Article 17 web tool

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: The estimate of habitat area is based on an extrapolation method or expert based judgement, using when appropriate the techniques suggested by the ETC. Such methodologies may have a degree of uncertainty that cannot be quantified; for this reason, the values included in the report are to be considered approximate estimates. ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Wartość podana w polu 4.1 (15000km2) jest wyższa niż wartość podana w raporcie z 2013 r. (9991 km2), ale faktyczny zasięg nie uległ znacznej zmianie w porównaniu z poprzednim okresem raportowania. W aktualnym okresie raportowym wartość podana w polu 4.1 została wyliczona przy użyciu dedykowanego narzędzia (Range Tool) przygotowanego przez ETC/BD oraz EEA, w sposób automatyczny na podstawie rozmieszczenia kwadratów, w których występuje siedlisko w regionie biogeograficznym. Przy obliczaniu powierzchni zasięgu siedliska zastosowano „gap distance” wynoszący 40km, a wyliczony przez narzędzie zasięg nie został przycięty do granic Polski. ||
->Coverage: W poprzednim raporcie powierzchnię siedliska oszacowano na podstwie Bazy Invent (obejmującą tereny zarządzane przez PGL LP - ok 80% powierzchni leśnej Polski a w regionie alpejskim ok 75% powierzchni leśnej) i uzupełniono to o szacunek powierzchni siedliska na pozostałych gruntach. Obecnie Bank Danych o Lasach (zawiera zaktualizowane i częściowo zweryfikowane dane zawarte w Bazie Invent) podaje areał siedliska 9110 na poziomie 226 km2. Przyjmujac, że udział siedliska 9110 na terenie innych własności jest taki sam jak na terenie zarządzanym przez PGL LP otrzymujemy w przybliżeniu 290 km2. ||
->HabCondition: Do określenia powierzchni siedliska w dobrym, złym lub nieznanym stanie (pkt. 6.1) wykorzystano rozkład ocen parametru struktura i funkcje na stanowiskach monitoringowych oraz wartość powierzchni siedliska w regionie podaną w pkt. 5.2 c). Przyjęto następujące założenia:
- minimalna powierzchnia siedliska w dobrym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na FV
- maksymalna powierzchnia siedliska w dobrym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na FV i U1
- minimalna powierzchnia siedliska w złym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na U2
- maksymalna powierzchnia siedliska w złym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na U1 i U2
- minimalna i maksymalna powierzchnia siedliska o nieznanym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na XX ||
->Future: N/A ||
->Conclusion: Ocena stanu ochrony została wystawiona w oparciu o dane zebrane z 47 stanowisk monitoringowych.
Parametr struktura i funkcję oraz ocena ogólna w porównaniu do poprzedniego raportu uległa pogorszeniu z FV na U1. Jest to wynik uzyskania danych o lepszej jakośc.
