Anthropogenic impacts on community structure and function within intertidal ecosystems

生态系统功能与群落结构之间的关系是复杂的、动态的。了解这种复杂相互作用的机制以及这种关系如何随着我们改变环境而变化是一个具有挑战性的问题。这一挑战现在尤其重要，因为气候变化和污染等人类活动正在迅速改变水生和陆生群落，从而改变营养物质和元素在这些系统中的循环方式。维护生态系统是一项必要条件，因为作为一个社会，我们依赖这些系统来获得健康的土壤、清洁的空气和水。** 2004年，“微塑料”一词被引入来描述一种新认识到的污染物;小于5毫米的微塑料（例如，化妆品磨砂中的微珠）和来源于较大塑料物品降解的微塑料（例如，瓶）。 越来越多的文献表明，这些污染物对海洋生态系统和物种构成威胁，包括依赖这些生态系统提供服务和商品的人类。* 关于微塑料对水生生态系统的影响，问题仍然多于答案。 数据缺口包括沉积物中微塑料在吸附金属能力方面的“地球化学”行为、沉积物中与微塑料相关的金属的生物利用度，以及这些金属通过海洋食物网转移到包括人类在内的更高营养水平的潜力。* 传统上，沉积物被描述为有机物和锰和铁的氧化物的百分比。这三个组成部分是影响沉积物过程的关键因素，如沉积物-无机生物的金属生物利用度。由于沉积物中存在高浓度的微塑料（高达8000微塑料kg-1沉积物）以及这些颗粒物影响地球化学过程的潜力，沉积物必须被视为不仅由经典的地球化学参数组成，而且现在还包括微塑料。微塑料有可能作为镉等有毒金属的第四个吸附位点，通过竞争其他三种沉积物成分，提供迄今为止量化的金属进入食物网。微塑料对金属的吸附也可能取决于沉积物基质（例如，有机物含量高的沉积物与有机物含量低的沉积物相比将导致微塑料对金属的吸附较少）和微塑料的类型（例如，微珠对纤维）。 我的5年研究计划的目标是解决这些关键数据缺口，并确定微塑料在通过潮间带食物网转移有毒金属中的作用。然后，这些新信息可用于评估沉积物中存在微塑料的风险最大的沿海生态系统，以确定其在海洋食物网内污染物转移中的作用。

The relationship between ecosystem function and community structure is complex and dynamic. Understanding the mechanisms underlying this complex interplay and how this relationship changes as we modify our environment is a challenging problem. This challenge is especially relevant now as anthropogenic activities such as climate change and pollution are rapidly altering aquatic and terrestrial communities and hence how nutrients and elements cycle through these systems. The maintenance of ecosystems is a requirement because as a society we are dependent on these systems for healthy soils, clean air and water. ******In 2004, the term “microplastics” was introduced to describe a newly recognized pollutant; microplastics less than 5 mm (e.g., microbeads in cosmetic scrubs) and microplastics whose origin is the degradation of larger plastic items (e.g., bottles). An exponentially growing body of literature has demonstrated the threat these pollutants pose to marine ecosystems and those species, including humans that rely on these ecosystems for their services and goods. ******There are still more questions than answers as to the impact microplastics may have on aquatic ecosystems. Data gaps include the “geochemical” behavior of microplastics within sediments with respect to their ability to sorb metals, the bioavailability of metals associated with microplastics within sediments, and the potential for these metals to move through marine foodwebs to higher trophic levels including humans. ******Traditionally, sediments have been described as percent organic matter and oxides of manganese and iron. These three components are key factors influencing sediment processes such as metal bioavailability to sediment-ingesting organisms. With the high concentrations of microplastics that occur within sediments (up to 8000 microplastics kg-1 sediment) and the potential for these particulates to influence geochemical processes, sediments must be viewed as being comprised not only of the classic geochemical parameters, but now, also microplastics. Microplastics have the potential to act as a 4th sorption site for toxic metals such as cadmium by outcompeting the other three sediment components providing an as yet quantified entry of metals into foodwebs. Metal sorption by microplastics could also be dependent on the sediment matrix (e.g., sediments high in organic matter would result in less sorption of metals by microplastics versus sediments low in organic matter) and the type of microplastic (e.g., microbead versus fiber). The objective of my 5 year research plan is to address these key data gaps and determine the role of microplastics in the transfer of toxic metals through intertidal foodwebs. This new information can then be applied to evaluate coastal ecosystems at greatest risk to the presence of microplastics within sediments with respect to their role in the transfer of pollutants within marine food webs.**