Incorporating spatial heterogeneity into evapotranspiration estimates for bioretention basins
Abstract. Green stormwater infrastructure (GSI) systems like bioretention basins are frequently used in urban settings to reduce the amount of stormwater runoff entering combined sewer systems, thus protecting downstream waterbodies. Retaining stormwater in GSI allows it to infiltrate into the soil or return to the atmosphere via evapotranspiration (ET). While infiltration rates can be quantified with reasonable accuracy, methods of quantifying ET typically rely on models designed for homogeneous landcover like agricultural fields; the high spatial variation in factors including vegetation, light, and soil moisture renders estimates of ET from bioretention basins highly uncertain. To assess the influence of such variation on basin-scale ET and evaluate means of correcting for it, we quantified ET for a bioretention basin in Philadelphia, USA using three approaches: (1) an empirically-based model that incorporated direct measurements of ET and accounted for heterogeneity in plant size, light conditions, and microtopography, (2) an empirical estimate of ET based on changes in soil moisture that did not account for spatial heterogeneity, and (3) a series of conventional ET models that did not account for spatial heterogeneity. We further evaluated three methods of adjusting modeled ET estimates to better align with ours. Our empirically-based model found basin-scale daily ET to range from 0–6 mm d-1, with temporal variation dependent on weather conditions and time of year. A sensitivity analysis demonstrated that the spatial composition of plant height and shade strongly influenced basin-scale estimates. The soil moisture-based method found daily values to range from 0–4 mm d-1, which largely agreed with the empirically-based modeling estimates for the location where sensors were placed, but underpredicted estimates of basin-scale ET. Most conventional models overpredicted ET compared to our empirically-based values on average, though three were less sensitive to variation in atmospheric conditions (Granger-Grey, Hargreaves-Samani, and Matt-Shuttleworth) and thus overpredicted ET at the low to middle part of the range but underpredicted ET at the upper end of the range. This limited the ability of additive or multiplicative adjustments to improve agreement, though adjustments were highly effective for the three conventional models more sensitive to atmospheric conditions (Penman-Monteith ASCE, Penman-Monteith FAO, and Priestly-Taylor). The strongest agreement we could achieve came from an additive adjustment to Penman-Monteith-derived values (subtracting 2.31 mm d-1 from the ASCE formulation or 1.82 mm
d-1 from the FAO formulation). Multiplicative adjustments (i.e., landscape coefficients) and corrections accounting for shade were also effective. Our results highlight the importance of implicitly or explicitly accounting for spatial heterogeneity when quantifying ET, especially with respect to vegetation height and shade. For basins similar to our focal basin, this can be accomplished through the provided adjustments to conventional models. Additional calibration is required otherwise, but the growing availability of required data makes this increasingly viable.
General comments:
Very interesting article on how estimate at high spatial resolution the evapotranspiration fluxes (ET) in the very heterogeneous urban canopy. The subject is important for the estimation of the runoff reduction in green space but also of the water need of urban green space.
The article is outstanding due to the diversity of estimation, with measurements (chamber as the reference but also soil water content) and modeling (empirical-statistical as the reference but also a wide range of conventionnal formula).
The work is very clearly presented, with a very complete and rigourus methodology combining different aspects (shading, vegetation characterisitcs, statistical test, ...). The database with the characterisation of the site (soil, vegetation, topography, urban scene) and with the temporal series of different hydrological and meteorological variables is really interesting and outstanding.
The form is perfect, with clear text and illustration ; I do not have a look to the data (https://www.hydroshare.org/resource/ba487d9c6e4b473f88d8298499ee1c6d/), due to a lack of time.
Specific comments:
See the pdf file for specific and detailed comments.
I suggest "Minor revision" (rather than "accepted subject to technical corrections") because I suggest to add some details on the development & performance of the empirical model (adding a chapter in the Supplementary Information at least). The evaluation is presented positivly in two lines in the article (L284-285), even though the model is subsequently used as a reference throughout the rest of the article. It would be useful, at the very least, to show and discuss the observed/simulated scattergram at the basin scale, and, if possible, at the various measurement points as well.
Three other points could be add in the discussions part:
- the spatial role of other micrometeorological conditions than the radiation, for example the wind or the VPD ? Do you have some site informations of these variability (contrast in the two weather station for example) ? For another work, it could be possible / interesting to introduce such spatial variables in the empirical model ?
- At different lines in the article, the validity of conventional models (=formulas) is debated in terms of whether or not they take water stress into account (for example, lines 427–429). Upon examining the soil water content at -5cm (Fig. 3d), I find that the values are not particularly low (and one would expect higher values at greater depths) and that it is not certain that ET could be limited by soil water availability. This hypothesis is consistent with the shape of the scatter plots between ET values simulated by the empirical model and the different formulas: for example, this relationship is highly linear for the PM formulas across all ranges of ET values (Fig7), including high values whereas for these high values one might expect more severe water stress to occur. In summary, I get the impression that ET water limited situations are rare in the database, and therefore that the reasons for the offset between the empirical model and the PM models must be sought elsewhere ;
- The linearity of the relationships between the empirical and PM models, which consistently involve a simple offset, is truly impressive. A theoretical comparison of the two models could be useful for analyzing the following observation:
+ the empirical model uses the following explanatory variables: topography (via a 1/0 index), vegetation height (spatial variability only?), VPD (temporal variability only?), solar radiation (spatial and temporal variability), and soil moisture status (temporal variability at a single point); it is statistically calibrated on 7 x 11 daily ETs;
+ PM formulas primarily use the temporal variability of solar radiation, VPD, wind, and temperature, with a constant vegetation height.
So, for example, the effect of wind is taken into account in PM (via its aerodynamic term), which is not the case in the empirical model. Could this be a source of overestimation of PM ET ?