimentary habitats is required to underpin the management advice provided for Marine Protected Areas, as well as supporting other UK marine monitoring and assessment work. The sensitivity of marine sedimentary habitats to a range of pressures induced by human activities has previously been systematically assessed using approaches based on expert judgement for Defra Project MB0102 (Tillin et al. 2010). This previous work assessed sensitivity at the level of the broadscale habitat and therefore the scores were typically expressed as a range due to underlying variation in the sensitivity of the constituent biotopes. The objective of this project was to reduce the uncertainty around identifying the sensitivity of selected subtidal sedimentary habitats by assessing sensitivity, at a finer scale and incorporating information on the biological assemblage, for 33 Level 5 circalittoral and offshore biotopes taken from the Marine Habitat Classification of Britain and Ireland (Connor et al. 2004). Two Level 6 sub-biotopes were also included in this project as these contain distinctive characterising species that differentiate them from the Level 5 parent biotope. Littoral, infralittoral, reduced and variable salinity sedimentary habitats were excluded from this project as the scope was set for assessment of circalittoral and offshore sedimentary communities. This project consisted of three Phases. • Phase 1 - define ecological groups based on similarities in the sensitivity of characterising species from the Level 5 and two Level 6 biotopes described above. • Phase 2 - produce a literature review of information on the resilience and resistance of characterising species of the ecological groups to pressures associated with activities in the marine environment. • Phase 3 - to produce sensitivity assessment ‘proformas’ based on the findings of Phase 2 for each ecological group. This report outlines results of Phase 2. The Tillin et al., (2010) sensitivity assessment methodology was modified to use the best available scientific evidence that could be collated within the project timescale. An extensive literature review was compiled, for peer reviewed and grey literature, to examine current understanding about the effects of pressures from human activities on circalittoral and offshore sedimentary communities in UK continental shelf waters, together with information on factors that contribute to resilience (recovery) of marine species. This review formed the basis of an assessment of the sensitivity of the 16 ecological groups identified in Phase 1 of the project (Tillin & Tyler-Walters 2014). As a result: • the state of knowledge on the effects of each pressure on circalittoral and offshore benthos was reviewed; • the resistance, resilience and, hence, sensitivity of sixteen ecological groups, representing 96 characteristic species, were assessed for eight separate pressures; • each assessment was accompanied by a detailed review of the relevant evidence; Assessing the sensitivity of subtidal sedimentary habitats to pressures associated with human activities • knowledge gaps and sources of uncertainty were identified for each group; • each assessment was accompanied by an assessment of the quality of the evidence, its applicability to the assessment and the degree of concordance (agreement) between the evidence, to highlight sources of uncertainty as an assessment of the overall confidence in the sensitivity assessment, and finally • limitations in the methodology and the application of sensitivity assessments were outlined. This process demonstrated that the ecological groups identified in Phase 1 (Tillin & Tyler-Walters 2014) were viable groups for sensitivity assessment, and could be used to represent the 33 circalittoral and offshore sediments biotopes identified at the beginning of the project. The results of the sensitivity assessments show: • the majority of species and hence ecological groups in sedimentary habitats are sensitive to physical change, especially loss of habitat and sediment extraction, and change in sediment type; • most sedimentary species are sensitive to physical damage, e.g. abrasion and penetration, although deep burrowing species (e.g. the Dublin Bay prawn - Nephrops norvegicus and the sea cucumber - Neopentadactyla mixta) are able to avoid damaging effects to varying degrees, depending on the depth of penetration and time of year; • changes in hydrography (wave climate, tidal streams and currents) can significantly affect sedimentary communities, depending on whether they are dominated by deposit, infaunal feeders or suspension feeders, and dependant on the nature of the sediment, which is itself modified by hydrography and depth; • sedentary species and ecological groups that dominate the top-layer of the sediment (either shallow burrowing or epifaunal) remain the most sensitive to physical damage; • mobile species (e.g. interstitial and burrowing amphipods, and perhaps cumaceans) are the least sensitive to physical change or damage, and hydrological change as they are already adapted to unstable, mobile substrata; • sensitivity to changes in organic enrichment and hence oxygen levels, is variable between species and ecological groups, depending on the exact habitat preferences of the species in question, although most species have at least a medium sensitivity to acute deoxygenation; • there is considerable evidence on the effects of bottom-contact fishing practices and aggregate dredging on sedimentary communities, although not all evidence is directly applicable to every ecological group; • there is lack of detailed information on the physiological tolerances (e.g. to oxygenation, salinity, and temperature), habitat preferences, life history and population dynamics of many species, so that inferences has been made from related species, families, or even the same phylum; • there was inadequate evidence to assess the effects of non-indigenous species on most ecological groups, and Assessing the sensitivity of subtidal sedimentary habitats to pressures associated with human activities • there was inadequate evidence to assess the effects of electromagnetic fields and litter on any ecological group. The resultant report provides an up-to-date review of current knowledge about the effects of pressures resulting from human activities of circalittoral and offshore sedimentary communities. It provides an evidence base to facilitate and support the provision of management advice for Marine Protected Areas, development of UK marine monitoring and assessment, and conservation advice to offshore marine industries. However, such a review will require at least annual updates to take advantage of new evidence and new research as it becomes available. Also further work is required to test how ecological group assessments are best combined in practice to advise on the sensitivity of a range of sedimentary biotopes, including the 33 that were originally examined.

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Nociception is the ability to perceive a noxious stimulus and react in a re flexive manner and occurs across a wide range of taxa. However, the ability to experience the associated aversive sensation and feeling, known as pain, is not widely accepted to occur in nonvertebrates. We examined the responses of a decapod crustacean, the prawn, Palaemon elegans, to different noxious stimuli applied to one antenna to assess reflex responses (nociception) and longer-term, specifically directed behavioural responses that might indicate pain. We also examined the effects of benzocaine, a local anaesthetic, on these responses. Noxious stimuli elicited an immediate reflex tail flick response, followed by two prolonged activities, grooming of the antenna and rubbing of the antenna against the side of the tank, with both activities directed specifically at the treated antenna. These responses were inhibited by benzocaine; however, benzocaine did not alter general swimming activity and thus the decline in grooming and rubbing is not due to general anaesthesia. Mechanical stimulation by pinching also resulted in prolonged rubbing, but this was not inhibited by benzocaine. These results indicate an awareness of the location of the noxious stimuli, and the prolonged complex responses indicate a central involvement in their organization. The inhibition by a local anaesthetic is similar to observations on vertebrates and is consistent with the idea that these crustaceans can experience pain.

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Dissertação de Mestrado, Aquacultura e Pescas, Faculdade de Ciências do Mar e do Ambiente, Universidade do Algarve, 2008