Tuesday, October 10, 2023

Notes about the dynamic nature of the GEOframe-Po Project

Here below you can find some provisional notes, to be improved in the next days about our Deployment of the GEOframe system to the river Po for the basin Authority of the river Po.  

Basin extraction

it's not a straightforward operation. In fact, it has never been done systematically all over Italy. It serves two opposing needs: to be objective and to align with the official grid provided by basin Authorities and Regions. The initial phase relies mainly on slope analysis and requires processing digital terrain data, which have become available only in recent years, especially if we refer to data produced with laser altimetry. The starting point is the Digital Elevation Models (DEMs) provided by the regions, which have been reprojected and standardized to correct reference systems. The initiation of the hydrographic networks is determined by an area threshold, while sub-basins, for the Po river, are delineated to have an average area of 10 km2. Procedures have been standardized in geographic information systems (GIS) over the last twenty years, but for this specific task, the Horton Machine library developed by Univrsity of Trento and HydroloGIS was used (Abera et al., 2016, serving as reference), incorporating some innovative elements: a parser to aggregate smaller basins into adjacent larger ones and addressing certain topological situations, especially those in flat areas for the subsequent use with GEOframe.
The tools was named GEOframeInputBuilder.

The extraction of lakes, particularly the large Lombard lakes and Lake Garda, required special attention and made the process less automated. Visual analysis reveals a differentiated geometry between mountain basins and lowland inter-basins, since the early years of fluvial geomorphology, but now objectively observed. The database, now available, enables statistical analysis of their geometry and topology, which previously relied on more qualitative cartographic analysis. The basin initiation with an area threshold is functional to the hydrological modelling but the reader should be aware that this topic is a very alive hydrological research topic, especially along with the work by Gianluca Botter and coworkers [insert CITATION].

The grid, as currently constructed, will be distributed for free use and will serve as a fundamental standard for further cartographic-digital and hydrological analyses and developments.

Photo by Luigi Ghirri



Interpolation

Interpolation techniques have seen significant development between the 1980s and 90s [insert citation], but especially geostatistical methods have slowly made their way into the practice of digital analysis of meteorological forcings in the hydrological cycle. These require the definition of an estimation model of the correlation between measurements, known as a variogram, the robustness of which is fundamental to the reliability of the result.
The starting database is made up of measurements collected by ground stations from regional entities operating on the Po basin. These data have been analyzed, cleaned, and subsequently interpolated, currently on each centroid of the sub-basins identified in the first phase of the work. The interpolation was carried out for precipitation and temperatures on a daily scale, as a first step to produce hourly or sub-hourly interpolation at any point of a suitable one-kilometer grid.
The interpolation technique used was kriging with drift to account for orographic effects, especially on temperature. For the interpolation of the experimental variogram, a ?linear? Exponential? What else? model was used using the interpolators implemented in GEOframe.
The interpolation covered the entire period from 1990 to today, and the data are stored in CSV files in folders containing the data for each individual sub-basin.

It is clear that the procedure is a first approximation that will serve as the basis for future improvements. For example, the extension of the interpolation on the one-kilometer grid is one aspect. The next improvement could be to introduce high-resolution reanalysis data, combining geostatistical techniques with simulations of atmospheric circulation and any data coming from radar and satellite. Convergent research come from atmospheric physics and meteorology whose resolution is arrived at the scales useful for hydrology. Some work should be done for connecting better the two communities.

Setup:

GEOframe-NewAGE allows numerous configurations, as various components are available for the same phenomenon. For the basic configuration of each single Hydrologic Response Unit (HRU), the one already partially tested in [insert citation] called Embedded Reservoir Model (ERM) was chosen, the description of which can be found in the cited bibliography or in the linked videos. In summary, the ERM model is composed of a component for interception, one for snow, when present, a fast surface runoff separator based on the Hymod model, a nonlinear reservoir for the description of the root zone, and a second nonlinear reservoir for groundwater. Structurally, it is not much different from the HBV Model [insert citation]. In the basic configuration, flood propagation is neglected.
For the part of evapotranspiration, a simple Priestley-Taylor model was used, where however the radiation is provided through a rather accurate model [insert citations].
Each of these ERM models was then connected to the others through the Net3 infrastructure [insert citation] to form a directed acyclic graph in which each node represents an HRU. Potentially, each HRU can be characterized not only by its own topographic and meteorological data, but also by its own models.
In the basic configuration, however, the same model structure is usually used for all HRUs while the values of the model parameters are obtained by subsequent calibration with spatially differentiated parameters, if the available data allow it.
The potential setup variants are numerous, encompassing at least three options for snow modeling, three for evapotranspiration modeling, and an array of choices for reservoir modeling. The inclusion or exclusion of flow propagation modules, as well as the potential elimination or addition of compartments to be modeled and their diverse connections, further expand the possibilities. An overview of potential topological configurations is presented, for instance, in [insert MaRmot citation]. As even a novice reader can comprehend, the possible combinations multiply far beyond exponentially with the number of connected Hydrological Response Units (HRUs), which can, in turn, be linked in various manners. This complexity underscores why our comprehensive study on the Po River necessitates distribution and further refinement by others to enhance the precision of the results and better align them with local needs which cannot be gained by a single yet very productive team of people. In turn this open the question on how the re-analysis performed by external researchers or teams can be accepted and inserted back into the main project.

The analysis of multiple configurations is therefore entrusted to later phases of the project.

Calibration

Among the phases of a simulation, the calibration phase is the most time-consuming. It essentially consists of a large number of attempts to combine the model parameters to reproduce the measured data as faithfully as possible. The space of possible parameters is generally very large, even for a single simulation HRU. Therefore, the tools for calibration try to use intelligent strategies (including ML) to quickly guess which are the best parameter configurations.

The goodness of the simulated values' fit to the measured ones is usually quantified through some goodness of fit (GOF) algorithms. In our case, these are generally the KGE [insert citation] or the NS [insert citation]. An analysis of the various GOFs can be found in [insert citation], whose result can be further detailed, in the validation phase (see below), with additional indicators such as those presented, for example, in Addor et al., 2017. Another method of analysis, post-hoc of the goodness of the simulations, much more refined, is that presented in [insert Shima work citation]. The latter can also serve as a Bias corrector of the final result and it is going to be systematically applied to the results of the Po project.

From an algorithmic point of view, the calibration carried out in the project is based on the LUCA model [insert citation], which is a sophisticated implementation of SCEM-UA [insert citation], but a particle swarm [insert citation] could also be used. The calibration procedure follows some standards. Having a set of data to base the calibration on, the data are usually divided into two subsets, one used for calibration and another for the so-called validation phase. In the former, the problem of having available input and output data is solved, determining the parameters (or models) in a way similar to what is done in normal ML techniques (which, for this purpose, could probably be used profitably). In the latter, the performance of the model solution on data not used for parameter determination (and should be "independent" of the former) is evaluated. As already mentioned, in the validation phase, additional GOF indicators can be used to better discern the performance of the adopted solution.

A note concerns the word "validation". This is the term used but does not imply any ontological meaning about the nature of the truth described by the model, but only a practical meaning related to the reliability of the model in predicting a certain sequence of numbers.
The calibration/validation procedure can be implemented for a single variable, in the specific case, usually the flow in a section of the hydrographic network, or for more variables, for example, snow cover, soil water content, evapotranspiration, if these measurements are available. These latter possible measures, however, have a different character from the discharge as, while discharge is an aggregate variable, resulting from the concentration of the fallen water on the watershed area in a single point, the others remain variables distributed spatially, before being aggregated for the purposes of the watersheds budget, and therefore the methods of determining the goodness of reproduction of the measured data follow more articulated paths, if not more complex. The good thing is that GEOframe allows you to calibrate the various quantities separately, as each of them is modeled by "different components" that can be used separately from the overall model. The use case is performed throufh quite a lot of manual intervention so far and could be made more automatic.

In any case, if the target variables are more than one, we speak of multi-objective calibration, while if there are variables measured at multiple sites, we speak of multi-site calibration [insert citation].

I would like further to suggest an enhancement to our analysis and move from the daily to hourly time scale. This is particularly crucial for understanding processes within smaller watersheds, approximately on a 1km^2 scale, where many significant phenomena demonstrate sub-daily dynamics.


