The impact objective is sustainable production of seaweed for a range of commercial applications. Mostly on sheltered shores and can be found up to a depth of 30m. 3.12. This is a good validation of our sustainable harvesting methods and the efforts we have gone to., Peter adds, What we do in Caithness is highly sustainable and we see ourselves as stewards of these harvesting sites. The seas provide a portion of our diet and just like all natural ecosystems on the land, they provide an array of ecosystem services that are essential to life on Earth. 3.8. Indicator species can mark a change in the condition of an ecosystem. An exercise to establish a greater understanding of activity across Scotland by mapping what, where and how much wild harvesting is happening or planned, by whom and how activity is being regulated; A review of the current regulatory framework for harvesting and cultivation and proposed enhancements to ensure the framework is fit for purpose. Peter also says that, NatureScot (formally known as Scottish Natural Heritage) reviewed our harvesting methods and when we do our initial site assessments, we research the protection for wildlife, like birds, around that site and this assessment, along with other criteria, is used to choose our harvesting sites., SHOREs products have also achieved Soil Associations organic certification which commends the sustainability of their operations and their sensitivity to their environmental impact. These 14 species were chosen because they're good indicator species - a species whose presence, absence or abundance reflects a specific environmental factor. The bushy top half of the frond is pulled off, leaving the base and holdfast behind. There are a plethora of edible seaweed varieties, from the rather mysterious-sounding native species spiral wrack, Irish moss and gutweed to the Japanese staples of kombu and nori. With a slight increase in exposure A. nodosum is replaced by a greater abundance of Fucus vesiculosus. The extent and impact of each pressure from a given activity will vary according to its intensity or frequency. Figure 4: Generalised littoral and sublittoral zonation of wracks and kelps on a sheltered shore (adapted from Hiscock (1979)).
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