Full text: XVIIIth Congress (Part B7)

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The objectives of this paper are thus to use 
CZCS imagery to estimate the concentrations of 
the major photosynthetic pigment (chlorophyll 
a plus phaeophytin) in the GSL and to charac- 
terize their spatio-temporal distribution. 
This study ig the first to provide ‘a synoptic 
viewoof phytoplankton pigments in the whole 
Qulf of St. Lawrence using remote sensing 
data. 
2. METHODOLOGY 
Study area 
The GSL system (Figure 1) is a semi-enclosed 
sea of about 200 000 km?, located between 45- 
57 °N and 56-70 °W. It is connected with the 
Atlantic Ocean through Cabot Strait (104 km 
wide and 480 m deep), and Belle-Isle Strait 
(16 km wide and 60 m deep). The bathymetry of 
the gulf is dominated by the Laurentian 
Channel (350 m), running from Cabot Strait to 
the Saguenay River with a branch toward the 
northeast. The southern part of the gulf is a 
large shallow area of average depth 50 m. Due 
to a large annual freshwater input of about 
424 kn? (Bugden et al, 1982), most of which 
(75$) originating from the St. Lawrence River 
system, circulation of the GSL waters is basi- 
cally density-driven and the water column in 
the gulf is vertically stratified into three 
layers during the summer. 
Image analysis 
Surface phytoplankton pigments (chlorophyll a 
plus phaeophytin) in the GSL were evaluated 
using a set of 80 CZCS images taken between 
March and September during the first three 
years of the satellite life (1979-1981). only 
these years were considered because the sensor 
was affected by erratic loss of sensitivity 
afterward (Evans and Gordon, 19945. 
Radiometric corrections were done using the 
Sensor sensitivity reduction correction 
factors of Gordon‘ et a1.27^$1983b) and the 
calibration coefficients provided by Williams 
et al. (1985). Clouds and land were masked 
using the Ekstein and Simpson (1991a) method, 
while pixels contaminated by signal overflow 
Were detected with the Mueller (1988) proce- 
dure. Only gain 1 and 2 images were used in 
this study because higher gains generated 
problems related to molecular spread cor- 
rection. The molecular scattering (Rayleigh) 
Was evaluated using a single scattering model 
(Gordon et al... :1983a), on the basis: that 
Single-Rayleigh scattering is comparable to 
the multiple-Rayleigh scattering method 
(Simpson, 1993) : However, the single 
Scattering model was modified using an 
extraterrestrial solar radiance coefficient 
(Ekstein and Simpson, 1991b) and an ozone 
Optical depth value (Sturm, 1981). 
ea subtraction was done using an interac- 
EA technique (Arnone and LaViolette, 
1). This approach was selected because many 
407 
problems prevented the use of the clear water 
pixel method in. the. GSL. It allows the ope- 
raton. to..select the optimum  Angstróm 
coefficient for each of the first three CZCS 
channels. After the atmospheric corrections 
were completed, the phytoplankton pigments 
were calculated using the algorithm proposed 
by Gordon et al. (1983a). 
Sediment contaminated waters were detected by 
transforming the reflectances at 443, 520 and 
550 nm into a IHS image. Spectral signatures 
of sediment contaminated waters were then cal- 
culated in this new color space and used to 
filter the images using a supervised classifi- 
cation method. 
The images were then geometrically corrected 
by using the georeferenced data included in 
the CZCS raw data to produce a first approxi- 
mation correction which was then fine-tuned by 
rectifying the images on a stereographic 
projection using the World Data Bank Feature 
Codes. The nearest-neighbour method was used 
as the resampling scheme to avoid  distorting 
the pixel's pigment content. 
Finally, the mean pigment value of overlaping 
pixels free from clouds, overflow, and suspen- 
ded matter from each geometrically corrected 
image was calculated. Seasonal analysis was 
based on bi-monthly groups: April-May, June- 
July, and August-September, (hereafter refered 
to spring, summer, and fall). Interannual 
variability was evaluated using the mean of 
all the available images for each of the three 
years. 
  
     
  
  
MAGDALEN x 
SHALLOWS N Et 
AGDALEN \ tei fi 
"ISLAND... ^; cABOT, SN > Y 
s A! . t. 
     
   
   
NEW-BRUNSWICK 
  
  
  
Figure 1. The St. Lawrence Gulf (from de 
Lafontaine et al., 1991) 
Data validation 
The scarcity of available in situ measurements 
simultaneous with the CZCS images made the 
data validation process difficult. Using all 
the known available data, the mean chloro- 
phyll a plus phaeophytin values for the top 
fifth of the euphotic layer was calculated to 
compare with evaluated pigment values from the 
satellite images (Morel and Berthon, 1989). 
Results of the linear regression showed that 
International Archives of Photogrammetry and Remote Sensing. Vol. XXXI, Part B7. Vienna 1996 
 
	        
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