Yüksek Ahsen, Okuş Erdoğan, Yilmaz I Noyan, Aslan-Yilmaz Asli, Taş Seyfettin
Institute of Marine Sciences and Management, Istanbul University, Muskule Sok., No. 1, 34470 Vefa, Istanbul, Turkey.
Mar Pollut Bull. 2006 Oct;52(10):1209-18. doi: 10.1016/j.marpolbul.2006.02.006. Epub 2006 Mar 6.
Long-term biological data supported by physicochemical parameters were evaluated to investigate the biodiversity of the Golden Horn Estuary from the past to the present. Limited observations dating back to 60 years ago indicated the existence of a diverse community in this small estuary. Unfortunately, in parallel with the increase in unplanned settlements and industry around the Golden Horn, pollution stress increased since the 1960s. Preliminary studies in the 1990s indicated survival of only a couple of pollution-resistant species, in the relatively cleaner lower estuary. Following the intensification of rehabilitation studies in 1998 and particularly after the opening of the floating bridge at the mid estuary; a remarkable day-by-day recovery in marine life has begun with the improving water quality. Nutrient concentrations decreased markedly; while water clarity significantly increased. Fecal coliform values decreased 10(3) fold. Phytoplankton composition changed and dense blooms of eukaryotic phytoplankters frequently occurred. Hydrogen sulfide almost completely disappeared even during the warmest periods of the year and dissolved oxygen concentrations increased. All results clearly depicted that the Golden Horn ecosystem shifted to eutrophic conditions from an anoxic environment. SCUBA dives in 2002, documented the level of diversification of life in the Golden Horn. All appropriate substratums were intensely covered by macrobenthic forms until the Halic Bridge and filter feeders dominated the plankton-rich ecosystem. Achieving the diversity of 1940s is not possible since the Black and Marmara seas, influencing water quality of the Golden Horn, are also suffering from anthropogenic impacts and are far less diverse than their rich diversity in 1940s. However, the Golden Horn is a good example that even the most polluted ecosystems can recover when appropriate measures are taken.
为了调查金角湾河口过去到现在的生物多样性,对由物理化学参数支持的长期生物数据进行了评估。可追溯到60年前的有限观测表明,这个小河口存在着多样化的群落。不幸的是,随着金角湾周边无规划定居点和工业的增加,自20世纪60年代以来污染压力不断增大。20世纪90年代的初步研究表明,在相对较清洁的河口下游,仅存少数几种耐污染物种。1998年强化修复研究后,特别是河口中部浮桥开通后,随着水质改善,海洋生物开始出现显著的逐日恢复。营养物浓度显著下降;而水体透明度显著提高。粪大肠菌群值下降了10³倍。浮游植物组成发生变化,真核浮游植物频繁出现密集水华。即使在一年中最温暖的时期,硫化氢也几乎完全消失,溶解氧浓度增加。所有结果清楚地表明,金角湾生态系统从缺氧环境转变为富营养化状态。2002年的水肺潜水记录了金角湾生物多样性的水平。直到哈利奇桥,所有合适的底层都被大型底栖生物密集覆盖,滤食性生物在这个浮游生物丰富的生态系统中占主导地位。由于影响金角湾水质的黑海和马尔马拉海也受到人为影响,且远比20世纪40年代丰富的多样性要少,因此不可能实现20世纪40年代的生物多样性。然而,金角湾是一个很好的例子,说明即使是污染最严重的生态系统,采取适当措施后也能恢复。