Groundwater methodologies#

Purpose and overview#

This section:

  • revises the information related to Groundwater methodologies in the 2nd and 3rd cycle of reporting of the Water Framework Directive River Basin Management Plans

  • presents a simplified proposal for the electronic reporting in the 4th cycle as a separate dataset within the Groundwater dataflow, to allow the cross-check between the methodologies data and the data reported at water body level

GWMET_2022 schema - 3rd cycle#

The GWMET_2022 schema defined the required data about about the groundwater methodologies (Figure 48).

../_images/ClassDiagram_GWMET_2022.png

Figure 48 GWMET_2022 Schema - 3rd cycle#

The GWMET_2022 schema was already partially revised (see Current structure - 3rd cycle). Specifically, the GWExemptions data (Figure 92) is no longer requested in the 4th cycle.

Figure 49 shows a simplified diagram to help focus the discussion on the remaining issues.

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classDiagram

class GWMethodologies {
  + gwCharacterisationReference: ReferenceType [1..*]
  + diminutionDamage: YesNoNotApplicable_Union_Enum
  + methodCriterionExtentExceedance: MethodCriterionExtentExceedance_Enum
  + proportionExceedanceAllowed: NumberDecimal0100Type [0..1]
  + impactsGWAbstractionBalance: YesNoCode_Enum
  + impactsGWAbstractionSWObjective: YesNoCode_Enum
  + impactsGWAbstractionSWDiminutionStatus: YesNoCode_Enum
  + impactsGWAbstractionDamageGWDE: YesNoCode_Enum
  + impactsGWAbstractionSalineIntrusion: YesNoCode_Enum
  + availableGroundwaterResource: YesNoPartially_Union_Enum
  + needsTerritorialEcosystems: YesNoNotApplicable_Union_Enum
  + balanceRechargeAbstraction: BalanceRechargeAbstraction_Enum
  + trendAssessmentPerformed: YesNoCode_Enum
  + trendAssessmentMethodology: YesNoCode_Enum [0..1]
  + timeSeries: YearRangeType [0..1]
  + statisticalElements: StatisticalElements_Enum [0..1]
  + additionalTrendAssessment: YesNoCode_Enum
  + trendReversalMethodology: YesNoCode_Enum
  + thresholdValueElementProtectionEcosystem: YesNoCode_Enum
  + thresholdValueElementProtectionGWDE: YesNoCode_Enum
  + thresholdValueElementProtectionUses: YesNoCode_Enum
  + thresholdValueElementSalineIntrusion: YesNoCode_Enum
  + thresholdValueBackgroundLevels: ThresholdValueBackgroundLevels_Enum
  + transboundaryGWBPresent: YesNoCode_Enum
  + transboundaryThresholdValues: YesNoCode_Enum
  + gwMethodologiesChemicalStatusClassificationReference: ReferenceType [1..*]
  + gwMethodologiesQuantitativeClassificationReference: ReferenceType [1..*]
  + gwMethodologiesTransboundaryReference: ReferenceType [0..*]
}

class GWPressures{
  + gwPressuresNotAssessed: SignificantPressureType_Enum [1..*]
  + gwSignificantPressurePointSourceTools: SignificantPressureTools_Enum
  + gwSignificantPressureDiffuseSourceTools: SignificantPressureTools_Enum
  + gwSignificantPressureWaterAbstractionTools: SignificantPressureTools_Enum
  + gwSignificantPressureArtificialRecharge: SignificantPressureTools_Enum
  + gwSignificantPressureOtherSourceTools: SignificantPressureTools_Enum
  + gwSignificanceDefinition: YesNoCode_Enum
  + gwSignificanceLinkFailure: YesNoCode_Enum
  + gwPressuresReference: ReferenceType [1..*]
}


class ThresholdValue{
  + pollutantIndicatorCode: ChemicalSubstances_Union_Enum
  + pollutantIndicatorCodeOther: OtherType [0..1]
  + thresholdValueRange: ThresholdType [0..1]
  + thresholdValueUnit: UnitOfMeasure_Enum
  + thresholdValueDerivedFromCV: YesNoCode_Enum
  + cvDrinkingWaterValueRange: ThresholdType [0..1]
  + cvDrinkingWaterValueUnit: UnitOfMeasure_Enum [0..1]
  + cvIrrigationValueRange: ThresholdType [0..1]
  + cvIrrigationValueUnit: UnitOfMeasure_Enum [0..1]
  + cvIndustryValueRange: ThresholdType [0..1]
  + cvIndustryValueUnit: UnitOfMeasure_Enum [0..1]
  + cvOtherValueRange: ThresholdType [0..1]
  + cvOtherValueUnit: UnitOfMeasure_Enum [0..1]
  + thresholdValueScale: GeographicalScale_Enum
  + startingPointTrendReversal: ThresholdType
}


class GWMET {
  + countryCode: CountryCode_Enum
  + euRBDCode: FeatureUniqueEUCodeType
}

GWMethodologies <-- GWMET : 1..1
GWPressures <-- GWMET : 1..1
ThresholdValue <-- GWMET : *..0
    