Przy określaniu oceny parametru struktura i funkcje stosowano inne progi wartości niż podane w wytycznych. Przyjęto następującą waloryzację parametru:
- Jeśli na ponad 50% monitorowanych stanowisk stan struktury i funkcji siedliska został oceniony jako właściwy FV i jednocześnie na mniej niż 20% stanowisk został oceniony jako zły U2 – ocena FV
- Inne kombinacje – ocena U1
- Jeśli na ponad 33% monitorowanych stanowisk stan struktury i funkcji siedliska został oceniony jako zły U2 – ocena U2 ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Distribution map is based on vegetation maps within Natura 2000-sites and relevé data in- and outside Natura 2000-sites over a period of 12 years. Some vegetation maps still contain uncertainties and relevé data may have gaps, but we assume that total distribution is well covered for 90% or more. A change of 10% is used as a threshold for positive or negative trends. Range data and trends are based upon maps in Dutch Rijksdroehoek co-ordinates, while distribution maps have been delivered in ETRS co-ordinates. ||
->Coverage: No reliable new data on area available ||
->HabCondition: S&F assessment based on NDFF analysis, in cooperation with CBS. Secondary source: Analysis of average dead wood volume per ha based on plot data from the Fifth (2001-2005) and Sixth (2012-2013) Dutch Forest Inventory (DFI). NDFF-score U2 and DFI-score U2 are overruled by TS-score U1 because of methodological uncertainty and the small sample sizes (due to the small range and area). As a consequence S&F trend is considered unknown. ||
->Future: N/A ||
->Conclusion: Functioning (NDFF)-score U2 is overruled because 1) TS score U1 and 2) positive trend in area in good condition and 3) uncertainty about the NDFF-method and DeadWood-method in this small and compact habitat range (with high spatial autocorrelation) ||
->JustificationThreshold: 10% decrease/increase is used as threshold for all trends, due to uncertainty in data; a formula with 75%/25%-thresholds is used for conservation status of Structure & Function and Typical species. ||
->Other: Report by Rienk-Jan Bijlsma (WEnR)

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Maps and CVs are calculated with the standard GIS range tool (DG Environment 2017). Short-term trends are evaluated by visually comparing the new maps with those produced in the previous reporting round. No major differences are found between maps. It is generally expected that the range of forest habitat types has remained stable in the past and is not predicted to change due to current pressures or future threats. Thus, it is generally expected that FRR = CV. ||
->Coverage: The CVs and trends are estimated mainly on data collected by the National Forest Inventory during two consecutive five-year periods (2008-2012 and 2013-2017; Berglund 2019). The FRAs are set equal to at least the CVs in 1995, the year of entry into force of the Habitats Directive, or to an estimated long-term area need, corrensponding to 20% of the pre-industrial/original area (Berglund 2019). ||
->HabCondition: The proportions of the area in good, not good and unknown condition within the Natura-2000 sites are used as indicators of the respective proportions in the region concerned. Thus, the results obtained based on the data from the Natura-2000 sites are extrapolated to the whole forest landscape in the region while assuming that the conditions in sites outside the Natura-2000 network are no better than within (Berglund 2019). ||
->Future: The current status and the trends of the range and the area as well as the structures and functions are expected to remain the same as in the current reporting period 2013-2018. Hence, the future prospects are expected to be equal to the overall results for the current reporting period obtained when summing the results of the three other factors; i.e. the range, the area, and the structures and functions. ||
->Conclusion: The overall status and the trend in status are evaluated according to the guidelines (DG Environment 2017). ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Use of the map produced by the range tool without exclusion of grid squares as the range is overall consistent ||
->Coverage: Wallonia: surface and its trends are estimated through the information coming from the Walloon Forest Inventory. Even if the difference between the 1st cycle and the (not yet finalized) 2nd cycle of Walloon Forest Inventory is positive, it is statistically not sifnificant and the trends is considered stable. The habitat in some plots has been better identified since last reporting, which explains the difference of surface area ||
->HabCondition: In Wallonia, structures & functions of forests are assessed through information coming from the Walloon Forest Inventory. Assessment of surfaces in good condition is not relevant, as some parameters can only be calculated at Walloon biogeographical scale and make no sense in individual plots, due to the size of plots (~ 0,1 ha). These parameters include average number of large dead and living trees, diversity of structures, and evolution of old growth forests surfaces... Estimating local condition of plots excluding these regional parameters would provide a very bad image of real condition of forests, which may not be consistent with the final status. Thus, the final status of structures and functions and its real trends are only assessed at biogeographical level, and all the Walloon share of the surface is mentioned as "unknown status" in field 6.1. The real trend of structures and functions at biogeographical is indicated in field 6.5. For habitat 9110, most constitutive parameters of S&F are stable, except large living woods (slightly increasing - positive trend) and soil compaction (increasing - but with a better collection of data at 2nd cycle of Forest Inventory). The balance between trends leads to the conclusion that the overall trend is stable ||
->Future: N/A ||
