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CSPS

A multi-level assessment framework for Aquatic Ecosystem Models (AEMs)

CSPS is a framework for the hierarchical assessment of aquatic ecosystem models built on a range of metrics and characteristic signatures relevant to aquatic ecosystem condition. The framework is comprised of four levels: 0) conceptual validation; 1) comparison of simulated state variables with observations (‘state validation’); 2) comparison of fluxes (process rates) with measured fluxes (‘process validation’); and 3) comparison of system-level emergent properties, patterns and relationships (‘system validation’). Of these, only levels 0 and 1 are routinely undertaken at present. To highlight a diverse range of contexts relevant to the aquatic ecosystem modelling community, we present several case studies of improved validation approaches using the level 0-3 assessment hierarchy. It is our goal that the community–driven adoption of these metrics will lead to more rigorously assessed models, ultimately accelerating advances in model structure and function, and improved confidence in model predictions

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Property being assessed

Description

Validation level

Typical range of data observation frequency

Spatial scale

Assessment technique
(see Table 1)

Comments (e.g. processing requirements)

Example references*

Water balance, waves & circulation

 

Water level

Time-series comparison

1a

minutes-monthly

point;

multiple points

E, R,

V(TS), V(XY)

Direct observation or calculation from logged pressure gauge sensors, or from remote sensing approaches (e.g., satellite altimetry, radar)

 

Missaghi and Hondzo (2010)

 

 

Tidal propagation

2b

minutes-hourly

horizontal transect

V(TX)

Magnitude of attenuation or amplification of tidal range within an estuary or coastal embayment, plotted as a function of distance

 

 

Surface waves

Significant wave height

1a

seconds-minutes

point

V(TS), E, R

For models simulating surface waves the comparison of wave properties can be undertaken

Ji (2017)

 

 

Wave length and period

1b

seconds-minutes

point

V(TS)

 

 

 

Frequency spectra

1c

seconds-minutes

point

FFT, WT

 

Evaporation

Time-series comparison

2a

minutes-daily

point

V(TS), E, R

Evaporative mass flux data can be collected from an evaporation pan, or flux anemometer

Rimmer et al. (2009)

 

 

Time-series comparison

2b

minutes-hourly

point

V(TS), E, R

Comparison against latent heat fluxes derived from energy balance fitting to surface meterological data

Nussboim et al. (2017)

 

 

H2O isotopes

2b

ad hoc

point

V(other)

Fitting isotopic data can help source identification and compute evaporation rates based on deviation of meteoric water line

Stadnyk et al. (2013)

 

Velocity

Time-series comparison

1a

hourly-weekly

point;
horizontal transect

V(TS), E, R V(XZ), MAE(DXZ),

Use of point ADCP measurements for point scale or cross section

 

 

 

Variance ellipse

1c

hourly-weekly

point

V(other)

Summary of magnitude and direction of current field that can be compared with point data

Hetland and DiMarco (2012)

 

 

Residual currents

3

weekly-seasonal

surface layer; horizontal transect

V(XY), V(XZ)

Particle trajectories from model simulations can be compared with tracks from drogues and/or drifters released in the field.

Dissanayake et al. (2019)

 

Mixing

Mixing intensity

2a

ad hoc

vertical profile

V(other)

Turbulent diffusivities derived from SCAMP data can guide turbulence parameterisation

Rueda and MacIntyre (2010)

 

 

Tracer dilution

2b

ad hoc

surface layer; horizontal transect

V(TS)

Capturing the horizontal and vertical dispersion of a conservative tracer (e.g., rhodamine or chloride) can ensure diffusion is being accurately captured

 

 

Retention characteristics

Water age variation

3

ad hoc

multiple sites

E, R

The use of radioisotopes could be used to correlate simulated water age with observed estimates from geochemical tracers

 

 

 

Water source apportionment

3

ad hoc

multiple sites

V(other)

Use of conservative tracers indicating water source from specific surface or groundwater inputs or rainfall, e.g., caffeine, radon, etc.

 

Heat & salt balance

 

Temperature or salinity

Time-series comparison

1a

minutes-monthly

point

V(TS), E, R

Data measured from an in situ thermistor or salinity sensor, or ad hoc measurement

Most papers present this

Frequency spectra

1c

minutes-hourly

point

FFT, WT

Data measured from a thermistor or salinity sensor logging at high frequency

Kara et al. (2012)

Spatial comparison

1a

daily-monthly

surface layer

V(XY),

MAE(DXY), d2

Satellite acquired temp data (e.g., LANDSAT, MODIS etc) compared pixel for pixel with simulation. Model or data may require averaging to ensure spatial resolutions match

Spillman et al. (2007)

Menesguen et al. (2007)

Spatial variability

1c

daily-monthly

surface layer

DF

Compares distribution and range of T or S variation within the simulated domain without conducting pixel by pixel comparison

Spatial patchiness

1c

daily-monthly

surface layer

CCF

Can assess similarity in spatial coherence of T or S

 

 

Eddy structure

3

hourly-monthly

water column

V(XY)

Visual comparison of the emergence of complex eddy structures and gyre formation in T or S fields

Holt et al. (2014)

Temperature

Albedo

2a

ad hoc

surface layer

V(TS), E, R

Models simulating spatiotemporal variability in albedo can validate against estimates computed via upwelling and downwelling pyranometer

 

 

 

Radiative heat flux

2a

ad hoc

surface layer or benthic layer

V(TS), E, R

Radiative heat flux across the surface of the water or at the sediment-water interface measured using eddy-correlation, microprofiles, IR measurements.

