PEARL is an acronym of Pesticide Emission Assessment at Regional and Local scales. It is a one-dimensional numerical model of pesticide behaviour in the soil-plant system which has been developed by Wageningen University and Research (WUR), the National Institute of Public Health and the Environment (RIVM) and the Netherlands Environmental Assessment Agency (PBL) in close co-operation.
The PEARL development team consists of (in alphabetical order):
Aaldrik Tiktak (PBL)
Daniel van Kraalingen (WUR)
Erik van den Berg (WUR)
Jos Boesten (WUR)
Marius Heinen (WUR)
Joop Kroes (WUR).
PEARL web site: http://www.pearl.pesticidemodels.eu/
Short Model Description
Summary of process descriptions
Water flow in soil is described by Richard’s equation including a range of possible lower boundary conditions (for instance groundwater levels that fluctuate in response to the rainfall input). Soil evaporation and plant transpiration is calculated via multiplying a reference evapotranspiration rate with soil and crop factors. For the FOCUS scenarios, crop growth is simulated with a simple growth model that assumes a fixed length of the growing season. In this growth model, both the leaf area index and the rooting depth are a function of the development stage of the crop. Heat flow in soil is described with Fourier’s law. The thermal properties are a function of porosity and water content and are therefore a function of time and soil depth. PEARL is based on: (i) the convection/dispersion equation including diffusion in the gas phase with a temperature dependent Henry coefficient, (ii) a two-site Freundlich sorption model (one equilibrium site and one kinetic site), (iii) a transformation rate that depends on water content, temperature and depth in soil, (iv) a passive plant uptake rate. The model includes formation and behaviour of transformation products and describes also lateral pesticide discharge to drains (but drainage is switched off for the FOCUS scenarios). PEARL does not simulate preferential flow. Volatilisation from the soil surface is calculated assuming a laminar air layer at the soil surface. PEARL uses an explicit finite difference scheme that excludes numerical dispersion (the dispersion length was set to 5 cm).
See also this figure
Short description of the PEARL software package
PEARL does not simulate water flow and soil temperatures, but uses output from the Soil Water Atmosphere (SWAP) model, so the software package for simulation consists of two models: SWAP and PEARL. The simulation of leaching to groundwater with PEARL requires that first the hydrology of the soil system during the simulation period is computed with SWAP. Daily SWAP output is written to a file which is one of the input files needed for PEARL. However, the user only has to specify input to PEARL: the PEARL model itself organises the input for the SWAP model.
The PEARL User Interface was developed as a user-friendly environment for running FOCUS scenarios. The interface is an integrated environment for data storage and data retrieval, model control and viewing of output data as shown in the next figure.
The user interface is linked to a relational database for easy data access. It generates the input files for the PEARL model and calls the model. Summary outputs are transferred back to the PEARL database where they can be accessed. More comprehensive model outputs can be viewed with a separate graphical program, XYWin. The FOCUS input is stored in the database in such a way that all data that should not be changed by the user are locked. The user can generate a FOCUS scenario for a desired crop-location combination with a wizard.
History of PEARL development
PEARL is based on PESTLA (PESTicide Leaching and Accumulation; Boesten & Van der Linden, 1991; Van den Berg and Boesten, 1999) and PESTRAS (PEsticide TRansport Assessment; Tiktak et al., 1994; Freijer et al., 1996), the latter being a modification of PESTLA version 1. PESTLA was based on the numerical model developed by Leistra & Dekkers (1976). The Leistra & Dekkers model was based on (i) Richard’s equation, (ii) the convection/dispersion equation, (iii) linear sorption that was a function of soil depth and (iv) a transformation rate that was a function of temperature and soil moisture. The Leistra & Dekkers model was used in Dutch pesticide registration from 1976 until 1989 after which it was superseded by the PESTLA model that was used from 1989 until 2000. The PESTRAS model was used in Dutch pesticide registration from 1996 until 2000 for volatile compounds. Since 2000 the PEARL model is used in Dutch pesticide registration.
Role and Place in FOCUS scenarios calculation
PEARL is used for assessment of pesticide leaching in the EU evaluation process and input for all nine groundwater scenarios, including all possible crops, has been developed. PEARL calculates the leaching at the FOCUS target depth (default is 1 m), but also allows for evaluation of leaching at greater depths. For the nine scenarios the total depth of the soil system in PEARL is at least 3 m. As PEARL is able to describe fluctuating groundwater tables and can use information on transformation rates in subsoils, effects of these processes can be studied as well.
Current use outside FOCUS
PEARL is used in Dutch pesticide registration for first and higher tier assessments. Higher tier assessments include the interpretation of lysimeter studies for pesticide registration. PEARL is also used for national Dutch assessments of trends in reductions of emissions to groundwater.
For uses outside FOCUS it is recommended to register at the PEARL website.
Excerpt of existing model documentation
- Boesten, J.J.T.I. and A.M.A. van der Linden, 1991. Modeling the influence of sorp-tion and transformation on pesticide leaching and persistence. Journal of Environmental Quality 20: 425-435.
- Boesten, J.J.T.I. & B. Gottesbüren, 2000 Testing PESTLA using two modellers to simulate bentazone and ethoprophos behaviour in a sandy soil. Agric. Water Management 44: 283-305.
- Freijer, J.I., A. Tiktak, S.M. Hassanizadeh and A.M.A. van der Linden, 1996. PESTRAS v3.1.: A one dimensional model for assessing leaching, accumulation and volatilisation of pesticides in soil. RIVM report 715501007, Bilthoven, the Netherlands.
- Leistra, M. and W.A. Dekkers, 1976. Computed leaching of pesticides from soil under field conditions. Water, Air and Soil Pollution 5: 491-500.
