Dissolved Organic Carbon along the Louisiana coast from MODIS and MERIS satellite data Nazanin Chaichi Tehrani1, Eurico J. D’Sa 1 1School of the Coast and Environment, Department of Oceanography and Coastal Sciences ,Coastal Studies Institute Louisiana State University, Baton Rouge, LA 70803, U.S.A. [email protected] Abstract 5. Results Colored dissolved organic matter (CDOM), the optically active fraction of dissolved organic matter can be used as an alternative proxy to trace Dissolved organic carbon (DOC). Satellite-derived CDOM, and in situ CDOM and DOC concentrations were used to derive DOC from MODIS and MERIS. To develop a CDOM retrieval algorithm, empirical relationships between CDOM absorption coefficient at 412 nm (aCDOM(412)) and remote sensing reflectance ratios (Rrs(488)/Rrs(555)) for MODIS and (Rrs(510)/Rrs(560)) for MERIS were established. Further, empirical algorithms were developed to estimate DOC concentration using the relationship between in situ aCDOM(412) and DOC, as well as using the newly developed CDOM empirical algorithms. Algorithms were evaluated by comparing MODIS/MERIS-derived DOC with in situ DOC measurements. These preliminary results indicate that newly developed DOC retrieval algorithms performed reasonably well for the Louisiana coast. However, further evaluation of these algorithms are ongoing. 1. Introduction 5.1. CDOM-DOC relationship: To develop an empirical algorithm to derive DOC concentration remotely and using CDOM’s optical signature as a proxy for DOC, the main condition is conservative behavior between DOC and CDOM. So, DOC was plotted against CDOM to investigate conservative behavior of DOC. Figure (2-A) and (2-B) show the relationship between DOC and CDOM in spring-winter and summer, respectively. 5.2. CDOM algorithm development In order to develop an empirical algorithm to retrieve surface aCDOM(412), The Rrs band ratios Rrs(488)/ Rrs(555) for MODIS-Aqua and Rrs(510)/Rrs(560) for MERIS-Envisat were regressed against coincident in situ aCDOM(412) (Figure (3-A) and (3-B)). Figure (4-A) and (4-B) show surface CDOM distribution map from MODIS and MERIS for Feb 6, 2007, respectively. The validation matchup comparison between in situ and satellite-derived aCDOM(412) illustrates estimation of aCDOM(412) with Bias = 0.093, RMSE= 0.176, and R2 = 0.4 for MODIS(Figure 4-C), and Bias= 0.089, RMSE= 0.3, R2= 0.42 for MERIS (Figure 4-D). 800 (A) y = 137.22x+124.20 R2=0.90 400 400 200 200 0 0 1 2 3 4 2.5 (A) 2.0 1.5 1.0 y=0.4729+1.4831*exp(-4.6419*x) R2=0.679 0.5 0.5 0.0 (D) 1.0 1.5 3.0 0.0 1.0 2.0 2.0 2.5 3.0 May/Jul/Aug 2005 Apr 2007 Apr/Jun 2008 Aug 2009 best-fit line 2.5 (B) 2.0 B C aCDOM(412) MODIS 0.472 1.48 4.64 0.67 aCDOM(412) MERIS 510/560 0.617 0.66 2.47 0.62 Products DOC_MODIS_summer Bias 2.420 RMSE 26.69 SI 0.15 R2 0.52 Slope 0.61 Intercept 66.18 N 25 DOC_MERIS_summer 5.300 30.02 0.17 0.58 0.39 109.15 19 DOC_MODIS_spring-winter -13.67 32.29 0.22 0.40 0.43 56.96 25 DOC_MERIS_spring-winter 44.22 0.21 0.72 0.99 -2.39 7 -3.500 (A) (B) 1.5 y= 0.6176+0.6606*exp(-2.477x) R2=0.624 1.0 0.5 0.0 3.0 0.0 In situ aCDOM (412) (m-1) (E) A 1.0 2.0 3.0 In situ aCDOM(412) (m-1) Figure 3. (A) MODIS-derived Rrs band ratio (488nm and 555 nm) plotted against in situ surface aCDOM (412) (B) MERIS-derived Rrs band ratio ( 510nm and 560nm) plotted against in situ surface aCDOM (412). (A) (B) Figure 6. (A) MODIS-derived surface DOC (µmol C L-1) concentration for Feb 6, 2007, (B) MERIS-derived surface DOC concentration (µmol C L-1) for the same date. Figure .1 (A). Map of study area in the northern Gulf of Mexico(A). Location of stations in (B) March, May, July and August 2005, (C) March, April, May, July 2007, (D) Feb, April, June 2008, (E) August 2009. 6. Conclusion 3. Data A conservative behavior of CDOM and DOC was obtained for both spring-winter and summer seasons. The high correlation between CDOM and DOC shows that the distribution of DOC was highly influenced by physical mixing between two-end members. The conservative behavior enables us to relate DOC to remote sensing reflectance. The seasonal relationships between aCDOM(412) and DOC were combined with the aCDOM(412)-Rrs ratio to construct DOC seasonal empirical algorithms. Then satellite-derived DOC values were correlated against in situ DOC values to test algorithms’ performance. 