M. T. Namin, T. Valinassab, E. R. Fard, F. Ehteshami
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Also bentho-pelagics, the medium demersals, benthos, and crustaceans had a very negative impact on themselves due to cannibalism. Furthermore, the highest realized trophic level was 4.34 for sharks. The maximum omnivory index is calculated as 0.99 for medium demersals for feeding on a wide variety of preys. Also, the average catch per net primary production, i.e., the gross efficiency of the system was around 0.000198 (lower than the global average) indicating that the fishery is harvesting fishes high in the food chain. The primary production/respiration (PP/R) ratio is found to be 3.57 and the values of ascendancy (45.40%) and overhead (54.60%) showed stability of the ecosystem. Thus northern Oman Sea can be classified as an immature ecosystem (in the developmental stage), although it has some kind of system maturity. Accordingly, the food web of northern Oman Sea is consisted mostly of detritivorous, planktivorous, and carnivorous fish species. 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引用次数: 3
摘要
在本研究中,通过使用质量平衡建模软件Ecopath with Ecosim(EwE)开发了阿曼海北部一些鱼类的营养结构模型。在该模型中,我们模拟了2017年至2018年分布在3998.20平方公里区域的16个功能群。本研究区域的平均营养水平为3.49。系统杂食性指数和连通性指数的计算值分别为0.42和0.44。然而,对于除鲨鱼和鳐鱼外的大多数高营养水平消费者来说,模型中的生态营养效率值都很高(>0.5),因为它们的捕鱼死亡率很高。因此,混合营养影响表明,浮游植物和碎屑对几乎所有生态群都产生了积极影响。此外,底栖动物、中型底栖动物、底栖动物和甲壳类动物也因自相残杀而对自身产生了非常负面的影响。此外,鲨鱼的最高营养水平为4.34。以各种各样的猎物为食的中等减分,最大杂食指数计算为0.99。此外,初级生产净产量的平均渔获量,即系统的总效率约为0.000198(低于全球平均水平),表明渔业正在捕捞食物链中较高的鱼类。初级生产/呼吸(PP/R)比为3.57,优势值(45.40%)和头顶值(54.60%)显示了生态系统的稳定性。因此,阿曼海北部可以被归类为一个不成熟的生态系统(处于发育阶段),尽管它具有某种系统成熟度。因此,阿曼海北部的食物网主要由碎屑性、浮游性和肉食性鱼类组成。此外,使用Ecosim(EwE)软件的Ecopath可以很好地研究生态群体之间的相互作用,以及阿曼海北部捕鱼的影响,这无疑有助于制定具体的管理策略。以生态系统为基础的适当渔业管理做法可以提高这一过度开发生态系统的效率。
Research Article: Trophic dynamics analysis and ecosystem structure for some fish species of northern Oman Sea
In the present study, a trophic structure model for some fish species of the northern Oman Sea is developed through using mass balance modeling software, Ecopath with Ecosim (EwE). In this model, we simulated 16 functional groups spread across an area of 3998.20 km2 from 2017 to 2018. Mean trophic level in the area of the present study was 3.49. Values calculated for system omnivory and connectance indices were 0.42 and 0.44, respectively. However, the values of ecotrophic efficiency in the model were high (>0.5) for most consumers of high trophic levels except for sharks and rays because of their high fishing mortality. Accordingly, mixed trophic impact showed that phytoplankton and detritus positively impacted almost all ecological groups. Also bentho-pelagics, the medium demersals, benthos, and crustaceans had a very negative impact on themselves due to cannibalism. Furthermore, the highest realized trophic level was 4.34 for sharks. The maximum omnivory index is calculated as 0.99 for medium demersals for feeding on a wide variety of preys. Also, the average catch per net primary production, i.e., the gross efficiency of the system was around 0.000198 (lower than the global average) indicating that the fishery is harvesting fishes high in the food chain. The primary production/respiration (PP/R) ratio is found to be 3.57 and the values of ascendancy (45.40%) and overhead (54.60%) showed stability of the ecosystem. Thus northern Oman Sea can be classified as an immature ecosystem (in the developmental stage), although it has some kind of system maturity. Accordingly, the food web of northern Oman Sea is consisted mostly of detritivorous, planktivorous, and carnivorous fish species. Besides, Ecopath with Ecosim (EwE) software can be an excellent option to examine interactions among ecological groups, and the impact of fishing in northern Oman Sea which is unquestionably helpful to develop concrete management strategies. The proper ecosystem-based fisheries management practice can improve the efficiency of this overexploited ecosystem.
期刊介绍:
1- Living various species (contains animals and vegetal species) in various aquatic ecosystems.
2- Health and diseases of aquatic species.
3- Determining the stocks and specific time and location for catching and reliable exploitation for sustainable development.
4- Methods of propagation and culture of high value aquatic resources.
5- Aquatic stock assessment and the methods of restocking the high value species and suggestion for rate, areas and the time for releasing fish and other aquatic organisms fries.
6- Pollutant agents and their effects to the environments of aquatic species.
7- Feed and feeding in aquatic organisms.
8- Fish processing and producing new products.
9- The economic and social aspects of fisheries.