Simulation/ Analysis/ECP

The validation phase is already a simulation stage (with predetermined parameters) and represents the normal completion of operations in a production phase. This production phase is usually understood in the hydrological literature as hindcasting, that is, as functional to the understanding of past events for which an explanation is sought in a quantitative framework. This involves the use of more accurate analysis and indicators than those used in the calibration/validation phase which require a certain speed. One of these is the analysis through empirical conditional distributions, as illustrated in Azimi et al., 2023. These analyses can eventually lead to a rethinking of the setup and calibration/validation phases in order to obtain more accurate results. As shown in Azimi et al (2023, 2024), ECPs can also be used as bias correctors and improve the overall statistical performance of the model's results, at least if it shows a certain stationarity of temporal behavior, that is, if, for example, the effects attributable to global warming do not significantly impact the structure of the model (including its parameters). The determination of the "reliability" of the models is then a key concept in the development of digital twins of the hydrological system (Rigon et al, 2022).

Another matter, and much less frequented by hydrologists, is that of forecasting future events. These future events, obviously, have to do with the time series input to hydrological models and therefore require forecasts of precipitation, temperature, wind speed, and air humidity. It is known that the meteorological system (global and local) is affected by a lack of predictability (predictability) due to deterministic chaos effects [insert citation]. To date, weather predictions have reliability, with respect to weather categories, of a few days, they have the ability to predict atmospheric temperatures, but they are still very imprecise in determining the amount of precipitation, in essence, they can be used to predict the hydrological future but with questionable quantitative value. The theoretical reason for this debacle has been somewhat said, but there are also others, for example, the heterogeneity of ground conditions and the absence of a description of the soil-atmosphere feedbacks, both conditions not described in meteorological models. Hydrological forecasts can therefore only be of a statistical nature and produce scenarios [insert citation], which are not devoid of meaning and practical value. In this area between Hydrology and meteorology the search for a common ground is mandatory for any evolution. In GEOframe, however, the input data treatment/modelling is quite well separated from the hydrological computation and any new source of data can be easily (but not without person/months work) included.

Distribution of results and participatory science

A fundamental aspect, already widely discussed in Rigon et al., 2022, is to understand how the results of a model can be shared with various users, but also how the model, its setup (including a very expensive phase of DEM analysis, weather data interpolation, and calibration/validation) can be shared, saving other researchers time. GEOframe is built in such a way that this is possible (share ability is by design of the informatics) and some experiences have already been made in this sense. Some within the Trento working group, others with external research groups from the University of Milan (whose work is to be incorporated) and the Polytechnic of Turin, where the basic data and models already pre-digested by the University of Trento served for further developments and analysis on some parts of the Po basin already processed.
The question on how to preserve, make use of multiple contributions to code, data, simulation configurations and simulations, is still open though.
It should be clarified that the GEOframe system is not only a set of data and models, but also a library of analysis tools, especially developed through Python Notebooks and often documented through a series of slides and video lessons [add the links here] and Schools [https://abouthydrology.blogspot.com/2021/10/the-geoframe-schools-index.html]. Although this system can be improved and automated, it has allowed the group from the Polytechnic of Turin to dramatically shorten the modeling times of a series of basins in Piedmont and will allow, for the moment in the planning stage, the sharing of the setup and analysis of the Lombard area of the large Alpine lakes. Other analyses, developed in parallel on areas such as Friuli by the University of Udine, can easily be inserted into a possible national system that covers all of Italy, even though they were developed separately.
From the informatics point of view organizing all of this information through appropriate repositories would be mandatory in the future for an effcient use of the resources.

Conclusions

The GEOframe-Po project is more than just a collection of models; it envisions a comprehensive system that encompasses a variety of input and output datasets, model configurations, and the flexibility to operate on diverse platforms such as laptops, servers, and the cloud (leveraging the OMS/CSIP platform). The interfaces, as evidenced by the available self-instruction materials, can range from simple text-based designs to more sophisticated visual tools, including augmented reality devices.
The system is designed for continuous improvement and customization, with the ability to implement changes with minimal overhead. This was a strategic requirement pursued at various levels of the information technology aspect of the project [insert citations]. The current models can be broadly categorized as physically based, with the majority of the implementation comprising what is referred to in literature as "lumped" models. However, the system is designed to accommodate extensions to more distributed models, a possibility that has already been partially realized in some research lines of the Trento group.
The integration of machine learning techniques into the system is also possible [insert citation], even though they have not been utilized to date. The design of the GEOframe-Po project, therefore, represents a flexible, adaptable, and forward-thinking approach to modeling and data analysis.