Figure 49 Class diagram for the GWMET_2022 schema in the 3rd cycle.#

The Commission has revised and simplified the GWMethodologies class, keeping only a subset of the elements requested in the 3rd cycle. The following elements were removed:

  • GWMET/GWMethodologies/diminutionDamage

  • GWMET/GWMethodologies/methodCriterionExtentExceedance

  • GWMET/GWMethodologies/proportionExceedanceAllowed

  • GWMET/GWMethodologies/impactsGWAbstractionBalance

  • GWMET/GWMethodologies/impactsGWAbstractionSWObjective

  • GWMET/GWMethodologies/impactsGWAbstractionSWDiminutionStatus

  • GWMET/GWMethodologies/impactsGWAbstractionDamageGWDE

  • GWMET/GWMethodologies/impactsGWAbstractionSalineIntrusion

  • GWMET/GWMethodologies/availableGroundwaterResource

  • GWMET/GWMethodologies/needsTerritorialEcosystems

  • GWMET/GWMethodologies/balanceRechargeAbstraction

  • GWMET/GWMethodologies/gwMethodologiesChemicalStatusClassificationReference

  • GWMET/GWMethodologies/gwMethodologiesQuantitativeClassificationReference

  • GWMET/GWMethodologies/gwMethodologiesTransboundaryReference

  • GWMET/GWMethodologies/transboundaryGWBPresent

  • GWMET/GWMethodologies/trendAssessmentMethodology

The following elements were moved or revised:

  • GWMET/GWMethodologies/trendAssessmentStatisticalElements

  • GWMET/GWMethodologies/thresholdValueBackgroundLevels

The Commission has revised and simplified the ThresholdValue class, keeping only a subset of the elements requested in the 3rd cycle. The following elements were removed:

  • GWMET/ThresholdValue/pollutantIndicatorCodeOther

  • GWMET/ThresholdValue/thresholdValueDerivedFromCV

  • GWMET/ThresholdValue/cvDrinkingWaterValueRange

  • GWMET/ThresholdValue/cvDrinkingWaterValueUnit

  • GWMET/ThresholdValue/cvIrrigationValueRange

  • GWMET/ThresholdValue/cvIrrigationValueUnit

  • GWMET/ThresholdValue/cvIndustryValueRange

  • GWMET/ThresholdValue/cvIndustryValueUnit

  • GWMET/ThresholdValue/cvOtherValueRange

  • GWMET/ThresholdValue/cvOtherValueUnit

  • GWMET/ThresholdValue/thresholdValueScale

The Commission has revised GWPressures class. The following elements were removed:

  • GWMET/GWPressures/gwSignificantPressureOtherSourceTools

  • GWMET/GWPressures/gwPressuresNotAssessed

  • GWMET/GWPressures/gwPressuresReference

The structure of the GWPressures class was also revised.

Methodologies dataset - 4th cycle#

This section shows the proposed structure for the groundwater methodologies reporting.

GWMethodologies table#

The GWMethodologies table has a structure similar to the corresponding class in the 3rd cycle reporting, minus the attributes removed by the Commission’s review (see Figure 50).

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classDiagram

class GWMethodologies {
  + euRBDCode: wiseIdentifier
  + gwCharacterisationReference: referenceCode
  + trendAssessmentPerformed: YesNo
  + trendAssessmentTimeSeries: range [0..1]
  + trendAssessmentStatisticalMethod: TrendStatisticalMethod [0..1]
  + additionalTrendAssessment: YesNo
  + trendReversalMethodology: YesNo
  + thresholdValueElementProtectionEcosystem: YesNo
  + transboundaryThresholdValues: YesNoNotApplicable
  + thresholdValueElementProtectionGWDE: YesNo
  + thresholdValueElementProtectionUses: YesNo
  + thresholdValueElementSalineIntrusion: YesNo
}

class TrendStatisticalMethod{
  <<enumeration>>
  statisticalSignificanceTrendDetection
  confidenceIntervalTrendMagnitude
  none
}

GWMethodologies .. TrendStatisticalMethod 

classDef default fill:white,stroke:#000;
classDef otherDataset fill:lightyellow,stroke:#000;
classDef forFixing fill:white,stroke:#f00;

    

Figure 50 Groundwater methodologies - GWMethodologies table - 4th cycle#

GWPressureAssessment table#

The GWPressureAssessment table has a modified structure (see Figure 51):

  • the reporting of “pressures not assessed” is eliminated, because the data was difficult to analyse and contained inconsistencies

  • instead, for each pressure (or group of pressures), three attributes are requested (gwPressureAssessmentMethod,gwSignificanceDefinition,gwSignificanceLinkFailure)

  • given that the pressure codelist is hierarchical, the granularity of the reporting is selected by Member States

  • the quality control procedure will verify that different levels are not selected simultaneously for any given RBD

For more information see PressureType codelist - 4th cycle.

