当社グループは 3,000 以上の世界的なカンファレンスシリーズ 米国、ヨーロッパ、世界中で毎年イベントが開催されます。 1,000 のより科学的な学会からの支援を受けたアジア および 700 以上の オープン アクセスを発行ジャーナルには 50,000 人以上の著名人が掲載されており、科学者が編集委員として名高い
。オープンアクセスジャーナルはより多くの読者と引用を獲得
700 ジャーナル と 15,000,000 人の読者 各ジャーナルは 25,000 人以上の読者を獲得
Robyn Hannigan
Coral bleaching occurs while corals degrade or expel their dinoflagellate symbionts in reaction to environmental stressors inclusive of expanded sea floor temperature and elevated UV radiation[1]. Although corals can reacquire symbionts and recover in weeks to months, recovered corals may also grow slower and feature decreased fecundity in comparison to formerly unbleached corals, giving bleaching-resistant corals an ecological benefit after bleaching events. In extreme cases, bleaching may also arise on the scale of hundreds to thousands of kilometres and radically modify coral cover and composition with coral mortality from bleaching events approaching 100% in extreme cases. Branching corals inclusive of acroporid and pocilloporid corals are often more susceptible to bleaching and mortality than are massive corals, allowing the slowerdeveloping huge corals to be extra chronic on reefs after bouts of robust bleaching [2]. Bleaching occasions now no longer only lower live coral cover however additionally offer large areas for seaweed colonization, and these seaweeds can prevent corals from re-establishing if herbivores aren’t present in enough numbers to suppress seaweed colonization and growth. Additionally, large-scale bleaching and mortality of branching corals can suppress fish populations that are dependent on live coral for shelter and food.