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Effects of Posidonia oceanica (L.) Delile (1813) Flowering on elemental components and on trace elements concentrations

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Effects of Posidonia oceanica (L.) Delile (1813) Flowering

on elemental components and on trace elements

concentrations

Laurence Lefebvre

1*

and Sylvie Gobert

1,2

1, Laboratory of Oceanology,MARE Centre, University of Liège, B6C Allée du 6 août, 15 Sart-Tilman,

4000 Liège, Belgium.. 2, STAtion de Recherche Sous-marine et Oceanographique (STARESO), Pointe

Revellata, BP 33, 20260 Calvi,France. *Author: l.lefebvre@uliege.be

Background

Aims and Method

Biometry

Trace elements analysis

CN concentrations

Take home message

Acknowledgment

Posidonia oceanica : a

magniolophyte endemic to the

Mediterranean Sea. Its

flowering is patchy and unusual

(Balestri et Vallerini,2003). In 2003, an

intense flowering event was recorded in the Mediterranean Sea with a high percentage of flowering (PF) and flowering intensity (FI) (PF = 0.86 and IF = 0.23 + -0.03 infl./stem (Diaz-Almela et al.,2006,2007). Since 2003,

the flowering phenomena are more frequent in Revelatta Bay.

• Research question:

Does the frequency of the flowering phenomenon impact the dynamics of CNP and traces elements in

P.oceanica tissues (comparison between the last flowering event in 2012 and that of 2018) ? Is the meadow weakening as a result of this stress?

(Gobert.,2002; Diaz-Almela et al., 2006; Calvo et al.,2006).

Sampling:

5 flowering and 5 non-flowering shoots were randomly taken at 10m depth and frozen at -18°C.

• Sampling site:

The port of STARESO, the marine research station, was chosen for its low anthropic impact and its accessibility (same sampling site in 2012).

• Analyzes of:

 Biometry (Giraud,1979; Dauby et Poulicek,1995)

 The CN elemental composition

(elemental analyser: vario MICRO cube™

, Elementar).

 P and Trace elements

(inductively Coupled Plasma Mass Spectrometry: ICP-MS ELAN DRC II, PerkinElmer Inc.).

This study is part of the STARE-CAPMED project funded by the STARESO Institute, The Territorial Collectivity

of Corsica (CDC) and The Rhône Mediterranean Corsica Water Agency.

• Negative impact on the biometry of flowering shoots;

• Al: soil contaminant, co-absorption with Fe (Amiard,2011; Benton Jones,2012; Barabasz et al.,2002; Richir, 2012).

• Fe: essential element for flowering (Garnett et Graham,2005;Tomoko et al.,2011).

• Cu: essential element for flowering and accumulated for fruit formation (Brown et Clark,1977;Garnell et Graham,2005).

• Al, Fe and Cu accumulate in the flowers • Depleting in the rest of the shoot.

• Fe ↓↓ in 2018  Al counterbalance ( co-absorption).

• Poor environment.

• Non-flowering shoots present a stronger concentration in essentials trace elements.

• The increasing frequency of flowering event in the P. oceanica meadow could have a negative long-term impact on the plant and its environment.

• During each flowering, the plant dedicates a large amount of resources in the flowers and deplete the rest of its system.

• C%wd is lower in inflorescence;

• N%wd is lower in leaves of flowering shoots (Gobert et al.,2005).

• N is limited in the study site and an efficient resorption of N arise from leaves to ensure the flowering event.

Modified from (Giraud et al, 1979).

The maximum flowering intensity would be reached every 10 years

(Pergent et al.,1989).

Mediterranean Sea,Corsica-France, 42°35’N,8°43’E

T °C

Δ Flowering

• Even more visible on adult leaves (Gobert et al.,2001).

• The inflorescence energy

is used to the detriment of other leaves.

• Modification in the

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