Reports

Contents

Title: East End - NDVI (SRS, Apogee, Planet)
Date:2017-06-07 - 2021-04-27
Data File: EE_NDVI.csv
Refers to:EE,2046503390,2046503344,1053,1054

Various sensors measuring NDVI have been installed across the Delta sites over the last several years. At some sites, the SRS sensors from Decagon/METER have been drifting low, so I wanted to compare them with other NDVI measurements.

  • SRS sensor (Decagon/METER): A pair of photodiodes with cosine correcting Teflon diffuser and hemispherical view. Red band is measured at 650nm and NIR band is measured at 810nm.
  • SR-411 sensor (Apogee): A pair of photodiodes with acrylic diffuser and hemispherical view. Red band is measured at 650nm and NIR band is measured at 810nm.
  • Planet Labs data: L3H (CESTEM) alpha data product. Pixel size is 3m, and there are daily gap-filled images from 2018-2020. Gap fills are done with Planet imagery from the day before and after, combined with daily MODIS data. From the full image, Joe cut out a 730mx730m tile for each site, centered on the tower. Product includes NDVI, GCC, ECI, and the following reflectances: red, NIR, green, blue. For more information, see Box/Biometlab/Remote_Sensing/PlanetLabs/L3H_distribution_lodi_islands_readme.pdf.
  • Broadband NDVI: NDVI calculated using reflected SW and PAR data from the tower, called "broadband" because it uses the broader bands of shortwave and PAR radiation rather than the narrow bands of the SRS and Apogee sensors. See Huemmrich et al., 1999 in Journal of Geophysical Research: Atmospheres and Tittebrand et al., 2009 in Theoretical and Applied Climatology.

I used Joe's datafetch tool to calculate daily average mid-day values of NDVI and GCC from the various sensors. Mid-day values included data from 11:00 to 13:00, 5 values a day. I despiked the data in Excel.

  • NDVI = (NIR reflectance - Red reflectance)/(NIR reflectance + Red reflectance)
  • Broadband NDVI = (rho_NIR-rho_PAR)/(rho_NIR+rho_PAR)
    • rho_NIR= (SWout-PARout)/(SWin-PARin)
    • rho_PAR=(PARout/PARin)
    • Units of both SW and PAR should be in W/m2. Use the conversion 4.6 umol/m2/s = 1 W/m2 to convert the usual PAR units (umol/m2/s) to W/m2.

See reports for other Delta sites here:

Bouldin Alfalfa

Bouldin Corn

East End

East Pond / Sherman Wetland Temp Tower (both sites had same set of SRS sensors)

Mayberry

Sherman Wetland

Twitchell Alfalfa / Sherman Barn (both sites had same set of SRS sensors)

West Pond

 

Site SRS sensor (incoming/outgoing) SR-411 sensor (incoming/outgoing) Summary
Calibration equation
East End sn 2046503390/ sn 2046503344 sn 1053 /sn 1054

At East End, SRS NDVI data is bad starting in November 2017; do not use. 650in and 810out are both bad.

  • Coming soon

16301255400842.png

Arable image of East End on June 29, 2018 (DOY 180). Lighter colors are higher NDVI and darker colors are lower NDVI (e.g., roads). I used a sampling area of 9 pixels, marked by the red box. Each pixel is 3x3m, so the total sampling area is 9x9m.

 

Figure 1. East End data. SRS data is suspicious because peak annual NDVI decreases year after year. Broadband NDVI peak is consistent across the whole time series and peak NDVI from the Planet imagery is consistent in 2018-2020. Broadband and Planet NDVI values match well. Apogee NDVI values from fall 2020 are similar to the SRS NDVI values when they those sensors were first installed in 2017.

 

Figure 2. SRS_650in peak is decreasing every year while SRS_810in peak is steady every year. At the least, the incoming sensor at EE is bad.

 

Figure 3. SRS_650out peak is stable every year, although it increases in 2021. SRS_810out peak decreases every year. For the outgoing sensor, it's hard to say from this figure if the changes are because of vegetation changes or because of sensor decays. However, Figure 5 below with NIR reflectance shows that the SRS peak decreases year-over-year compared to the PL peaks, so the 810out sensor is indeed bad.

 

Figure 4. Red reflectances from the SRS and PL data. Red reflectance peaks in the winter when plants are brown. The SRS red reflectance peak has increased in the last 2 winters because of the bad 650in sensor..

 

Figure 5. NIR reflectance from the SRS and PL data. NIR reflectance peaks in the summer when plants are green. SRS NIR reflectance peak has dcreased year after year, while the PL data show a similar peak in 2018 and 2019 with a higher peak in 2020 (all the dfPAR from fires in 2020?). The difference  in 2018 and 2019 between SRS and PL peaks confirm that the SRS 810out sensor is bad.

 

Regression Data

Residuals

Figure 6. Linear regression of EE data. What a mess! But we can still glean some info I think. The multiple clusters of the SRS-Planet regression and SRS-Broadband seem to indicate the SRS sensor is drifting through time. The SRS-Apogee regression has an ok fit, but since we have less than a year of Apogee data, it doesn't tell us much about how the SRS sensor has changed through time.

 

Regression Data

Residuals

Figure 7. Linear regression of EE data from 2018-02-12 to 2018-10-03 only. Originally, I thought this was the period the SRS sensor seemed most stable in its first year. Not the best fit. But based on new comparisons with Broadband NDVI, it seems the SRS sensor was bad starting November 2017, so a regression using 2018 data is not really worthwhile anyways.

 

Figure 8. Linear regression of EE data 2017-06-07 to 2017-10-31 only. R2=0.85. This relationship looks better than the previous regression including 2018 data. I think the SRS data is bad starting Nov 2017.

 

Figure 9. Corrected SRS NDVI data for 2019-present using the SRS-Planet relationship from 2018 and the SRS-Broadband relationship from 2017. This correction is not very good because it does not include a time component. Next step is to figure out a time-based correction.