 

 

 

Benthic perimeter heat exchange

2b

daily-monthly

water column

V(other)

Rate of change of bottom (hyoplimnion) temperature

Salmon et al. (2017)

Stratification

 

Temperature, salinity, density

Depth comparison

1a

minutes-monthly

vertical profile (continuous) or multiple depths (discrete)

V(TZ), R, d2

MAE(DTZ),

TZ error contour plot highlights errors in thermocline or pycnocline depth, by comparing interpolated observation and model profiles over time

Menesguen et al. (2007)

Missaghi and Hondzo (2010)

Duration of stratification

1b

hourly-seasonal

water column

BIAS, R, SR, DF

Capturing the total length of time a waterbody experiences stratification can be useful for understanding water quality and/or the impacts of climate change

Frassl et al. (2018)

 

 

Date of water column mixing/over turn

1b

hourly-monthly

water column

BIAS, R, SR, DF

Capturing the specific date of water column overturn may be important when forecasting water quality in reservoirs, for example.

 

 

 

Lateral gradient

1b

hourly-daily

horizontal transect

V(XZ), MAE(DXZ)

Comparison on lateral gradient in stratification can be used to diagnose model performance in capturing density currents associated with differential surface forcing or boundary inputs

Woodward et al. (2016)

 

 

Internal wave frequency spectra

1c

minutes-hourly

water column

FFT, WT, WC

Comparison of frequency spectra to demonstrate wave periods and modes are being reporeduced

Hodges et al. (2000)

 

Velocity

Depth comparison

1a

minutes-hourly

vertical profile

V(TZ),

MAE(DTZ)

TZ error contour plot highlights mixing errors, by comparing ADCP data and modelled velocity profiles over time

 

 

Layer structure

Surface mixed-layer depth

1b

daily-monthly

water column

V(TS), E, R

Capturing the mixed layer depth can aid in diagnosing mixing and heat balance problems

Bruce et al. (2018)

Steyn and Oke (1982)

Acreman and Jeffery (2007)

Bayer et al. (2013)

 

 

Metalimnion thickness

1b

daily-monthly

water column

V(TS), E, R

As above, the thickness of the thermocline (or pycnocline) region may assist in validating mixing in lake or ocean models

 

 

 

Bottom vs surface difference

1b

daily-monthly

2 layer

V(TS), E, R, V(TX)

Time-distance contour plot highlights errors in stratification horizontally, e.g., for assessing seasonal salt-wedge propagation in an estuary

Huang et al. (2018)

 

Layer stability

Richardson (Ri) number

1b

daily-monthly

2 layer

V(TS)

The (bulk) Richardson number can be estimated from surface and bottom densities and velocities, to give a quantitative measure of the buoyancy vs inertia forces controlling layer stability

 

Schmidt stability

1b

daily-monthly

water column

V(TS), E, R

As above, the Schmidt stability parameter is useful for diagnosing the strength of lake stratification

Bruce et al. (2018)

Bottom morphometry & sediment transport a

 

Bottom stress

Time-series comparison

1b

minutes-hourly

point

V(TS), E, R

Stress derived from velocity profile measurements can be used to validate model the bottom stress impacting the rate of resuspension

 

 

 

Wave attenuation

2b

ad hoc

multiple points

V(other)

Wave driven resuspension is important in shallow systems and model validation could consider wave attenuation with depth and depending on the character of the benthic substrate

Chen et al. (2007)

Sediment movement

Resuspension rate

2a

ad hoc

point

V(TS), R

In situ experiments measuring resuspension rate can be compared under different hydrodynamic conditions to validate model rates

 

 

Rate of accumulation or erosion of benthic sediments

2b

monthly-decadal

point

V(TS)

For models simulating the change in bottom depth due to sedimentation or erosion, the relative rate of changed in depth measured using hydro-acoustic methods can be used to validate models

 

 

 

Variation in particle size distribution

3

ad hoc

multiple points

V(other)

Spatial differences in particle size composition of bottom sediment can be used to validate areas of differential deposition rates between particle size classes.

 

 

 

Spatial changes in bathymetry

3

seasonal-decadal

bottom layer

V(XY),

MAE(DXY), d2

Can be used to compare model performance capturing spatial patterns in areas of net accumulation and erosion.

 

 

 

Wave length, height in sediment undulations

3

ad hoc

bottom layer

V(XY)

Complex patterns that emerge in fine-scale simulations of hydrodynamics and bottom sediment movement

Sun et al. (2010)

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Repository of Aquatic Ecosystem Modelling (AEM) validation and assessment metrics, using the CSPS framework

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