Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018

This report presents details of a monitoring survey conducted between 2015 and 2018 to assess the conservation status of the Annex II species Saxifraga hirculus (Marsh Saxifrage) (EU code 1528). The aims of the survey were to assess the species in terms of three parameters: Population, Habitat for t...

Full description

Bibliographic Details
Main Authors: O'Neill, Fionnuala, Hodd, Rory, Long, Maria
Format: Report
Language:English
Published: National Parks and Wildlife Service. Department of Culture, Heritage and the Gaeltacht 2019
Subjects:
Online Access:http://hdl.handle.net/2262/89914
id fttrinitycoll:oai:tara.tcd.ie:2262/89914
record_format openpolar
institution Open Polar
collection The University of Dublin, Trinity College: TARA (Trinity's Access to Research Archive)
op_collection_id fttrinitycoll
language English
topic Saxifraga hirculus
Marsh saxifrage
Monitoring
Annex II
EU Habitats Directive
Ecology
Conservation status
Article 17
Field survey
spellingShingle Saxifraga hirculus
Marsh saxifrage
Monitoring
Annex II
EU Habitats Directive
Ecology
Conservation status
Article 17
Field survey
O'Neill, Fionnuala
Hodd, Rory
Long, Maria
Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018
topic_facet Saxifraga hirculus
Marsh saxifrage
Monitoring
Annex II
EU Habitats Directive
Ecology
Conservation status
Article 17
Field survey
description This report presents details of a monitoring survey conducted between 2015 and 2018 to assess the conservation status of the Annex II species Saxifraga hirculus (Marsh Saxifrage) (EU code 1528). The aims of the survey were to assess the species in terms of three parameters: Population, Habitat for the Speciesand Future prospects. Nineteen sites were surveyed, comprising 16 in Co.Mayo and three in Co. Sligo. A review of the previous baseline and monitoring surveys was undertaken as part of the project remit. The assessment criteria were generally found to be suitable. However, following population surveys a number of points were noted: absence of Sagina nodosa did not necessarily signify unfavourable habitat condition, so expert judgement was applied on a site-by-site basis; the general target for vegetation height had been set too low at ?15cm and was adjusted upwards to ?20cm; and for water level, or hydrology, to pass, a pass rate of 40% of stops was applied in the current survey, with expert judgement the final decider of whether the site?s overall hydrology was suitable or not. Population extents were determined by extensive walkover surveys and recording GPS waypoints at the outer limits of the population. These points were used to map polygon envelopes in GIS. Assessment data were recorded within monitoring plots measuring 1 m2, which were placed at several locations throughout the population. Count data from monitoring plots were extrapolated up to the population level by multiplying the values in the 1m2 plots by the area in square metres of occupied habitat mapped in GIS. Population was assessed at each site by three criteria: total number of rosettes estimated for the population, density of rosettes (average of counts from 1m2 monitoring plots), and estimated number of flowering heads in the population. Habitat for the Species was assessed by seven criteria: area of S. hirculus (target to match or exceed that measured in the baseline survey), water level, cover of Sagina nodosa (positive indicator species), cover of Molinia caerulea (negative indicator species), cover of Holcus lanatus (negative indicator species), vegetation height, and grazing (recorded on a four-category scale). Positive and negative activities were recorded at sites where they occurred. Grazing was usually seen as a positive where it occurred, although grazing by cattle was regarded as negative and sheep grazing is generally preferable for fragile S. hirculus habitat. Most of the negative pressures recorded were of a low intensity or affected less than half of the habitat at a site. However, undergrazing was regarded as a serious pressure at three sites. Drainage was a direct problem at four sites, although the effect was recorded as low intensity. Water levels at two sites were regarded as too low for S. hirculus, with vegetation tolerant of drier conditions becoming tall and rank as a consequence and out-competing S. hirculus. Climate change may become an important negative impact in the future but its intensity is currently unknown and the length of time over which a measurable impact will be seen is likewise unknown. The Population, Habitat for the Species and Future prospects assessment results were combined to produce a single overall site-level assessment for each site. Thirteen sites received a Favourable assessment, four sites were assessed as Unfavourable-Inadequate, and two sites were Unfavourable-Bad. The report concludes with a discussion of the results and recommendations for monitoring the species in the future and improving the conservation status of less favourably scored sites. The NPWS Project Officer for this report was: Deirdre Lynn; Deirdre.Lynn@chg.gov.ie This IWM was edited by Deirdre Lynn & Neil Lockhart
format Report
author O'Neill, Fionnuala
Hodd, Rory
Long, Maria
author_facet O'Neill, Fionnuala
Hodd, Rory
Long, Maria
author_sort O'Neill, Fionnuala
title Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018
title_short Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018
title_full Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018
title_fullStr Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018
title_full_unstemmed Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018
