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Justification Justification of Red List Category This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence 30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern. Population justification The global population is estimated to number c.115,000-340,000 individuals (Wetlands International 2015). The European population is estimated at 37,600-66,400 calling or lekking males, which equates to 75,300-133,000 mature individuals (BirdLife International 2015).

National population estimates include: c.100-10,000 breeding pairs, c.50-1,000 individuals on migration and c.50-1,000 wintering individuals in China. Ecology Behaviour Populations breeding on the Atlantic coast of Europe, in the Mediterranean and in South Africa are largely sedentary due to the relatively mild winters (Newbery et al.

1996) (although they may make local dispersive movements related to rainfall) (Hancock and Kushlan 1984). Continental populations are mainly migratory however (Newbery et al.

1996, Kushlan and Hancock 2005) with a marked post-breeding dispersal of immatures (Kushlan and Hancock 2005). The species breeds from March to June in Eurasia and during the rains from September to January in South Africa (del Hoyo et al. It usually nests solitarily although males are polygamous and may mate with up to five females nesting on a large wetland site (del Hoyo et al. The species remains solitary throughout the year (del Hoyo et al. 1992) (although migratory individuals may travel in small flocks) (Kushlan and Hancock 2005), and is mainly crepuscular in its activities (Kushlan and Hancock 2005). Habitat Breeding The species has highly restrictive breeding habitat requirements (del Hoyo et al. It shows a strong preference for quiet lowland marshes around lakes and rivers (less than 200 m above sea-level) (Kushlan and Hancock 2005) with extensive dense young reedbeds of Phragmites spp.

With 1- 3 years worth of new growth (Marion et al. 2000, Puglisi et al. 2005) but still maintaining some old or dead stems (del Hoyo et al. 1992)) that are flooded but are fairly shallow (del Hoyo et al. 1992) (less than 30 cm deep) (Newbery et al.

1996), have few fluctuations in water-level (del Hoyo et al. 1992), have low acidity (Kushlan and Hancock 2005)and are surrounded by clear open areas (del Hoyo et al. 1992) of deeper water is maintained into the driest part of the breeding season (Gilbert et al. Breeding adults are more attracted to unfragmented (Puglisi et al. 2005) reedbeds over 20 ha in area, although smaller sites with networks of reed-fringed waterways or open wetland habitats with a number of small reedbeds (Newbery et al.

In case of issues, you can reference this file as a restoration point, particularly for the PATH variable: • set >>%TEMP% Environmental_Variables_Backup.txt • Enter the following command to update the environmental variables. Setting Environmental Variables After installation, you may need to set ARBORPATH, ESSBASEPATH, and PATH Environmental Variables (the latter allows batch scripts to call MaxL just by entering “startMaxL.cmd” rather than entering a fully qualified path). • Goto Start Menu > Run • Type in “cmd” and click OK • IMPORTANT – Enter the following commands to backup environmental variables to a temporary text file.

1996) (greater than 100 m) (Gilbert et al. 2005) over a wide area may also be used (Newbery et al. The species avoids saline waters (Kushlan and Hancock 2005) but is equally abundant in fresh or brackish habitats (del Hoyo et al. In estuarine or delta marshes) (Snow and Perrins 1998), and may occasionally nest in stands of rushes Scirpus spp. (del Hoyo et al. 1992) or Papyrus spp. If reeds are unavailable (Kushlan and Hancock 2005).

Non-breeding The species frequents a more varied range of habitats outside of breeding season, foraging on rice-fields, watercress beds, gravel pits, fish farms, ditches, sewage farms (del Hoyo et al. 1992), small ponds and wet grassy areas (Kushlan and Hancock 2005) as well as marshes and reedbeds (del Hoyo et al. It also forages in running water (e.g. Streams) when still waterbodies freeze during the winter (Hancock and Kushlan 1984). Diet Its diet varies depending on the site and season although it predominantly takes fish (particularly cyprinids and eels) and amphibians as well as adult and larval insects, spiders, crustaceans, molluscs, snakes, lizards, birds, nestlings and small mammals (del Hoyo et al.