Department of Climate Change, Area of Sustainability, EURECAT, Technological Centre of Catalonia, Amposta, Spain.
National Socio-Environmental Synthesis Center (SESYNC), University of Maryland, Annapolis, Maryland, USA.
Glob Chang Biol. 2023 Mar;29(5):1248-1266. doi: 10.1111/gcb.16520. Epub 2022 Dec 14.
Trends and ecological consequences of phosphorus (P) decline and increasing nitrogen (N) to phosphorus (N:P) ratios in rivers and estuaries are reviewed and discussed. Results suggest that re-oligotrophication is a dominant trend in rivers and estuaries of high-income countries in the last two-three decades, while in low-income countries widespread eutrophication occurs. The decline in P is well documented in hundreds of rivers of United States and the European Union, but the biotic response of rivers and estuaries besides phytoplankton decline such as trends in phytoplankton composition, changes in primary production, ecosystem shifts, cascading effects, changes in ecosystem metabolism, etc., have not been sufficiently monitored and investigated, neither the effects of N:P imbalance. N:P imbalance has significant ecological effects that need to be further investigated. There is a growing number of cases in which phytoplankton biomass have been shown to decrease due to re-oligotrophication, but the potential regime shift from phytoplankton to macrophyte dominance described in shallow lakes has been documented only in a few rivers and estuaries yet. The main reasons why regime shifts are rarely described in rivers and estuaries are, from one hand the scarcity of data on macrophyte cover trends, and from the other hand physical factors such as peak flows or high turbidity that could prevent a general spread of submerged macrophytes as observed in shallow lakes. Moreover, re-oligotrophication effects on rivers may be different compared to lakes (e.g., lower dominance of macrophytes) or estuaries (e.g., limitation of primary production by N instead of P) or may be dependent on river/estuary type. We conclude that river and estuary re-oligotrophication effects are complex, diverse and still little known, and in some cases are equivalent to those described in shallow lakes, but the regime shift is more likely to occur in mid to high-order rivers and shallow estuaries.
本文综述和讨论了河流和河口磷(P)下降以及氮(N)与磷(N:P)比值增加的趋势及其生态后果。结果表明,在过去二三十年,高收入国家的河流和河口呈现再贫化的主导趋势,而在低收入国家则广泛发生富营养化。在美国和欧盟的数百条河流中,P 的下降得到了很好的记录,但河流和河口除浮游植物下降之外的生物响应,如浮游植物组成的变化、初级生产力的变化、生态系统转变、级联效应、生态系统代谢的变化等,尚未得到充分监测和研究,也没有研究 N:P 失衡的影响。N:P 失衡具有显著的生态影响,需要进一步研究。越来越多的案例表明,由于再贫化,浮游植物生物量已经减少,但在少数几条河流和河口已经记录到从浮游植物向大型植物优势的潜在状态转变,而在浅湖中描述的这种状态转变尚未在其他河流和河口得到记录。状态转变在河流和河口很少被描述的主要原因,一方面是大型植物覆盖趋势数据的稀缺,另一方面是物理因素,如峰值流量或高浊度,这些因素可能会阻止像在浅湖中观察到的那样,淹没性大型植物的广泛传播。此外,与湖泊相比(例如,大型植物的优势较低)或与河口相比(例如,初级生产力受 N 而不是 P 的限制),河流再贫化的影响可能不同,或者可能取决于河流/河口的类型。我们的结论是,河流和河口的再贫化效应是复杂的、多样的,目前还知之甚少,在某些情况下与浅湖中描述的效应相当,但状态转变更可能发生在中高等级河流和浅河口。