Saturday, September 30, 2023

Constraints to transpiration in a simple (but not too simple) model of transpiration

In our collaborative work with Concetta D'Amato  for the WATERSTEM project, we encountered the initial constraint of transpiration imposed by the hydraulic conductance of the stem-root system. Through our research, inspired by Manzoni et al. [2013], we discovered that the sigmoidal form of conductivity leads to an optimum for transpiration. We attempted to reproduce this phenomenon using the data provided by Kroeber et al. [2-13]. After considerable effort, we successfully generated the gray curve in the Figure, which exhibits a peak just before -4 MPa and enables too high transpiration.

However, we realized that the soil resistance was missing from our analysis. To address this, we incorporated the conductivity of a Silt Loam soil using the van Genuchten Mualem parameterization. The resulting brownish curves serve as evidence that the soil plays a crucial role, as anticipated by Carminati and Javaux [2020]. It is important to note that these curves depict the limits imposed by the soil and stem, which determine the potential sapflow rates, but do not reflect the constraints imposed by plant physiology. To account for plant physiology, we introduced the stomatal resistance, represented by the three dashed curves under different working hypotheses whose parameterization was taken from Daly et al. [2004]. The red points in the Figure represent the plant's working points (although the coupling with the atmospheric boundary layer is not depicted). One notable aspect of the Figure is that at typical soil suctions, the sapflow curves appear relatively flat, and the working points result in relatively constant sapflow despite variations in xylem/leaves pressure. The complete story will soon be available in Concetta's Ph.D. thesis, and the detailed process of creating the Figure can be found in its supplemental material notebooks.

References

Carminati, Andrea, and Mathieu Javaux. 2020. “Soil Rather Than Xylem Vulnerability Controls Stomatal Response to Drought.” Trends in Plant Science 25 (9): 868–80. https://doi.org/10.1016/j.tplants.2020.04.003.

Daly, Edoardo, Amilcare Porporato, and Ignacio Rodriguez-Iturbe. 2004. “Coupled Dynamics of Photosynthesis, Transpiration, and Soil Water Balance. Part I: Upscaling from Hourly to Daily Level.” Journal of Hydrometeorology 5 (3): 546–58. https://doi.org/10.1175/1525-7541(2004)005<0546:cdopta>2.0.co;2.

Kröber, Wenzel, Shouren Zhang, Merten Ehmig, and Helge Bruelheide. 2014. “Linking Xylem Hydraulic Conductivity and Vulnerability to the Leaf Economics Spectrum—A Cross-Species Study of 39 Evergreen and Deciduous Broadleaved Subtropical Tree Species.” PloS One 9 (11): e109211. https://doi.org/10.1371/journal.pone.0109211.

Manzoni, Stefano, Giulia Vico, Gabriel Katul, Sari Palmroth, Robert B. Jackson, and Amilcare Porporato. 2013. “Hydraulic Limits on Maximum Plant Transpiration and the Emergence of the Safety-Efficiency Trade-Off.” The New Phytologist 198 (1): 169–78. https://doi.org/10.1111/nph.12126.

Wednesday, September 6, 2023

A Fermi's like estimation of water fluxes in a plant (to check some consistencies)

 A Fermi's problem is an order-of-magnitude problem (or order-of-magnitude estimate, order estimation), is an estimation problem designed to teach dimensional analysis or approximation (in this case approximation) of extreme scientific calculations, and such a problem is usually a back-of-the-envelope calculation (cit. Wikipedia)


Let's assume that a plant transpires 1 cm per day (just to exaggerate) per unit of area. Suppose this plant canopy covers an area of 100 m^2. The transpired volume in one day is ET = 0.01 *  100 = 1 m^3 (which is a lot, plants are reported to transpirate "hundred of liters", not cubic meters).

