Butman Bradford, Aretxabaleta Alfredo L, Dickhudt Patrick J, Dalyander P Soupy, Sherwood Christopher R, Anderson Donald M, Keafer Bruce A, Signell Richard P
U.S. Geological Survey, 384 Woods Hole Road, Woods Hole, MA 02543, USA.
Integrated Statistics and U.S. Geological Survey, Woods Hole, MA 02543, USA.
Deep Sea Res 2 Top Stud Oceanogr. 2014 May 1;103:79-95. doi: 10.1016/j.dsr2.2013.10.011.
Cysts of , a dinoflagellate that causes toxic algal blooms in the Gulf of Maine, spend the winter as dormant cells in the upper layer of bottom sediment or the bottom nepheloid layer and germinate in spring to initiate new blooms. Erosion measurements were made on sediment cores collected at seven stations in the Gulf of Maine in the autumn of 2011 to explore if resuspension (by waves and currents) could change the distribution of over-wintering cysts from patterns observed in the previous autumn; or if resuspension could contribute cysts to the water column during spring when cysts are viable. The mass of sediment eroded from the core surface at 0.4 Pa ranged from 0.05 kg m near Grand Manan Island, to 0.35 kg m in northern Wilkinson Basin. The depth of sediment eroded ranged from about 0.05 mm at a station with sandy sediment at 70 m water depth on the western Maine shelf, to about 1.2 mm in clayey-silt sediment at 250 m water depth in northern Wilkinson Basin. The sediment erodibility measurements were used in a sediment-transport model forced with modeled waves and currents for the period October 1, 2010 to May 31, 2011 to predict resuspension and bed erosion. The simulated spatial distribution and variation of bottom shear stress was controlled by the strength of the semi-diurnal tidal currents, which decrease from east to west along the Maine coast, and oscillatory wave-induced currents, which are strongest in shallow water. Simulations showed occasional sediment resuspension along the central and western Maine coast associated with storms, steady resuspension on the eastern Maine shelf and in the Bay of Fundy associated with tidal currents, no resuspension in northern Wilkinson Basin, and very small resuspension in western Jordan Basin. The sediment response in the model depended primarily on the profile of sediment erodibility, strength and time history of bottom stress, consolidation time scale, and the current in the water column. Based on analysis of wave data from offshore buoys from 1996 to 2012, the number of wave events inducing a bottom shear stress large enough to resuspend sediment at 80 m ranged from 0 to 2 in spring (April and May) and 0 to 10 in winter (October through March). Wave-induced resuspension is unlikely in water greater than about 100 m deep. The observations and model results suggest that a millimeter or so of sediment and associated cysts may be mobilized in both winter and spring, and that the frequency of resuspension will vary interannually. Depending on cyst concentration in the sediment and the vertical distribution in the water column, these events could result in a concentration in the water column of at least 10 cysts m. In some years, resuspension events could episodically introduce cysts into the water column in spring, where germination is likely to be facilitated at the time of bloom formation. An assessment of the quantitative effects of cyst resuspension on bloom dynamics in any particular year requires more detailed investigation.
,一种在缅因湾引发有毒藻华的甲藻,其孢囊以休眠细胞的形式在底部沉积物上层或底部 nepheloid 层过冬,并在春季萌发以引发新的藻华。2011 年秋季,在缅因湾的七个站点采集了沉积物岩芯并进行侵蚀测量,以探究再悬浮(由波浪和水流引起)是否会改变前一年秋季观察到的越冬孢囊分布模式;或者再悬浮是否会在春季孢囊具有活力时将孢囊带入水柱。在 0.4 帕压力下从岩芯表面侵蚀的沉积物质量范围从大马南岛附近的 0.05 千克/平方米到威尔金森盆地北部的 0.35 千克/平方米。侵蚀的沉积物深度范围从缅因州西部陆架水深 70 米处含沙沉积物站点的约 0.05 毫米到威尔金森盆地北部水深 250 米处黏土质粉砂沉积物的约 1.2 毫米。沉积物侵蚀性测量数据被用于一个沉积物输运模型,该模型由 2010 年 10 月 1 日至 2011 年 5 月 31 日期间的模拟波浪和水流驱动,以预测再悬浮和底床侵蚀。底部剪应力的模拟空间分布和变化受半日潮流强度控制,该潮流沿缅因州海岸从东向西减弱,以及振荡波诱导流控制,后者在浅水区最强。模拟显示缅因州中部和西部海岸偶尔会因风暴出现沉积物再悬浮,缅因州东部陆架和芬迪湾因潮流出现稳定的再悬浮,威尔金森盆地北部没有再悬浮,约旦盆地西部再悬浮非常小。模型中的沉积物响应主要取决于沉积物侵蚀性剖面、底部应力的强度和时间历程、固结时间尺度以及水柱中的水流。基于对 1996 年至 2012 年近海浮标波浪数据的分析,春季(4 月和 5 月)诱导底部剪应力大到足以使 80 米深处沉积物再悬浮的波浪事件数量为 0 至 2 次,冬季(10 月至 3 月)为 0 至 10 次。在深度大于约 100 米的水中,波浪诱导的再悬浮不太可能发生。观测和模型结果表明,在冬季和春季可能会有大约一毫米左右的沉积物及相关孢囊被动员起来,并且再悬浮频率会年际变化。根据沉积物中孢囊浓度和水柱中的垂直分布,这些事件可能导致水柱中孢囊浓度至少达到 10 个/立方米。在某些年份,再悬浮事件可能会在春季偶尔将孢囊引入水柱,而此时在藻华形成时孢囊很可能更容易萌发。对任何特定年份孢囊再悬浮对藻华动态的定量影响进行评估需要更详细的调查。