Variations in Spectral Slope in Lake Taihu, a Large Subtropical Shallow Lake in China

ABSTRACT Spectral slope (S), describing the exponential decrease of the absorption spectrum over a given wavelength range, is an important parameter in the study of of chromophoric dissolved organic matter (CDOM) dynamics, and also an essential input parameter in remote sensing models. Furthermore, S is often used as a proxy for CDOM composition, including the ratio of fulvic to humic acids and molecular weight. The relative broad range in S values reported in the literature can be explained by the different spectral ranges and fitting methods used. A single exponential model is used to fit the S values for 17 investigations involving 458 samples in Lake Taihu from January to October in 2004. The average S value was 15.18 ± 1.39 μm−1 for the range of 280–500 nm, which fell within the range reported in the literature. The frequency distribution of S value basically obeyed a normal distribution. Significant differences in S values between summer and other seasons showed that phytoplankton degradation was one of the important sources of CDOM in summer, whereas CDOM mainly came from the river input in other seasons. Furthermore, the estimated S value decreased with increasing wavelength range used in regression. The maximum and minimum values derived from the regression were 17.89 ± 1.25 μm−1 and 13.62 ± 2.11 μm−1 for the wavelength ranges of 280–380 nm and 400–500 nm, respectively, a decrease of 23.9%. S values significantly decreased with the increase of CDOM absorption coefficients. CDOM absorption coefficients could be more appropriately estimated from exponential model introducing the variation of S with absorption coefficients, making them useful for a remote sensing bio-optical model of Lake Taihu. DOC-specific absorption coefficient a*(λ) and the parameter M describing molecular size of the humic molecules could also be used as a proxy for the sources and types of CDOM. A general relationship was found between S and a*(λ), and M values. S increased with the decrease of DOC-specific absorption coefficient and the increase of M corresponding to the decrease of molecular weight.

[1]  J. Catalán,et al.  Attenuation of ultraviolet radiation in mountain lakes: Factors controlling the among‐ and within‐lake variability , 2000 .

[2]  L. Harding,et al.  SeaWiFS retrievals of chlorophyll in Chesapeake Bay and the mid-Atlantic bight , 2005 .

[3]  R. Zika,et al.  Seasonal variation in molecular mass and optical properties of chromophoric dissolved organic material in coastal waters of southwest Florida , 2004 .

[4]  C. D. Castillo,et al.  Seasonal variability of the colored dissolved organic matter during the 1994 95 NE and SW Monsoons in the Arabian Sea , 2000 .

[5]  W. Gieskes,et al.  Regional and seasonal differences in light absorption by yellow substance in the Southern Bight of the North Sea , 1999 .

[6]  D. Kieber The effects of UV radiation in the marine environment: Photochemical production of biological substrates , 2000 .

[7]  H. de Haan,et al.  Solar UV-light penetration and photodegradation of humic substances in peaty lake water , 1993 .

[8]  Ronald D. Jones,et al.  Photochemical degradation of dissolved organic carbon and its impact on the oceanic carbon cycle , 1991, Nature.

[9]  Spectral Absorption and Fluorescence of Chromophoric Dissolved Organic Matter in Shallow Lakes in the Middle and Lower Reaches of the Yangtze River , 2005 .

[10]  R. Zika,et al.  Light‐induced destruction of the absorbance property of dissolved organic matter in seawater , 1992 .

[11]  K. Carder,et al.  Marine humic and fulvic acids: Their effects on remote sensing of ocean chlorophyll , 1989 .

[12]  H. Siegel,et al.  Ocean colour remote sensing relevant water constituents and optical properties of the Baltic Sea , 2005 .

[13]  M. DeGrandpre,et al.  Seasonal variation of CDOM and DOC in the Middle Atlantic Bight: Terrestrial inputs and photooxidation , 1997 .

[14]  M. Moran,et al.  Carbon loss and optical property changes during long‐term photochemical and biological degradation of estuarine dissolved organic matter , 2000 .

[15]  D. Morris,et al.  The role of photochemical degradation of dissolved organic carbon in regulating the UV transparency of three lakes on the Pocono Plateau , 1997 .

[16]  A. Cunningham,et al.  Radiative transfer modelling of the relationship between seawater composition and remote sensing reflectance in sea lochs and fjords , 2002 .

[17]  R. Davies‐Colley Yellow substance in coastal and marine waters round the South Island, New Zealand , 1992 .

[18]  J. Adolf,et al.  Bio-optical model for Chesapeake Bay and the Middle Atlantic Bight , 2004 .

[19]  M. Perry,et al.  In situ phytoplankton absorption, fluorescence emission, and particulate backscattering spectra determined from reflectance , 1995 .

[20]  W. Cooper,et al.  Characterization of CDOM in an organic-rich river and surrounding coastal ocean in the South Atlantic Bight , 2003, Aquatic Sciences.

[21]  D. Doxaran,et al.  Spectral signature of highly turbid waters: Application with SPOT data to quantify suspended particulate matter concentrations , 2002 .