->Conclusion: Better information on surface has been acquired since last reporting cycle, and shows that the surface is actually not decreasing, but even seems slightly (but not signficantly) increasing, which explains the estimation of a stable trends. ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Lücken im Nordosten und Südwesten des Verbreitungsgebiets bzw. fehlende Größenanteile gehen auf fehlende aktuelle Daten zurück bzw. sind methodenbedingt, bedeuten aber im Regelfall keine tatsächlichen Verluste im Verbreitungsgebiet des LRT. ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: Il faudrait pouvoir retravailler la liste d'espèces typiques en prenant en compte tous les compartiments de la biocénose forestière. ||
->Future: N/A ||
->Conclusion: QA feedback : Confirmation des résultat des structures et fonctions U1. Si on avait pu ventiler les surfaces, non pas en bon versus mauvais état, mais en trois classes de valeurs, on aurait majoritairement affecté la classe intermédiaire correspondant au "défavorable inadéquat". ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: The estimate of habitat area is based on an extrapolation method or expert based judgement, using when appropriate the techniques suggested by the ETC. Such methodologies may have a degree of uncertainty that cannot be quantified; for this reason, the values included in the report are to be considered approximate estimates. ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: The evaluation for the last reporting period was based on a nationwide inventory of forests realised from 1992 to 2002 the results of which had to be interpreted for the annex I habitat type report. For the reporting periode 2013 - 2018, results of a new inventory of forest habitats and other habitats within forest areas are available. From 2014 to 2018, 67% of all forest areas have been inventorised with special focus on the information needed for the present reporting. Information for the remaining third was based on the initial inventory. The country-wide survey will be finalised by 2020.
Because of this improved knowledge, we do not consider the reduced range compared to the last reporting period as a real loss but rather as more accurate data. ||
->Coverage: The evaluation for the last reporting period was based on a nationwide inventory of forests realised from 1992 to 2002 the results of which had to be interpreted for the annex I habitat type report. For the reporting periode 2013 - 2018, results of a new inventory of forest habitats and other habitats within forest areas are available. From 2014 to 2018, 67% of all forest areas have been inventorised with special focus on the information needed for the present reporting. Information for the remaining third was based on the initial inventory.
Because of this improved knowledge, we do not consider the larger area compared to the last reporting period as a real gain but rather as more accurate data. ||
->HabCondition: For forest habitat types, estimations for area under good respectively under not good condition were based on the recent survey of 67% of all wooded areas. The value indicated for area under good respectively under not good condition for a given habitat type is the result of the survey within forest areas. The area of this habitat type where only data from former inventories are available is indicated in the fields "area where condition is not known". ||
->Future: N/A ||
->Conclusion: From 2014 to 2018, 67% of all forest areas have been inventorised with special focus on the information needed for the present reporting. Of the 53,63 km2 of habitat type 9110 surveyed, 99,5% were in good condition. ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Wartość podana w polu 4.1 (171200km2) jest wyższa niż wartość podana w raporcie z 2013 r. (169704 km2), ale faktyczny zasięg nie uległ znacznej zmianie w porównaniu z poprzednim okresem raportowania. W aktualnym okresie raportowym wartość podana w polu 4.1 została wyliczona przy użyciu dedykowanego narzędzia (Range Tool) przygotowanego przez ETC/BD oraz EEA, w sposób automatyczny na podstawie rozmieszczenia kwadratów, w których występuje siedlisko w regionie biogeograficznym. Przy obliczaniu powierzchni zasięgu siedliska zastosowano „gap distance” wynoszący 40km, a wyliczony przez narzędzie zasięg nie został przycięty do granic Polski. ||
->Coverage: W poprzednim raporcie powierzchnię siedliska oszacowano na podstwie Bazy Invent (obejmującą tereny zarządzane przez PGL LP - ok 80% powierzchni leśnej) i uzupełniono to o szacunek powierzchni siedliska na pozostałych gruntach. Obecnie Bank Danych o Lasach (zawiera zaktualizowane i częściowo zweryfikowane dane zawarte w Bazie Invent) podaje areał siedliska 9110 na poziomie 767 km2. Przyjmujac, że udział siedliska 9110 na terenie innych własności jest taki sam jak na terenie zarządzanym przez PGL LP otrzymujemy w przybliżeniu 920 km2. ||
->HabCondition: Do określenia powierzchni siedliska w dobrym, złym lub nieznanym stanie (pkt. 6.1) wykorzystano rozkład ocen parametru struktura i funkcje na stanowiskach monitoringowych oraz wartość powierzchni siedliska w regionie podaną w pkt. 5.2 c). Przyjęto następujące założenia:
- minimalna powierzchnia siedliska w dobrym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na FV
- maksymalna powierzchnia siedliska w dobrym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na FV i U1
- minimalna powierzchnia siedliska w złym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na U2
- maksymalna powierzchnia siedliska w złym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na U1 i U2
- minimalna i maksymalna powierzchnia siedliska o nieznanym stanie to jest powierzchnia wskazana w pkt 5.2 c) x procent stanowisk monitoringowych, na których parametr struktura i funkcje został oceniony na XX ||
->Future: N/A ||
->Conclusion: Ocena stanu ochrony została wystawiona w oparciu o dane zebrane z 190 stanowisk monitoringowych.
