4.7 Article

The Effect of Optical Properties on Secchi Depth and Implications for Eutrophication Management

Journal

FRONTIERS IN MARINE SCIENCE
Volume 5, Issue -, Pages -

Publisher

FRONTIERS MEDIA SA
DOI: 10.3389/fmars.2018.00496

Keywords

secchi depth; monitoring; management; eutrophication; CDOM; SPM; Chl-a; EU directives

Funding

  1. FORMAS funded initiative Strategic Marine Environmental Research programs Baltic Sea Adaptive Management (BEAM) based at Stockholm University
  2. Ecosystem dynamics in the Baltic Sea in a Changing climate perspective (EcoChange) based at Umea University
  3. Swedish National Space Board [147/12, 110/16, 175/17]
  4. Swedish Environmental Protection Agency
  5. Swedish Agency for Marine and Water Management research program Waterbody Assessment Tools for Ecological Reference conditions and status in Sweden (WATERS) [10/179, 13/33]
  6. Svealand Coastal Water Association (Svealands kustvattenvardsforbund, SKVVF)

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Successful management of coastal environments requires reliable monitoring methods and indicators. Besides Chlorophyll-a concentration (Chl-a), water transparency measured as Secchi Depth (Z(SD)) is widely used in Baltic Sea management for water quality assessment as eutrophication indicator. However, in many coastal waters not only phytoplankton but also colored dissolved organic matter (CDOM) and suspended particulate matter (SPM) influence the under-water light field, and therefore the Z(SD). In this study all three main optical variables (CDOM, Chl-a, and SPM [organic and inorganic]) as well as Z(SD) were measured in three Swedish regions: the Bothnian Sea, the Baltic Proper, and the Skagerrak in 2010-2014. Regional multiple regressions with Chl-a, CDOM, and inorganic SPM as predictors explained the variations in Z(SD) well (R-adj(2) = 0.53-0.84). Commonality analyses of the regressions indicated considerable differences between regions regarding the contribution of each factor to the variance, R-adj(2), in Z(SD). CDOM explained most of the variance in the Bothnian Sea and the Skagerrak; in general, Chl-a contributed only modestly to the Z(SD) variance. In the Baltic Proper the largest contribution was from the interaction of all three variables. As expected, the link between Chl-a and Z(SD) was much weaker in the Bothnian Sea with high CDOM absorption and SPM concentration. When applying the Swedish EU Water Framework Directive threshold for Good/Moderate Chl-a status in the models it was shown that Z(SD) is neither a sufficient indicator for eutrophication, nor for changes in Chl-a. Natural coastal gradients in CDOM and SPM influence the reference conditions for Z(SD) and other eutrophication indicators, such as the depth distribution of macro-algae. Hence, setting targets for these indicators based on reference Chl-a concentrations and simple Chl-a to Z(SD) relationships might in some cases be inappropriate and misleading due to overestimation of water transparency under natural conditions.

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