Scanlan C M, Foden J, Wells E, Best M A
Scottish Environment Protection Agency, Greyhope Road, Aberdeen AB11 9RD, United Kingdom.
Mar Pollut Bull. 2007;55(1-6):162-71. doi: 10.1016/j.marpolbul.2006.09.017. Epub 2006 Oct 30.
Among the various quality elements which the Water Framework Directive requires should be monitored are macroalgae. One aspect of these is the presence, in transitional waters particularly, of large blooms of opportunistic macroalgae, such as Ulva and Enteromorpha. Within the United Kingdom (UK) and Republic of Ireland (RoI) there are currently no set ecological quality objectives or standards for macroalgae. Nor are there standard methods for monitoring macroalgal blooms, although various combinations of aerial photography, remote sensing and measurements on the ground are used. This paper attempts to set a logical framework for the prioritisation of sites for monitoring, the development of a tiered monitoring procedure and the derivation of thresholds for classification. Draft threshold limits for percentage cover and biomass of macroalgae have been derived from the literature. The importance of secondary effects and physico-chemical parameters is discussed.
《水框架指令》要求监测的各类质量要素中包括大型海藻。其中一个方面是,尤其是在过渡水域中,出现大量诸如石莼属和浒苔属等机会性大型海藻的水华现象。在英国和爱尔兰共和国,目前没有针对大型海藻设定的生态质量目标或标准。也没有监测大型海藻水华的标准方法,尽管采用了航空摄影、遥感和实地测量等各种组合方法。本文试图建立一个合理的框架,用于确定监测地点的优先级、制定分层监测程序以及推导分类阈值。大型海藻覆盖百分比和生物量的阈值限制草案已从文献中得出。文中还讨论了次生效应和物理化学参数的重要性。