Conclusions
We have presented a methodology to estimate tree height and canopy extent, thereby allowing the calculation of daily shade, the fractional penetration of radiation and its effect on global incoming radiation for water quality modelling purposes. This methodology includes the use of high resolution spatial data capable of capturing riparian canopy structure and a model that simulates the position of the sun across the sky for hourly or sub-hourly intervals to model the daily shade over the river surface. It also uses measurements of hourly radiation and daily sunshine duration, which are corrected to account for the shade effect in order to be input to the water quality model. The results demonstrate:
• Consideration of riparian shading is important for water quality simulation, as is demonstrated by the big differences arising when considering or not considering shade (Table 1).
• An increased level of confidence about riparian shade condition in terms of percent occupancy (proportion of channel length with trees) and fractional penetration (fraction of direct radiation reaching the river through the tree canopy) along the River Thames.
• Water quality impacts are sensitive to the level of shade as estimated using the two datasets. Calculations using EA LIDAR DSM are different to those using NTM (partly due to the seasonal coverage of the EA LIDAR DSM data).