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class GWPressureAssessment{
  + euRBDCode: wiseIdentifier
  + gwPressure: PressureType
  + gwPressureAssessmentMethod: PressureAssessmentMethod
  + gwSignificanceDefinition: YesNoNotApplicable
  + gwSignificanceLinkFailure: YesNoNotApplicable
}

class PressureAssessmentMethod{
<<enumeration>>
  numericalTools
  expertJudgement
  combinationOfBoth
  notAssessed 
}

GWPressureAssessment ..> PressureAssessmentMethod 

classDef default fill:white,stroke:#000;
classDef otherDataset fill:lightyellow,stroke:#000;
classDef forFixing fill:white,stroke:#f00;

    

Figure 51 Groundwater methodologies - GWPressureAssessment table - 4th cycle#

GWThresholdValue table#

The GWThresholdValue table has a structure similar to the corresponding class in the 3rd cycle reporting, minus the attributes removed by the Commission’s review (see Figure 52). Note that:

  • a unique gwThresholdIdentifier was introduced to avoid ambiguity

  • duplicate records will be detected (i.e. records with identical values for all attributes, except the identifier)

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classDiagram
class GWThresholdValue{
  + gwThresholdIdentifier: wiseIdentifier
  + parameterCode: Parameter
  + thresholdValueRange: range
  + thresholdValueUnit: UnitOfMeasure

  + startingPointTrendReversal: range [0..1]
  «reference»
  + gwThresholdReference: referenceCode [0..n]
}

class GWPollutant ["GroundWaterDataset::GWPollutant"]:::otherDataset{
  + euGroundWaterBodyCode
  + gwPollutantCode
  + gwThresholdIdentifier
}

GWThresholdValue <.. GWPollutant: gwThresholdIdentifier

classDef default fill:white,stroke:#000;
classDef otherDataset fill:lavender,stroke:#000;
classDef forFixing fill:white,stroke:#f00;

    

Figure 52 Groundwater methodologies - GWThresholdValue table - 4th cycle#

Codelists - 4th cycle#

  • For the PressureAssessmentMethod codelist, see Table 58.

  • For the TrendStatisticalMethod codelist, see Table 43.

TrendStatisticalMethod codelist
Table 43 Codelist - 4th cycle - TrendStatisticalMethod#

Notation

Label

Definition

statisticalSignificanceTrendDetection

Statistical significance

The existence of a significant trend was assessed using statistical tests.

confidenceIntervalTrendMagnitude

Confidence interval

The existence of a significant trend was assessed using statistical tests, the magnitude of the trend was quantified and the uncertainty was assessed using confidence intervals.

none

None

The trend assessment did not use statistical methods (i.e. expert judgement only)

Annexes - Data analysis - 3rd cycle#

trendAssessmentMethodology#

The WFD2022 guidance document definitions for the trendAssessmentPerformed, trendAssessmentMethodology and statisticalElements elements of the GWMethodologies class are transcribed in Table 44.

Table 44 Definitions for trendAssessmentPerformed, trendAssessmentMethodology and statisticalElements – 3rd cycle.#

Attribute

Guidance

Option

trendAssessmentPerformed

Required.
Indicate whether trend assessment in groundwater pollutants was performed.

‘Yes’
‘No’

trendAssessmentMethodology

Conditional.
If trend assessment in groundwater pollutants was performed, indicate whether a methodology for identifying significant and upward trends in any pollutant’s concentration has been applied.

‘Yes’
‘No’

statisticalElements

Conditional.
If trend assessment in groundwater pollutants was performed, select from the enumeration list which statistical element was used.

‘Statistical significance’
‘Confidence intervals’
‘None’

The reported data for combinations of the three elements is presented in Table 45.

The first four records may be interpreted as:

  • in 95 river basin districts, trends were assessed and a test for statistical significance of an upward trend was used
    (e.g. using a linear regression t-test or a non-parametric Mann-Kendall test)

  • in 36 river basin districts, trends were not assessed

  • in 16 river basin districts, trends were assessed and the magnitude of significant upward trends was quantified using confidence intervals

  • in 2 river basin districts, trends were assessed but no methodology for detecting significant upward trends exists, and no statistical element was used (i.e. only expert judgement was used?)

The last two records are difficult to interpret, and possibly result from reporting mistakes:

  • in 6 river basin districts trends were assessed, a methodology for detecting significant upward trends was applied, but somehow no statistical element was used

  • in 1 river basin districts trends were assessed, a methodology for detecting significant upward trends was not applied, but somehow statistical significance was determined

In conclusion:

  • the trendAssessmentMethodology element appears to be redundant with respect to the statisticalElements element, and may be removed to simplify the reporting and avoid mistakes

  • the meaning of the statisticalElements element should be made clearer to both data provider and end-users, to facilitate the interpretation

Table 45 Reported data for trendAssessmentPerformed, trendAssessmentMethodology and statisticalElements – 3rd cycle.#

trendAssessmentPerformed

trendAssessmentMethodology

statisticalElements

numberOfRBDs

numberOfCountries

Yes

Yes

Statistical significance

95

20

No

«null»

«null»

36

5

Yes

Yes

Confidence intervals

16

6

Yes

No

None

2

1

Yes

Yes

None

6

2

Yes

No

Statistical significance

1

1

References#