Key Laboratory of Aquatic Botany and Watershed Ecology, Wuhan Botanical Garden, Chinese Academy of Sciences, Wuhan 430074, China; Australian Rivers Institute and Griffith School of Environment, Griffith University, Brisbane 4111, Australia; College of Life Sciences, University of Chinese Academy of Sciences, Beijing 100049, China.
Australian Rivers Institute and Griffith School of Environment, Griffith University, Brisbane 4111, Australia.
Sci Total Environ. 2018 Mar;616-617:899-907. doi: 10.1016/j.scitotenv.2017.10.230. Epub 2017 Oct 26.
Decline of submerged vegetation is one of the most serious ecological problems in eutrophic lakes worldwide. Although restoration of submerged vegetation is widely assumed to enhance ecological functions (e.g., nitrogen removal) and aquatic biodiversity, the evidence for this assumption is very limited. Here, we investigated the spatio-temporal patterns of sediment potential nitrification, unamended denitrification and NO production rates along a vegetation gradient in the Lake Honghu, where submerged vegetation was largely restored by prohibiting net-pen aquaculture. We also used five functional genes as markers to quantify the abundance of sediment nitrifying and denitrifying microorganisms. Results showed that unvegetated sediments supported greater nitrification rates than rhizosphere sediments of perennial or seasonal vegetation. However, the absence of submerged vegetation had no significant effect on denitrification and NO production rates. Additionally, the abundance of functional microorganisms in sediments was not significantly different among vegetation types. Season had a strong effect on both nitrogen cycling processes and microbial abundances. The highest nitrification rates were observed in September, while the highest denitrification rates occurred in December. The temporal variation of sediment nitrification, denitrification and NO production rates could be due to changes in water quality and sediment properties rather than submerged vegetation and microbial abundances. Our findings highlight that vegetation restoration in eutrophic lakes improves water quality but does not enhance sediment nitrogen removal rates and microbial abundances. Therefore, for reducing the N level in eutrophic lakes, major efforts should be made to control nutrients export from terrestrial ecosystems.
水生植被的衰退是全球富营养化湖泊面临的最严重生态问题之一。尽管人们普遍认为恢复水生植被可以增强生态功能(如氮去除)和水生生物多样性,但这一假设的证据非常有限。在这里,我们调查了沿洪湖植被梯度的沉积物潜在硝化、未施肥反硝化和 NO 产生速率的时空格局,在洪湖,通过禁止网箱养殖,水生植被得到了广泛的恢复。我们还使用了五个功能基因作为标记来量化沉积物硝化和反硝化微生物的丰度。结果表明,无植被沉积物的硝化速率大于多年生或季节性植被的根际沉积物。然而,没有水生植被对反硝化和 NO 产生速率没有显著影响。此外,沉积物中功能微生物的丰度在植被类型之间没有显著差异。季节对氮循环过程和微生物丰度都有强烈的影响。硝化速率最高出现在 9 月,而反硝化速率最高出现在 12 月。沉积物硝化、反硝化和 NO 产生速率的时间变化可能是由于水质和沉积物性质的变化,而不是水生植被和微生物丰度的变化。我们的研究结果表明,富营养化湖泊的植被恢复可以改善水质,但不能提高沉积物氮去除率和微生物丰度。因此,为了降低富营养化湖泊中的氮含量,应该大力控制陆地生态系统的营养物质输出。