On the production, elemental composition (C, N, P) and distribution of photosynthetic organic matter in the Southern Black Sea

Author(s):  
Ayşen Yilmaz ◽  
Süleyman Tuğrul ◽  
Çolpan Polat ◽  
Dilek Ediger ◽  
Yeşim Çoban ◽  
...  
2018 ◽  
Vol 63 (3) ◽  
pp. 1425-1443 ◽  
Author(s):  
Andrew R. Margolin ◽  
Margherita Gonnelli ◽  
Dennis A. Hansell ◽  
Chiara Santinelli

2013 ◽  
Vol 10 (6) ◽  
pp. 3943-3962 ◽  
Author(s):  
A. Capet ◽  
J.-M. Beckers ◽  
M. Grégoire

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.


2016 ◽  
Vol 1 (2) ◽  
pp. 3-17 ◽  
Author(s):  
N. K. Revkov

Lessepsian invader Anadara kagoshimensis is one of the important elements in the adaptive transformation of the Black sea shelf ecosystem in the second half of the XX century. The aim of the work is to analyse the Black Sea spatial and temporal colonization by this species according to the benthic database of Benthos Ecology Department of IMBR RAS (for the Crimean coasts) and literary sources for the whole Black Sea basin. The phases of this process are considered. A 10-year latency period followed after the first detection anadara in 1968 at Caucasian shelf. The main wave of anadara colonization in the Black Sea covered the Western and Eastern parts of the sea and fall within the period from second half of 1970s to 1980s. During that time period the extended development of A. kagoshimensis lead to forming own reproductive potential for next steps of expansion of this species to Anatolian and Crimean coasts in 1990s. About 20–25 years delay in detection of introduced species at the Northern and Southern parts of the Black Sea shelf, in presence at the Western and Eastern parts, could be an evidence of existing hydrological barrier between far distant nearshore areas of the Black Sea shelf. The reasons of the fluctuations in development of this species settlements are discussed. The phenomenon of introduction and mass development of A. kagoshimensis in the Black Sea during its the “most demand” period as a consumer of excess amount of organic matter, in conditions of eutrophication’s peak in the Black Sea basin at the end of 1980s – the beginning of 1990s is marked. Estuarine areas of the Black Sea shelf enriched by organic matter are the most favourable conditions for the mass development of this species. This quantitative rising is due to wide ecological plasticity and stress tolerance of A. kagoshimensis, which are determined by its physiological and biochemical adaptations to a hypoxic conditions often appearing during eutrophication. Based on parameters of abundance and biomass the actual implementation of A. kagoshimensis biotic potential in the Black Sea is revealed at least within Eastern and Western areas of the shelf, where peaks of its quantitative development is already passed in previous years. This conclusion for the Crimean sector is not obvious because of more recent invasion by anadara of this region. A decrease and stabilization of A. kagoshimensis development, with the exception of local zones near organic ”pollution” sources should be expected under maintaining the tendency of the basin deeutrophication.


Author(s):  
E. A. Tikhonova ◽  

As part of the 113th cruise of the R/V “Professor Vodyanitsky”, research was conducted on organic pollution of bottom sediments in the coastal areas of Crimea and the Caucasus, as well as the water area in front of the Kerch Strait. Concentration of chloroformextractable substances was determined by the weight method and that of petroleum hydrocarbons was determined using infrared spectrometry. Both in 2020 and 2016 (the 83d cruise of the R/V “Professor Vodyanitsky”), properties of the bottom sediments of the Crimean and Caucasian coasts were typical of the marine soils of this region. This indicates that the studied water areas are generally in good condition. In accordance with the regional classification of bottom sediment pollution, the maximum concentrations of chloroform-extractable substances obtained for both the Black Sea and the Sea of Azov coast indicate pollution level III (23% of analysed samples). These values were found in bottom sediments in the Sevastopol water area (225 mg·100 g-1), in the coastal area of Cape Tarkhankut (120 mg·100 g-1) and Karadag (120 mg·100 g-1), the southern part of the Sea of Azov (125 mg·100 g-1) and Tuapse (110 mg·100 g-1). The content of chloroform-extractable substances in bottom sediments off the Black Sea coast of the Caucasus and the Sea of Azov coast is slightly lower than that off the Crimean coast. Pollution level II is assigned to bottom sediments in 46 % of the samples, with an average concentration of 72 mg·100 g-1 of air-dry solids. The rest (31 %) of the studied area was classified as conditionally clean (pollution level I, i. e. less than 50 mg·100 g-1). There has been a slight increase in the concentration of petroleum hydrocarbons in the bottom sediments of both the Black Sea and the Sea of Azov and their share in the total amount of chloroformextractable substances. In general, the level of pollution of bottom sediments by organic matter remained unchanged if compared with previous years, in particular with the data from 2016


1993 ◽  
Author(s):  
Alexander M. Chekalyuk ◽  
Dmitrii K. Bunin ◽  
A. V. Chechendaev ◽  
M. Y. Gorbunov ◽  
D. V. Klimov ◽  
...  

Sign in / Sign up

Export Citation Format

Share Document