Now let's consider the specific hydraulic conductivity KS in Kg m^{-1} s^{-1} MPa^{-1}. According to Krober et al. (2014) and their database, the maximum hydraulic conductivity of Castanea Henryi is approximately (simplifying the numbers) 10 Kg m^{-1} s^{-1} MPa^{-1}. Skipping some details, the maximum sap flow, E_S, derived from this is of the same order of magnitude, expressed in Kg m^{-1} s^{-1} (hint: you need to calculate K(\psi) \psi, with K varying with psi, and psi being the pressure (in MPa) in the xylem, as in Manzoni et al., 2014).

To compare E_S and ET, I need to multiply E_S by the active trunk cross-sectional area CSA (according to Thurner) and divide it by the plant height (10 m) to account for the gradient. Then, I need to convert from Kg per second to Kg per day (multiplying by 10^5) and divide by the density of water to obtain the result in terms of volume (10^3 kg/m^3). Therefore:

E_S = 10 [ES value] * 10^5 [Seconds in a Day] * CSA [Cross-sectional Area] / 10^4 [Plant Height * Water Density] = 100 CSA

From ES = ET, it follows that:

CSA = 0.01 m^2

which could not  be an unreasonable value (plant physiologists have to tell me). If the density measurement made by Kroeber et al. is actually related to the entire branch/trunk they used, it could mean that in a 1 m^2 stem (if the stem were 1 m^2), 1% contributes to the xylem flow. Unless I have forgotten any factor somewhere (which would be embarrassing, but I'll take the risk) or the measurements made by Kroeber et al. need to be adjusted differently.

According to Lüttschwager's study, this value would imply a much higher specific hydraulic conductivity than the KS observed in the outermost regions of the trunk where the flow is concentrated. Another consequence is that the less conductive species of this Chinese chestnut (38 out of 39 in the study) could only sustain such evaporation demands with much larger stems, which seems unreasonable, or a large percentage of vessels.

I would like to ask if the numbers I presented seem correct and reasonable to you, and if there is anything blatantly wrong in my reasoning or deduction from Kroeber's work (for those familiar with it) or elsewhere. Any comments are welcome.

P.S. - Most species in Kroeber's study have a KS that is 10 times smaller, which would require a CSA 10 times larger for the same evaporative demand.

References

Manzoni, Stefano, Giulia Vico, Gabriel Katul, Sari Palmroth, Robert B. Jackson, and Amilcare Porporato. 2013. “Hydraulic Limits on Maximum Plant Transpiration and the Emergence of the Safety-Efficiency Trade-Off.” The New Phytologist 198 (1): 169–78. https://doi.org/10.1111/nph.12126.

Kröber, Wenzel, Shouren Zhang, Merten Ehmig, and Helge Bruelheide. 2014. “Linking Xylem Hydraulic Conductivity and Vulnerability to the Leaf Economics Spectrum—A Cross-Species Study of 39 Evergreen and Deciduous Broadleaved Subtropical Tree Species.” PloS One 9 (11): e109211. https://doi.org/10.1371/journal.pone.0109211.

Lüttschwager, Dietmar, and Rainer Remus. 2007. “Radial Distribution of Sap Flux Density in Trunks of a Mature Beech Stand.” Annals of Forest Science 64 (4): 431–38. https://doi.org/10.1051/forest:2007020.

Thurner, Martin, Christian Beer, Thomas Crowther, Daniel Falster, Stefano Manzoni, Anatoly Prokushkin, and Ernst-Detlef Schulze. 2019. “Sapwood Biomass Carbon in Northern Boreal and Temperate Forests.” Global Ecology and Biogeography: A Journal of Macroecology 28 (5): 640–60. https://doi.org/10.1111/geb.12883.

Thursday, August 31, 2023

Some papers that discuss tree allometry to obtain biomass and sapwood cross sectional area

In order to accurately determine the water budget of trees (see also yesterday's post), it is crucial to establish a connection between the quantity of sapwood and the transpiration rate from the leaves. One essential factor in this process is obtaining accurate measurements of the sapwood cross-sectional areas (CSA). However, it is important to note that these CSA measurements can vary significantly from one plant to another. Acquiring this data can be challenging, and as a result, researchers have conducted studies aiming to establish allometric relationships as a means to estimate these measurements. To assist me in finding relevant literature on this topic, I reached out to my colleague involved in the WATERSTEM project. Below, you will find the literature they recommended.