[22]  K. Carder,et al.  Reflectance Model for Quantifying Chlorophyll- a in the Presence of Productivity Degradation Products , 1991 .

[23]  F. Chavez,et al.  Two models for absorption by coloured dissolved organic matter (CDOM) , 2002 .

[24]  Steven G. Paulsen,et al.  Ultraviolet radiation in North American lakes: Attenuation estimates from DOC measurements and implications for plankton communities , 1996 .

[25]  M. Gosselin,et al.  Interactions of ultraviolet‐B radiation, mixing, and biological activity on photobleaching of natural chromophoric dissolved organic matter: A mesocosm study , 2000 .

[26]  T. Fisher,et al.  Chromophoric dissolved organic matter and dissolved organic carbon in Chesapeake Bay , 2002 .

[27]  Tiit Kutser,et al.  Mapping lake CDOM by satellite remote sensing , 2005 .

[28]  R. Zepp,et al.  Factors Influencing Photoreactions of Dissolved Organic Matter in a Coastal River of the Southeastern United States , 1998 .

[29]  Boqiang Qin,et al.  Long-term dynamics of phytoplankton assemblages: Microcystis-domination in Lake Taihu, a large shallow lake in China , 2003 .

[30]  K. Pihlaja,et al.  Molecular size distribution and spectroscopic properties of aquatic humic substances , 1997 .

[31]  G. Ferrari,et al.  The relationship between chromophoric dissolved organic matter and dissolved organic carbon in the European Atlantic coastal area and in the West Mediterranean Sea (Gulf of Lions) , 2000 .

[32]  K. Carder,et al.  Semianalytic Moderate‐Resolution Imaging Spectrometer algorithms for chlorophyll a and absorption with bio‐optical domains based on nitrate‐depletion temperatures , 1999 .

[33]  Maria Vernet,et al.  The effects of UV radiation in the marine environment: Index , 2000 .

[34]  L. Prieur,et al.  Absorption by dissolved organic matter of the sea (yellow substance) in the UV and visible domains1 , 1981 .

[35]  B. Osborne,et al.  Light and Photosynthesis in Aquatic Ecosystems. , 1985 .

[36]  P. Huovinen,et al.  Spectral attenuation of solar ultraviolet radiation in humic lakes in Central Finland. , 2003, Chemosphere.

[37]  C. Stedmon,et al.  Optical properties and signatures of chromophoric dissolved organic matter (CDOM) in Danish coastal waters , 2000 .

[38]  R. Sempéré,et al.  Dissolved organic carbon contamination induced by filters and storage bottles , 1999 .

[39]  D. Siegel,et al.  Seasonal dynamics of colored dissolved material in the Sargasso Sea , 1998 .

[40]  Lu Wan-ning,et al.  Inversing Chlorophyll Concentration of Taihu Lake by Analytic Model , 2006, National Remote Sensing Bulletin.

[41]  Craig E. Williamson,et al.  The attenuation of solar UV radiation in lakes and the role of dissolved organic carbon , 1995 .

[42]  Christopher B. Field,et al.  Diurnal centroid of ecosystem energy and carbon fluxes at FLUXNET sites. , 2003 .

[43]  T. Fisher,et al.  Production of chromophoric dissolved organic matter fluorescence in marine and estuarine environments: an investigation into the role of phytoplankton , 2002 .

[44]  B. Qin,et al.  A Preliminary Study of Chromophoric Dissolved Organic Matter (CDOM) in Lake Taihu, a Shallow Subtropical Lake in China , 2005 .

[45]  Yosef Z. Yacobi,et al.  Absorption spectroscopy of colored dissolved organic carbon in Georgia (USA) rivers: The impact of molecular size distribution , 2003 .

[46]  M. Suzumura,et al.  Origin and distribution of inositol hexaphosphate in estuarine and coastal sediments , 1995 .

[47]  Dariusz Stramski,et al.  Variations in the light absorption coefficients of phytoplankton, nonalgal particles, and dissolved organic matter in coastal waters around Europe , 2003 .

[48]  Arnold G. Dekker,et al.  Detection of optical water quality parameters for eutrophic waters by high resolution remote sensing , 1993 .

[49]  J. Morell,et al.  Analysis of the optical properties of the Orinoco River plume by absorption and fluorescence spectroscopy , 1999 .

[50]  E. Aas,et al.  Spectral light absorption by yellow substance in the Kattegat-Skagerrak area , 2001 .

[51]  M. Kishino,et al.  Retrieval of Chlorophyll a, suspended solids, and colored dissolved organic matter in Tokyo Bay using ASTER data , 2005 .

[52]  Michael S. Twardowski,et al.  Photobleaching of aquatic dissolved materials: Absorption removal, spectral alteration, and their interrelationship , 2002 .

[53]  Piotr Kowalczuk,et al.  Modeling absorption by CDOM in the Baltic Sea from season, salinity and chlorophyll , 2006 .