Abstract

Abstract. The Black Sea northwestern shelf (NWS) is a shallow eutrophic area in which the seasonal stratification of the water column isolates the bottom waters from the atmosphere. This prevents ventilation from counterbalancing the large consumption of oxygen due to respiration in the bottom waters and in the sediments, and sets the stage for the development of seasonal hypoxia. A three-dimensional (3-D) coupled physical–biogeochemical model is used to investigate the dynamics of bottom hypoxia in the Black Sea NWS, first at seasonal and then at interannual scales (1981–2009), and to differentiate its driving factors (climatic versus eutrophication). Model skills are evaluated by a quantitative comparison of the model results to 14 123 in situ oxygen measurements available in the NOAA World Ocean and the Black Sea Commission databases, using different error metrics. This validation exercise shows that the model is able to represent the seasonal and interannual variability of the oxygen concentration and of the occurrence of hypoxia, as well as the spatial distribution of oxygen-depleted waters. During the period 1981–2009, each year exhibits seasonal bottom hypoxia at the end of summer. This phenomenon essentially covers the northern part of the NWS – which receives large inputs of nutrients from the Danube, Dniester and Dnieper rivers – and extends, during the years of severe hypoxia, towards the Romanian bay of Constanta. An index H which merges the aspects of the spatial and temporal extension of the hypoxic event is proposed to quantify, for each year, the intensity of hypoxia as an environmental stressor. In order to explain the interannual variability of H and to disentangle its drivers, we analyze the long time series of model results by means of a stepwise multiple linear regression. This statistical model gives a general relationship that links the intensity of hypoxia to eutrophication and climate-related variables. A total of 82% of the interannual variability of H is explained by the combination of four predictors: the annual riverine nitrate load (N), the sea surface temperature in the month preceding stratification (Ts), the amount of semi-labile organic matter accumulated in the sediments (C) and the sea surface temperature during late summer (Tf). Partial regression indicates that the climatic impact on hypoxia is almost as important as that of eutrophication. Accumulation of organic matter in the sediments introduces an important inertia in the recovery process after eutrophication, with a typical timescale of 9.3 yr. Seasonal fluctuations and the heterogeneous spatial distribution complicate the monitoring of bottom hypoxia, leading to contradictory conclusions when the interpretation is done from different sets of data. In particular, it appears that the recovery reported in the literature after 1995 was overestimated due to the use of observations concentrated in areas and months not typically affected by hypoxia. This stresses the urgent need for a dedicated monitoring effort in the Black Sea NWS focused on the areas and months concerned by recurrent hypoxic events.

Highlights

  • Hypoxia is a major global environmental problem affecting marine waters and is among the most widespread deleterious anthropogenic influences

  • Hypoxic conditions may be encountered in various parts of the ocean, where water ventilation is not able to renew the oxygen consumed for the degradation of organic matter

  • The main aims of this study are (1) to understand and identify the drivers of hypoxia at seasonal and interannual scales, (2) to propose a statistical model to predict the interannual variability of hypoxia and to quantify the contributions of the identified drivers to this variability, (3) to assess the timescale of recovery of the system submitted to eutrophication due to the sediment inertia, and (4) to give some recommendations for the monitoring of hypoxia on the Black Sea northwestern shelf (NWS)

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Summary

Introduction

Hypoxia is a major global environmental problem affecting marine waters and is among the most widespread deleterious anthropogenic influences. It has been shown that low oxygen concentrations already affect living organisms above that threshold (Vaquer-Sunyer and Duarte, 2008). Hypoxic conditions may be encountered in various parts of the ocean (e.g., the coastal area, the shelf and the deep ocean), where water ventilation is not able to renew the oxygen consumed for the degradation of organic matter. The coastal area which receives the input of organic matter from rivers and adjacent land is exposed to this phenomenon. In this shallow area, where the bottom is occupied by a benthic ecosystem, the occurrence of hypoxic conditions may be lethal to these organisms and catastrophic for the benthic biodiversity (Levin et al, 2009)

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