- Leistra, M., A.M.A. van der Linden, J.J.T.I.Boesten, A. Tiktak and F. van den Berg, 2000. PEARL model for pesticide behaviour and emissions in soil-plant systems. Description of processes. Alterra report 13, RIVM report 711401009, Alterra, Wageningen, 107 pp.
- Tiktak, A., A.M.A. van der Linden and F.A. Swartjes. 1994. PESTRAS: A one dimensional model for assessing leaching and accumulation of pesticides in soil. RIVM report 715501003, Bilthoven, the Netherlands.
- Tiktak, A., F. van den Berg, J.J.T.I. Boesten, M. Leistra, A.M.A. van der Linden & D. van Kraalingen (2000). Pesticide Emission Assessment at Regional and Local Scales: User Manual of Pearl version 1.1. RIVM Report 711401008, Alterra Report 28, RIVM, Bilthoven, 142 pp.
- Van den Berg, F. and J.J.T.I. Boesten, 1999. Pesticide leaching and Accumulation model (PESTLA) version 3.4. Description and User’s Guide. Technical Document 43, DLO Winand Staring Centre, Wageningen, The Netherlands, 150 pp.
- Van den Berg, F. , J.H. Smelt, J.J.T.I. Boesten & W. Teunissen (1999) Volatilization of methyl isothiocyanate from soil after application of metam-sodium with two techniques. Journal of Environmental Quality 28: 918-928.
- Van Dam, J.C., J. Huygen, J.G. Wesseling, R.A. Feddes, P. Kabat, P.E.V. van Walsum, P. Groenendijk and C.A. Van Diepen, 1997. Theory of SWAP version 2.0. Simulation of water flow, solute transport and plant growth in the Soil-Water-Atmosphere-Plant environment. Technical Document 45, DLO Winand Staring Centre, Wageningen, The Netherlands.
Latest Version : FOCUS_PEARL_5.5.5gw_5.5.1soil
|Package||FOCUSPEARL_5.5.5_September2021.zip (21/September/2021, 1 file, 17 MB) replacing the 09/June/2021 version (see Advice below)|
|Test Results||These can be found in the package zip file|
Users have to install FOCUS_SPIN_3.3 as PEARL v 5.5.5 itself does not store substance properties. This should be done before installing PEARL v 5.5.5. SPIN has to be installed on a local (and not network) drive. The default directory for installing the SPIN application is C:\Program files (x86)\Pesticide Models/SPIN on a 64 bit platform or C:\Program files\Pesticide Models/SPIN on a 32 bit platform. It should be noted that SPIN version 3.3 facilitates the use of both FOCUSSWASH 5.3 and FOCUSPEARL 5.5.5. To avoid problems by modifying the properties of a substance using one application while the other application is running at the same time, only one application at the time can have access to the SPIN database. So the user has to exit from the application that has a connection to the SPIN database before the other application using SPIN can be started.
The scenarios defined in this download package and shell generate tier 1 groundwater outputs that are in accordance with European Commission, 2014. Sanco/13144/2010 version 3, 613pp and Generic Guidance for Tier 1 FOCUS Ground Water Assessments (version 2.3)
The package also delivers Tier-3A PEC soil as defined in EFSA, 2017. EFSA guidance document for predicting environmental concentrations of active substances of plant protection products and transformation products of these active substances in soil. EFSA Journal 2017;15(10):4982, doi: 10.2903/j.efsa.2017.4982, 115 pp. https://www.efsa.europa.eu/en/efsajournal/pub/4982
If you already installed the earlier PEARL download package that was dated 09/June/2021 and it always completed groundwater simulations then it’s possible and appropriate to continue to use that installation. However if you are a user that encountered that for some simulations (i.e. at the Okehampton scenario) SWAP did not complete its hydrology simulation (was reported by users with computers having certain AMD processors), please use the installation package now available dated September 2021. The problem was linked to the compiler version that had been used to generate the executable of the SWAP model in November 2014. Using the more recent compiler version that has been used to generate the executable of the PEARL model, (i.e. the Intel Parallel Studio XE 2019 compiler), no errors occurred when executing runs with the Okehampton scenario on machines with AMD processors.
|Package||FOCUS_PEARL_4.4.4.exe (11/Apr/2011, 1 file, 23 MB)|
|Comments||The scenarios defined in this download package and shell generate tier 1 outputs that are in accordance with Sanco/13144/2010 version 1, 604pp and Generic Guidance for Tier 1 FOCUS Ground Water Assessments (version 2.0)
The installation of Interbase (ensures transfer of data between database and user interface). This is only required on PCs where FOCUS PEARL has not been installed before. InterBase6_5.zip
|Package||FOCUS_PEARL_3.3.3.exe.zip (22/May/2006, 1 file, 30 MB)|
|Test Results||HTML, Word|
|Comments||Release Notes for FOCUS_PEARL_3.3.3 (Word)|
|Package||FOCUS_PEARL_2.2.2.exe.zip (7/Aug/2003, 1 file, 38 MB)|
|Test Results||HTML, Word|
|Comments||Differences between PEARL_2.2.2 and PEARL_1.1.1 (including Known Bugs for PEARL_2.2.2) : HTML or Word
|Package||FOCUS_PEARL_1.1.1.exe.zip (5/Jan/2001, 1 file, 20 MB)|
|Test Results||HTML, Word|
An error has been discovered in the parameters describing water withdrawal by cotton (in the Sevilla and Thiva scenarios). This error results in a simulated transpiration of water by cotton that is far too low. As a consequence, the water percolation and leaching concentrations are overestimated. Problem will be addressed in next release.
Warning (21/October/2003) :