title_sort results of a monitoring survey of the annex ii species saxifraga hirculus (marsh saxifrage) in ireland 2015?2018
publisher National Parks and Wildlife Service. Department of Culture, Heritage and the Gaeltacht
publishDate 2019
url http://hdl.handle.net/2262/89914
long_lat ENVELOPE(-145.100,-145.100,-76.467,-76.467)
geographic Lockhart
geographic_facet Lockhart
genre Marsh Saxifrage
Saxifraga hirculus
genre_facet Marsh Saxifrage
Saxifraga hirculus
op_relation 2019
No.112
Irish wildlife manuals
Fionnuala O'Neill, Rory Hodd, Maria Long, 'Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018', [report], National Parks and Wildlife Service. Department of Culture, Heritage and the Gaeltacht, 2019-10, Irish wildlife manuals, No.112, 2019
13936670
http://hdl.handle.net/2262/89914
op_rights Y
openAccess
_version_ 1766066951975600128
spelling fttrinitycoll:oai:tara.tcd.ie:2262/89914 2023-05-15T17:10:22+02:00 Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018 O'Neill, Fionnuala Hodd, Rory Long, Maria 2019-10 http://hdl.handle.net/2262/89914 en eng National Parks and Wildlife Service. Department of Culture, Heritage and the Gaeltacht IE 2019 No.112 Irish wildlife manuals Fionnuala O'Neill, Rory Hodd, Maria Long, 'Results of a monitoring survey of the Annex II species Saxifraga hirculus (Marsh Saxifrage) in Ireland 2015?2018', [report], National Parks and Wildlife Service. Department of Culture, Heritage and the Gaeltacht, 2019-10, Irish wildlife manuals, No.112, 2019 13936670 http://hdl.handle.net/2262/89914 Y openAccess Saxifraga hirculus Marsh saxifrage Monitoring Annex II EU Habitats Directive Ecology Conservation status Article 17 Field survey report edepositireland 2019 fttrinitycoll 2020-12-10T23:51:31Z This report presents details of a monitoring survey conducted between 2015 and 2018 to assess the conservation status of the Annex II species Saxifraga hirculus (Marsh Saxifrage) (EU code 1528). The aims of the survey were to assess the species in terms of three parameters: Population, Habitat for the Speciesand Future prospects. Nineteen sites were surveyed, comprising 16 in Co.Mayo and three in Co. Sligo. A review of the previous baseline and monitoring surveys was undertaken as part of the project remit. The assessment criteria were generally found to be suitable. However, following population surveys a number of points were noted: absence of Sagina nodosa did not necessarily signify unfavourable habitat condition, so expert judgement was applied on a site-by-site basis; the general target for vegetation height had been set too low at ?15cm and was adjusted upwards to ?20cm; and for water level, or hydrology, to pass, a pass rate of 40% of stops was applied in the current survey, with expert judgement the final decider of whether the site?s overall hydrology was suitable or not. Population extents were determined by extensive walkover surveys and recording GPS waypoints at the outer limits of the population. These points were used to map polygon envelopes in GIS. Assessment data were recorded within monitoring plots measuring 1 m2, which were placed at several locations throughout the population. Count data from monitoring plots were extrapolated up to the population level by multiplying the values in the 1m2 plots by the area in square metres of occupied habitat mapped in GIS. Population was assessed at each site by three criteria: total number of rosettes estimated for the population, density of rosettes (average of counts from 1m2 monitoring plots), and estimated number of flowering heads in the population. Habitat for the Species was assessed by seven criteria: area of S. hirculus (target to match or exceed that measured in the baseline survey), water level, cover of Sagina nodosa (positive indicator species), cover of Molinia caerulea (negative indicator species), cover of Holcus lanatus (negative indicator species), vegetation height, and grazing (recorded on a four-category scale). Positive and negative activities were recorded at sites where they occurred. Grazing was usually seen as a positive where it occurred, although grazing by cattle was regarded as negative and sheep grazing is generally preferable for fragile S. hirculus habitat. Most of the negative pressures recorded were of a low intensity or affected less than half of the habitat at a site. However, undergrazing was regarded as a serious pressure at three sites. Drainage was a direct problem at four sites, although the effect was recorded as low intensity. Water levels at two sites were regarded as too low for S. hirculus, with vegetation tolerant of drier conditions becoming tall and rank as a consequence and out-competing S. hirculus. Climate change may become an important negative impact in the future but its intensity is currently unknown and the length of time over which a measurable impact will be seen is likewise unknown. The Population, Habitat for the Species and Future prospects assessment results were combined to produce a single overall site-level assessment for each site. Thirteen sites received a Favourable assessment, four sites were assessed as Unfavourable-Inadequate, and two sites were Unfavourable-Bad. The report concludes with a discussion of the results and recommendations for monitoring the species in the future and improving the conservation status of less favourably scored sites. The NPWS Project Officer for this report was: Deirdre Lynn; Deirdre.Lynn@chg.gov.ie This IWM was edited by Deirdre Lynn & Neil Lockhart Report Marsh Saxifrage Saxifraga hirculus The University of Dublin, Trinity College: TARA (Trinity's Access to Research Archive) Lockhart ENVELOPE(-145.100,-145.100,-76.467,-76.467)