Applying near-infrared reflectance spectroscopy to predict carbon, nitrogen, phosphorus, and organic-bound cadmium in lake picoplankton

This study describes the 0.1–3 μm particle size fraction in a Precambrian Shield lake (37-ha Lake 382 in the Experimental Lakes Area, northwestern Ontario) receiving experimental additions of cadmium to determine fate and effects of low cadmium loading. This size fraction is important in binding cadmium in water. The study examined the feasibility of using near-infrared reflectance spectrophotometry (NIRS) for quantifying carbon, nitrogen, and phosphorus in this size fraction in 20-fold concentrated water samples from the lake and from a limnocorral experiment exploring the effect of fertilization on sedimentation of cadmium from the water column. NIRS was also used for detecting and characterizing organic matter in this size fraction associated with cadmium. Aliquots (1.5 ml) of the concentrated samples were applied to pre-ashed Whatman GF/C glass fibre filters. The filters containing 40–150 μg carbon, 1–21 μg nitrogen, 1–10 μg phosphorus, and 0.21–2.21 ng cadmium, were scanned by NIRS, then analyzed by traditional methods for carbon, nitrogen, and phosphorus. Cadmium was determined in the concentrated samples by atomic absorption spectrophotometry. Coefficients of determination,r2, between chemically-measured and NIRS-predicted values were 0.921 for carbon, 0.852 for nitrogen, 0.869 for phosphorus, and 0.752 for cadmium. Several lines of evidence suggested that the organic material associated with cadmium was predominantly algae <3 μm. NIRS is useful for measuring organic matter in this size fraction and is potentially useful for characterizing organic matter that binds metals.

[1]  D. Schindler,et al.  Preliminary Chemical Characterization of Waters in the Experimental Lakes Area, Northwestern Ontario , 1971 .

[2]  D. Schindler,et al.  Geography and Bathymetry of Selected Lake Basins, Experimental Lakes Area, Northwestern Ontario , 1971 .

[3]  M. Stainton,et al.  The Chemical Analysis of Fresh Water , 1977 .

[4]  T. Fearn,et al.  Near infrared spectroscopy in food analysis , 1986 .

[5]  P. Williams,et al.  Near-Infrared Technology in the Agricultural and Food Industries , 1987 .

[6]  L. Sigg,et al.  Vertical transport of heavy metals by settling particles in Lake Zurich , 1987 .

[7]  D. F. Malley,et al.  Whole lake addition of cadmium-109: radiotracer accumulation in the mussel population in the first season. , 1989, The Science of the total environment.

[8]  Effect of Cadmium on a Stable, Large Volume, Laboratory Ecosystem Containing Daphnia and Phytoplankton , 1989 .

[9]  A. Boudou,et al.  Dynamics of Cadmium, Lead, and Zinc Exchange between Nymphs of the Burrowing Mayfly Hexagenia rigida (Ephemeroptera) and the Environment , 1991 .

[10]  M. Servos,et al.  Partitioning of polychlorinated dioxins and furans between water, sediments and biota in lake mesocosms , 1992 .

[11]  Application of Near-Infrared Reflectance Spectroscopy in the Measurement of Carbon, Nitrogen, and Phosphorus in Seston from Oligotrophic Lakes , 1993 .

[12]  Evidence for particle-mediated transport of 2,3,7,8-tetrachlorodibenzofuran during gas sparging of natural water , 1993 .

[13]  R. Hesslein,et al.  Sediment–Water Distribution Coefficients and Speciation of Cadmium in a Canadian Shield Lake , 1994 .

[14]  P. C. Williams,et al.  Rapid measurement of suspended C, N, and P from Precambrian Shield Lakes using Near-infrared Reflectance Spectroscopy , 1996 .

[15]  Multi-year experimental additons of cadmium to a lake epilimnion and resulting water column cadmium concentrations , 1996 .