Sydney Institute of Marine Science, Building 19 Chowder Bay Road, Mosman, New South Wales, 2088, Australia; Department of Biological Sciences, Macquarie University, North Ryde, New South Wales, 2109, Australia.
Sydney Institute of Marine Science, Building 19 Chowder Bay Road, Mosman, New South Wales, 2088, Australia; School of Biological, Earth and Environmental Sciences, University of New South Wales, 2052, Australia.
Mar Environ Res. 2021 Mar;165:105243. doi: 10.1016/j.marenvres.2020.105243. Epub 2021 Jan 5.
The marine environment is being increasingly modified by the construction of artificial structures, the impacts of which may be mitigated through eco-engineering. To date, eco-engineering has predominantly aimed to increase biodiversity, but enhancing other ecological functions is arguably of equal importance for artificial structures. Here, we manipulated complexity through habitat structure (flat, and 2.5 cm, 5 cm deep vertical and 5 cm deep horizontal crevices) and seeding with the native oyster (Saccostrea glomerata, unseeded and seeded) on concrete tiles (0.25 m × 0.25 m) affixed to seawalls to investigate whether complexity (both orientation and depth of crevices) influences particle removal rates by suspension feeders and colonisation by different functional groups, and whether there are any ecological trade-offs between these functions. After 12 months, complex seeded tiles generally supported a greater abundance of suspension feeding taxa and had higher particle removal rates than flat tiles or unseeded tiles. The richness and diversity of taxa also increased with complexity. The effect of seeding was, however, generally weaker on tiles with complex habitat structure. However, the orientation of habitat complexity and the depth of the crevices did not influence particle removal rates or colonising taxa. Colonisation by non-native taxa was low compared to total taxa richness. We did not detect negative ecological trade-offs between increased particle removal rates and diversity and abundance of key functional groups. Our results suggest that the addition of complexity to marine artificial structures could potentially be used to enhance both biodiversity and particle removal rates. Consequently, complexity should be incorporated into future eco-engineering projects to provide a range of ecological functions in urbanised estuaries.
海洋环境正日益受到人工结构的改变,这些影响可以通过生态工程来减轻。迄今为止,生态工程主要旨在增加生物多样性,但增强其他生态功能对于人工结构同样重要。在这里,我们通过生境结构(平面和 2.5cm、5cm 深的垂直和 5cm 深的水平裂缝)以及在混凝土瓦片(0.25m×0.25m)上用本地牡蛎(Saccostrea glomerata,未播种和播种)进行播种来操纵复杂性,这些瓦片固定在海堤上,以研究复杂性(裂缝的方向和深度)是否会影响悬浮食者的颗粒去除率以及不同功能组的定殖,以及这些功能之间是否存在任何生态权衡。12 个月后,复杂的播种瓦片通常比平面瓦片或未播种瓦片支持更多的悬浮食者类群,并且具有更高的颗粒去除率。类群的丰富度和多样性也随着复杂性的增加而增加。然而,播种的效果在具有复杂生境结构的瓦片上通常较弱。然而,生境复杂性的方向和裂缝的深度并不影响颗粒去除率或定殖的类群。与总类群丰富度相比,非本地类群的定殖较低。我们没有发现颗粒去除率增加与关键功能组的多样性和丰度之间存在负的生态权衡。我们的结果表明,向海洋人工结构中添加复杂性可能有助于提高生物多样性和颗粒去除率。因此,未来的生态工程项目应纳入复杂性,以在城市化河口提供一系列生态功能。