705
700 800
ity of the
scale, of
ons in The
:ed at 440 nm.
el, with d =
:pth measurement
ata. Reflection
is with
lured at a water
i reflected flux
if extinctions
mus. This
ring of the
i bottom depth
m at two
nm. Other
istant and known
500 nm and 630
, and the ratio
avelengths. Two
sured
n figure 1 and
el, with
epth
a parameter
ction at 500 nm
; the measured
unction, and
al function was
ential humus
depth
i reflection
on values and
nction, for the
the humus is
at 500 nm.
column.
r
The calculated depth using the ratio of measured
humus extinction corresponds well with the depth of
.345 m. The calculated depth based on the exponential
absorption is systematically higher than the real
depth. The relative error increases with the humus
concentration.
The choice of the two wavelengths was arbitrary. A
pair of wavelengths that introduce a smaller relative
depth error is possible. The shape of the humus
extinction spectrum determines the wavelength range
where the exponential can be used. This range is
different for humus from an other place, as can be
seen in figure 2.
The variability of the absorption spectrum of humus
from different locations in the Netherlands is shown
in figure 2. The spectra are normalized at 440 nm.
The extinction at 440 nm varied from 1.06-9.33 m 1 .
The dashed line is the humus spectrum according the
exponential function, with d = -.014 nm 1 and
Ao = 440 nm.
It turns out that the differences among the samples
are even greater than the deviation from the
exponential model in the example shown before.
4 DISCUSSION
The results, obtained with spectrophotometric
measurements, demonstate that the shape of the humus
absorption spectrum cannot be described by an
exponential function. It also appears that the
variability of the humus absorption spectrum is
considerable. The simplified depth experiment
illustrates that substantial errors are made, when
the exponential function, with a fixed value for d,
is used.
Considerable improvement in the accuracy of the
interpretation of airborne reflection measurements
may be expected when actually measured absorption
spectra of aquatic humus (part of the optical
seatruth) are used as input for the deconvolution
algorithm.
Futher progress in the mathematical description of
the absorption spectrum of humus can only be made by
the introduction of models more complicated than an
exponential curve. As a first attempt we applied
conventional factor analysis to the data-set (figure
2). Preliminary results indicate that four components
are sufficient to cover the observed variability of
shape (Krijgsman and Buiteveld, unpublished results).
It will likely be possible to obtain more accurate
correlation between optical and chemical data of
humus than was possible with the exponential model.
In further studies factor analysis will be applied
to introduce error calculation and noise-analysis in
our experimental procedures and in the analysis of
reflection spectra of more complicated and realistic
situations, e.g. by the introduction of silt and
algae in the system.
REFERENCES
Bricaud, A, A. Morel and L. Prieur 1981. Absorption
by dissolved organic matter of the sea (yellow
substance) in the UV and visible domains. Limnol.
Oceanogr. 26:43-53.
Kalle, K. 1966. The problem of Gelbstoff in the sea.
Mar. Biol. Ann. Rev. 4:203-218
Prieur, L. and S. Sathyendranath 1981, An optical
classification of coastal and oceanic waters based
on the specific absorption curves of phytoplankton
pigments, dissolved organic matter and other
particulate materials. Limnol. Oceanogr.
26:671-689.
Smith, R.C. and K.S. Baker 1981. Optical properties
of the clearest natural waters (200-800 nm).
Applied Optics 20:177-184.
Zepp, R.G. and P.F. Schlotzhauer 1981. Comparison of
photochemical behavior of various humic substances
in water: III Spectroscopic properties of humic
substances. Chemosphere 10:479-486.