3.1. Satellite remote sensing 3.2. Field Data 2.0 1.0 (C) (D) 0.8 0.6 0.4 Bias= 0.093 RMSE=0.17 SI=0.45 2 R = 0.4 n=18 0.2 1.5 7. Acknowledgments: This work was supported by a NASA grant NNX09AR7OG. Authors would like to thank C. Osburn (UNC), T. Bianchi (Texas A&M) and B. Schaeffer (EPA) for the data used in this study 1.0 8. References Bias=0.089 RMSE=0.3 SI=0.16 R2=0.42 n=17 0.5 0.0 0.0 0.0 0.2 0.4 0.6 0.8 In situ aCDOM(412) (m-1) Field-measured data containing biogeochemical (CDOM absorption coefficient, DOC concentration) properties of water were obtained from the study area during 17 oceanographic cruises in 2005 and 2007 through 2009. Estimated aCDOM(412) (m-1) Estimated aCDOM (412) (m-1) Satellite remote sensing provides repeated and synoptic coverage of coastal and oceanic waters to monitor and analyze coastal processes. In this study MODIS/Aqua Level 1A LAC (~ 1 km at nadir, daily temporal resolution) were obtained from the NASA’s Ocean Color website and processed to Level 2 (L2) to retrieve Rrs bands at 488nm and 555nm using SeaDAS 6.0 software package. In addition, to develop an empirical algorithm to retrieve CDOM and DOC from MERIS/ENVISAT, Level 1 reduced resolution (RR) data (with a spatial resolution of ~1.2 km and daily temporal resolution) were obtained from European Space Agency (ESA) and processed to Level 2 using SeaDAS 6.0 software package. 1.0 R2 Rrs Band Ratio 488/555 Algorithms Evaluation aCDOM(412) (m-1) Mar/May/jun/jul2005 Apr/May/Auh 2007 Apr 2008 Aug 2009 best-fit line Satellite Figure 5. The procedure chart to develop DOC empirical algorithm. Table 2. Summary of error statistics obtained from validation matchup comparisons surface DOC concentration derived from MODIS and MERIS for the summer and spring-winter seasons. 0.0 Satellite (Rrs510/Rrs560) (A) 3.0 Product MODIS Data (B) Figure 2. Relationship between (A) aCDOM (412) and DOC in spring-winter, (B) aCDOM (412) and DOC in summer. Satellite (Rrs488/Rrs555) The study area is located in the northern Gulf of Mexico on the Texas-Louisiana shelf, covering the region from latitude 28.00° to 30.5° N and longitude 88.0° to 93.00° W. It is reported that the Mississippi River discharges 3.1×10-3 Pg of DOC into the Gulf of Mexico annually which accounts for 1.2% of the total global input of DOC from rivers to the ocean. Figure 1 shows our study area, our sampling locations for 2005, 2007, 2008, and 2009. (C) (B) Table 1. Summary of fitted coefficients for the regional MODIS and MERIS empirical algorithm for surface DOC concentration retrieval. MERIS Data 0 5 Seasonal DOC-CDOM Equations DOC=127.027 ln [(Rrs ratio-A)/B])/(-C)+77 Spring-Winter DOC=137.22 ln[(Rrs ratio-A)/B])/(-C)+124.20 Summer 600 aCDOM(412) (m-1) 2. Study Area CDOM-Rrs Equations for MODIS and MERIS 800 y = 127.027x+77.97 R2=0.90 600 DOC (µM) Dissolved organic carbon (DOC) as an energy source for heterotrophic bacteria and as a pool of carbon on the time scale of ocean circulation plays a critical role in the ocean carbon cycle and in the biological pump. As in situ measurement and analysis of DOC is time-consuming and expensive ocean color sensors provides an unprecedented tool with synoptic and repeated coverage. However, DOC cannot be sensed by satellites directly, but CDOM, the colored fraction of DOC, can be measured remotely and utilized as an inexpensive intermediary to investigate the carbon cycle and to estimate the standing stock of DOC in aquatic environments. Therefore a satellite based algorithm is first required to remotely estimate CDOM; then a conservative relationship between CDOM and DOC is essential for relating satellite-derive CDOM to DOC. 5.3. DOC Empirical Algorithm The DOC retrieval algorithms for both MODIS and MERIS were obtained by combining the aCDOM(412)-Rrs relationships with seasonal aCDOM(412)-DOC relationships, and then the seasonal DOC-Rrs relationships for the springwinter and the summer seasons were constructed , see Table 1. To evaluate DOC algorithms performance, MODIS/MERIS-derived DOC was compared with in situ measured surface DOC concentration, see Table 2. Figure (6-A) and (6-B) show surface DOC concentration from MODIS and MERIS, respectively, for Feb 6, 2007. 0.0 0.5 1.0 1.5 2.0 In situ aCDOM(412) (m-1) Figure 4. CDOM absorption map (aCDOM(412)) for Feb 6, 2007 using (A) the MODIS algorithm, (B) the MERIS algorithm for Feb 6, 2007; scatter plots between (C) MODIS-derived aCDOM (412) and in situ surface aCDOM(412), and (D) MERIS-derived aCDOM(412) and in situ surface aCDOM(412). 1. D'SA, E. J., and DIMARCO, S. F., 2009, Seasonal variability and controls on chromophoric dissolved organic matter in a large riverdominated coastal margin. Limnology and Oceanography, 54, 2233-2242. 2. D’SA, E.J., MILLER, R.L., DEL CASTILLO, C.E., 2006. Bio-Optical properties and ocean color algorithms for coastal waters influenced by the Mississippi River during a cold front. Applied Optics 45,No.28.7410-7428. 3. DEL CASTILLO, C. E., and MILLER, R. L., 2008, On the use of ocean color remote sensing to measure the transport of dissolved organic carbon by the Mississippi River Plume. Remote Sensing of Environment, 112, 836-844. 4. MANNINO, A., RUSS, M. E., and HOOKER, S. B., 2008, Algorithm development and validation for satellite-derived distributions of DOC and CDOM in the US Middle Atlantic Bight. Journal of Geophysical Research-Oceans, 113.
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