References

Berry, Z. Carter, Nathaniel Looker, Friso Holwerda, León Rodrigo Gómez Aguilar, Perla Ortiz Colin, Teresa González Martínez, and Heidi Asbjornsen. 2018. “Why Size Matters: The Interactive Influences of Tree Diameter Distribution and Sap Flow Parameters on Upscaled Transpiration.” Tree Physiology 38 (2): 263–75. https://doi.org/10.1093/treephys/tpx124.

Kubota, Mitsumasa, John Tenhunen, Reiner Zimmermann, Markus Schmidt, Samuel Adiku, and Yoshitaka Kakubari. n.d. “Influences of Environmental Factors on the Radial Profile of Sap Flux Density in Fagus Crenata Growing at Different Elevations in the Naeba.” https://academic.oup.com/treephys/article/25/5/545/1712832.

Lüttschwager, Dietmar, and Hubert Jochheim. 2020. “Drought Primarily Reduces Canopy Transpiration of Exposed Beech Trees and Decreases the Share of Water Uptake from Deeper Soil Layers.” Forests, Trees and Livelihoods 11 (5): 537. https://doi.org/10.3390/f11050537.

Lüttschwager, Dietmar, and Rainer Remus. 2007. “Radial Distribution of Sap Flux Density in Trunks of a Mature Beech Stand.” Annals of Forest Science 64 (4): 431–38. https://doi.org/10.1051/forest:2007020.

Niccoli, Francesco, Arturo Pacheco-Solana, Sylvain Delzon, Jerzy Piotr Kabala, Shahla Asgharinia, Simona Castaldi, Riccardo Valentini, and Giovanna Battipaglia. 2023. “Effects of Wildfire on Growth, Transpiration and Hydraulic Properties of Pinus Pinaster Aiton Forest.” Dendrochronologia 79 (126086): 126086. https://doi.org/10.1016/j.dendro.2023.126086.

Petrík, Peter, Ina Zavadilová, Ladislav Šigut, Natalia Kowalska, Anja Petek-Petrik, Justyna Szatniewska, Georg Jocher, and Marian Pavelka. 2022. “Impact of Environmental Conditions and Seasonality on Ecosystem Transpiration and Evapotranspiration Partitioning (T/ET Ratio) of Pure European Beech Forest.” WATER 14 (19): 3015. https://doi.org/10.3390/w14193015.

Thurner, Martin, Christian Beer, Thomas Crowther, Daniel Falster, Stefano Manzoni, Anatoly Prokushkin, and Ernst-Detlef Schulze. 2019. “Sapwood Biomass Carbon in Northern Boreal and Temperate Forests.” Global Ecology and Biogeography: A Journal of Macroecology 28 (5): 640–60. https://doi.org/10.1111/geb.12883.

Wednesday, August 30, 2023

A Rosetta stone for connecting the various forms of the Darcy-Buckingham law use in Hydrology and Plants Physiology

The information presented here is derived from the study conducted by Carminati and Javaux in 2020, which aimed to provide insights into plant hydraulics. Carminati referred to the work of Kroeber et al. in 2014, who conducted extensive measurements on a variety of plants and reported their data. However, a discrepancy arises between hydrologists and plant physiologists in the units used to measure hydraulic conductivity. While hydrologists measure it in meters per second (m/s), plant physiologists measure it in kilograms per meter per Pascal second [Kg m/(Pa s)].


In their study, Kroeber et al. reported conductivity per unit area, denoted as Kk, measured in kilograms per meter per Pascal second [Kg/(m Pa s)]. This unit might seem unfamiliar or obscure. To bridge the gap between my background and the new papers, Carminati and Javaux provide a clue. They suggest that the relationship between Kk and the commonly used hydraulic conductivity, K_w, expressed in centimeters per day (cm/day), can be established using the enigmatic equation K_w = g * 100 * 10^(-6) * 3600 * 24 * Kk. Now, the question arises: Is 'g' referring to the acceleration due to gravity?

So I dedicated a couple of days of my life to build a Rosetta Stone to translate the units and check the coherence of what done. The result is a short paper by me and Concetta D'Amato that you  can find here. 

For obtaining this I had to walk through the valley of the water potentials expressed in different units, but also this can be interesting for the reader.  

Next step is understand which is the value of the cross section through which the water flow to obtain, at the end, real cubic meter per second or kg per second. 