Parametr powierzchnia siedliska oraz perspektywy ochrony w porównaniu do poprzedniego raportu uległa poprawie z U1 na FV. Jest to wynik uzyskania danych o lepszej jakości.
Przy określaniu oceny parametru struktura i funkcje stosowano inne progi wartości niż podane w wytycznych. Przyjęto następującą waloryzację parametru:
- Jeśli na ponad 50% monitorowanych stanowisk stan struktury i funkcji siedliska został oceniony jako właściwy FV i jednocześnie na mniej niż 20% stanowisk został oceniony jako zły U2 – ocena FV
- Inne kombinacje – ocena U1
- Jeśli na ponad 33% monitorowanych stanowisk stan struktury i funkcji siedliska został oceniony jako zły U2 – ocena U2 ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: Maps and CVs are calculated with the standard GIS range tool (DG Environment 2017). Short-term trends are evaluated by visually comparing the new maps with those produced in the previous reporting round. No major differences are found between maps. It is generally expected that the range of forest habitat types has remained stable in the past and is not predicted to change due to current pressures or future threats. Thus, it is generally expected that FRR = CV. ||
->Coverage: The CVs and trends are estimated mainly on data collected by the National Forest Inventory during two consecutive five-year periods (2008-2012 and 2013-2017; Berglund 2019). The FRAs are set equal to at least the CVs in 1995, the year of entry into force of the Habitats Directive, or to an estimated long-term area need, corrensponding to 20% of the pre-industrial/original area (Berglund 2019). ||
->HabCondition: The proportions of the area in good, not good and unknown condition within the Natura-2000 sites are used as indicators of the respective proportions in the region concerned. Thus, the results obtained based on the data from the Natura-2000 sites are extrapolated to the whole forest landscape in the region while assuming that the conditions in sites outside the Natura-2000 network are no better than within (Berglund 2019). ||
->Future: The current status and the trends of the range and the area as well as the structures and functions are expected to remain the same as in the current reporting period 2013-2018. Hence, the future prospects are expected to be equal to the overall results for the current reporting period obtained when summing the results of the three other factors; i.e. the range, the area, and the structures and functions. ||
->Conclusion: The overall status and the trend in status are evaluated according to the guidelines (DG Environment 2017). ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: Assumption: 90% of habitat area is estimated to be in good condition. ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: The estimate of habitat area is based on an extrapolation method or expert based judgement, using when appropriate the techniques suggested by the ETC. Such methodologies may have a degree of uncertainty that cannot be quantified; for this reason, the values included in the report are to be considered approximate estimates. ||
->HabCondition: Fagus sylvatica
Luzula sp. pl.
Vaccinium sp. pl ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report  

Information provided in the field 2.7.5: Reported additionnal information: ||
->Range: N/A ||
->Coverage: N/A ||
->HabCondition: N/A ||
->Future: N/A ||
->Conclusion: N/A ||
->JustificationThreshold: N/A ||
->Other: N/A

Open Original Report