| gWMethodologiesID | euRBDCode | diminutionDamage | methodCriterionExtentExceedance | proportionExceedanceAllowed | impactsGWAbstractionBalance | impactsGWAbstractionSWObjective | impactsGWAbstractionSWDiminutionStatus | impactsGWAbstractionDamageGWDE | impactsGWAbstractionSalineIntrusion | availableGroundwaterResource | needsTerrestrialEcosystems | balanceRechargeAbstraction | trendAssessmentPerformed | trendAssessmentMethodology | timeSeries | statisticalElements | additionalTrendAssessment | startingPointTrendReversal | percentageStartingPoint | trendReversalMethodology | thresholdValueElementProtectionEcosystem | thresholdValueElementProtectionGWDE | thresholdValueElementProtectionUses | thresholdValueElementSalineIntrusion | thresholdValuesBackgroundLevels | transboundaryGWBPresent | transboundaryThresholdValues |
| 1 | ITC | Yes | Method 1: Proportion (%) of the number of monitoring sites exceeding a groundwater quality standard or threshold value compared to the total number of monitoring sites in the whole groundwater body | 20.0 | Yes | Yes | Yes | Yes | Yes | Yes | Not applicable | Method 2: A comparison of annual average groundwater abstractions against 'available groundwater resource' in the groundwater body has been reported to be calculated for a subset of all groundwater bodies | Yes | Yes | 2010--2015 | Statistical significance | No | Starting points for trend reversal have not been established. | 0 | No | Yes | Yes | Yes | Yes | Background levels are considered in a different way | No | |