References

Carminati, Andrea, and Mathieu Javaux. 2020. “Soil Rather Than Xylem Vulnerability Controls Stomatal Response to Drought.” Trends in Plant Science 25 (9): 868–80. https://doi.org/10.1016/j.tplants.2020.04.003.

Kröber, Wenzel, Shouren Zhang, Merten Ehmig, and Helge Bruelheide. 2014. “Linking Xylem Hydraulic Conductivity and Vulnerability to the Leaf Economics Spectrum—A Cross-Species Study of 39 Evergreen and Deciduous Broadleaved Subtropical Tree Species.” PloS One 9 (11): e109211. https://doi.org/10.1371/journal.pone.0109211.

Monday, July 31, 2023

Some observations about long rainfall and the generated discharges

 In well-known hydrologic response theories like the IUH, it has been established that for a specific catchment and a constant rainfall, there exists a 'critical rainfall duration' resulting in the maximum discharge for that catchment, which is usually known as concentration time. 

The next step is to associate a return period with the constant rainfall. This allows us to demonstrate that given a precipitation with an assigned return period, there is a critical rainfall duration that yields the highest possible discharge in that river section.This is what has been accomplished in Rigon et al., 2011 (but the research dates back to early 00, which is another interesting story). BTW, In the paper, we have also shown that this time is less or equal to the concentration time. 


The above argument may lead to the misconception that the “maximum discharge” for the catchment cannot be exceeded (keep in mind that the concept of maximum discharge obtainable is incomplete when you do not mention a return period).  Consider doubling the duration of the rainfall while keeping the intensity fixed. The first impulse results in the highest discharge with the assigned return period. Yet, it also has a discharge tail that, depending on the catchment's features, can last quite long. When the second impulse of precipitation arrives with the same intensity, it adds to the recession of the first impulse, usually increasing the discharge beyond the maximum discharge obtained with a single impulse.

In certain cases, like in the kinematic hydrograph model (uniform IUH) the rise of the new impulse discharge may precisely compensate for the decreasing recession of the older impulse, resulting in a constant discharge. However, this is not the general scenario, as simple calculations can show and sticking with this idea can be erroneous. Typically in fact, and especially when there is a marked contrast between the response time of the surface and subsurface storm flow waves, the recession discharge generated of the first impulse decreases more slowly than the increase in the new impulse discharge, effectively acting as additional rainfall. This effect is equivalent to increase the intensity of the effective rainfall to a return period which can be estimated through inverse modelling. In other words, two subsequent rainfall impulses, each with an assigned return period, are equivalent to a precipitation event with a higher return period. While the IUH theory establishes a precise equality between the return period of rainfall and discharge for a single impulse, the two return periods of discharges and rainfall become decoupled when multiple rainfall impulses occur.  

Although real-world precipitations are not constant and uniform, and the response of the catchment may not be time-invariant,  the main qualitative findings described above remain statistically valid and could be tested by generating ensembles of time-variable precipitations with numerical models. Besides, there are additional factors like sediment and vegetation transport that can add volume to the water (see for instance these posts),  increasing more than linearly the return period of discharge with increasing rainfall intensities. 


References 

Rigon, R., P. D’Odorico, and G. Bertoldi. 2011. “The Geomorphic Structure of the Runoff Peak.” Hydrology and Earth System Sciences 15 (6): 1853–63. https://doi.org/10.5194/hess-15-1853-2011.

Tuesday, July 4, 2023

C3A Six Years Plan

C3A is the Center for Agriculture (Agricoltura), Food (Alimenti), Environment (Ambiente) of the University of Trento (UniTrento).  As you can see in the brief history you can find in the document below, it was established to increase the involvement in the high education and research of the Province of Trento in Agrifood (and environmental field) together with the Edmund Mach Foundation (FEM) six years ago. 
The collaboration was actually not easy but at the same time fruitful and had a change in the recent years that were brought to a new agreement between the FEM and UniTrento. This agreement was the basis for the new six-years plan of the Center (due according to the regulations of the University of Trento) which you can find below. It design the research and educational activities for the next 6 years. 





The plan can be found by clicking on the above Figure. Here you can also find the slides I presented to the board of the University for presenting the Center and the plans.