Management


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Introduction

The  Danish and Swedish "Authorities Control- and Monitoring Programme for  the Fixed  Link across Øresund" applies aerial photography as a  means of  detecting changes in eelgrass  communities  during  the construction of  the  fixed  link.
In the  following,   we  refer to  the  Autorities Monitoring Programme and show  the most recent  results. (Published in Krause-Jensen et al. 1999).

Air photography

Air photography was carried out in august 1996-1998 from an altitude of 3000 ft in calm weather. The water transparency was generally very good. Images were recorded from a twin-engine aeroplan, Partenavia 68 observer.

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Partenavia 68 observer

The plane was equipped with a camera, Rolleiflex 6008, with a 50-mm special lens. Slides of the brand Ectachrome 200 Professional were used. Images were recorded at a resolution of 15-30 cm per pixel. In all, approximately 1500 pictures were taken to cover the Øresund area. The overlap of the images was approximately 40%: The position of the plan was established by DGPS with an accuracy of 5-10 m. The position, speed, altitude and banking was logged continuously on the flight computer by using the programme Bio Flight. Image orthoretification and image analyzing was done as descript under post-processing. 

Analysis of vegetation area coverage and biomass

Coverage of Zostera marina  was mapped on the basis of the factual information on coverage obtained by paravane diving along transects.

  (henvisning til sampling of vegetation for remote sensing analyses)

 

Results

Occurrence
Zostera marina is widely distributed in the central part of Øresund inside the 6 m depth curve. The accuracy of the analysis is lowest closest to the depth limit where coverage and biomass and, hence, reflection from the vegetation is lowest. because the transparency of the water was high when the air photographs were taken, however, it was possible to map the Zostera marina vegetation until the 6 m depth curve and sometimes even deeper. This means that it was possible to map the vegetation approximately until the depth limit of main occurrence.
In 1998, the distribution area of Zostera marina was 139,7 km². The distribution area increased from 1996 to 1997 and decreased again from 1997 to 1998.

Area coverage
The area coverage of Zostera marina was analysed on the basis of the   individual photos and supplemented with factual information on coverage obtained by paravane-diving along the transects. Using interpolation, maps where then drawn, showing the coverage of Zostera marina. In general, highest coverage is observed in the depth interval 1-4 m; in deeper water the distance between individual shoots increases, resulting in a decrease in total coverage.

Area biomass
Based on the key map of the coverage of Zostera marina and the relation between coverage and coverage-corrected biomass, a key map of the distribution of Zostera marina biomass in the central part of Øresund has been produced, figur x.  In 1998, the total Zostera biomass in the total area surveyed in Øresund was 8,944 t. The assessments of Zostera marina biomass are only approximate since some inaccuracy is contained in distribution areas, interpolation of coverage as well as in the conversion of coverage to biomass.

 

 


National
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This page was updated: 19. September 1999
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