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2.2.3.1  Coastal breeding localities  of  seabirds in  Skeleton  Coast
                  National Park




                  Authors: DB Tom, and RJM Crawford
                  Abstract:
                  Five seabird  species  have bred at 34 localities  along  the coastline  of Skeleton Coast National  Park (SCNP) in northern Namibia:
                  Cape Cormorant (Phalacrocorax capensis), White-breasted Cormorant (P. lucidus), Kelp Gull (Larus dominicanus), Grey-headed Gull
                  (Chroicocephalus  cirrocephalus) and Damara  Tern  (Sternula balaenarum).  The breeding  has taken place at 34 localities between
                  the mouths of the Cunene (Kunene) and Ugab rivers that include both natural sites and artificial structures such as ship wrecks. The
                  most recent estimates of numbers of Damara Terns breeding in SCNP suggest that 192 pairs bred there, or c. 25% of the species’
                  population.
                  Introduction:
                  Records  exist  of  breeding  by  five  species  of  seabirds  along  the  coastal  zone  of  Skeleton  Coast  National  Park  (SCNP),  Namibia,
                  which  stretches from the mouth of the Cunene  River at the border with Angola  in the north to that of the Ugab River.  The park’s
                  southern fence is just south of the Ugab River mouth (Braby 2011). The positions of the 34 localities are shown in Figure 1. Cape
                  Cormorant  (Phalacrocorax capensis) bred at four of the localities,  White-breasted  Cormorant  (P. lucidus) at ten, Kelp Gull (Larus
                  dominicanus)  at  three, Grey-headed  Gull (Chroicocephalus  cirrocephalus)  at  one and Damara  Tern  (Sternula balaenarum)  at  24.
                  Cape and White-breasted Cormorants, Kelp Gulls and Damara Terns also breed coastally in southern Angola. However, the Cunene River
                  mouth is the northernmost recorded locality for breeding by Grey-headed Gulls in the Benguela ecosystem.
                     Records of breeding in SCNP are collated below with brief descriptions of localities used for breeding. ‘√’ signifies breeding occurred
                  at the locality but the numbers were not ascertained; ‘?’ that breeding may have taken place. A short summary of methods used to obtain
                  estimates of numbers breeding is given in the chapter ‘Introduction to Seabird Breeding Localities’. Where data were available, the
                  number of Damara Terns breeding in 2021/22 were estimated from Kolberg (2022), as the larger of the count of pairs/nests (each fledgling
                  seen was assumed to represent a pair) and an estimate of breeding pairs that was derived from a relationship between approximately
                  concurrent counts of numbers of pairs and adults (Braby et al. 2024a). The most recent estimates of numbers of Damara Terns breeding
                  in SCNP suggest that 192 pairs bred there, or c. 25% of the species’ population (Braby et al. 2024b).
                     Only five localities (the Cunene River mouth and surrounds, Die Oase, the Henrietta Spachette wreck and saltpan, the Toscanini pylons
                  and Decca station and Huab River and surrounds) hosted more than one seabird species. These sites are dealt with first and then followed
                  by accounts of localities used by single species. In all groupings, the localities are ordered from north to south.

                  1. Multispecies breeding localities               Grey-headed Gull
                                                                         Year                 No. of pairs
                  Cunene River mouth and surrounds
                  Coordinates:  17.25  S; 11.80 E (estuary); 17.27 S;    2002 a                   6
                  11.73 E (surrounds)                               a Paterson (2004)
                  Description:  White-breasted  Cormorants  and Grey-
                  headed Gulls bred on vegetated, rocky islands  in the   Damara Tern
                  Cunene  River  estuary (Brooke et al. 1982, Patterson
                  2004). Nests of Grey-headed Gulls were platforms of reed,   Year            No. of pairs
                  lined with grass, that were built on top of short spiky grass   1992  a         2
                  c. 20 m from the water’s edge (Paterson 2004). Damara   2021/22 b               5
                  Terns bred  in the surrounding  area south of the estuary
                  (Braby 2011).                                     a Braby (2011)
                  Conservation status: It falls within SCNP but is a popular   b Kolberg (2022) as described in Braby et al. (2024a)
                  place for fishing, which may result in substantial vehicular
                  traffic  causing  disturbance  at  breeding  habitat  (Kolberg   Die Oase
                  2022).                                            Coordinates: 19.45 S; 12.82 E
                  Note: Caspian Terns (Hydroprogne caspia), which breed to   Description: A reed-fringed lake c. 7.5 km from the sea.
                  the north at Ilha dos Tigres in southern Angola and along   Cape and White-breasted Cormorants nested among the
                  the Namibian coast between Swakopmund and the Orange   reeds (Cooper et al. 1982, Kemper and Simmons 2015). In
                  River, occur at the Cunene River mouth. On nine counts   1983, a solitary Kelp Gull nest was located on a sandspit at
                  undertaken at the mouth, the mean number seen (± SD)   the lake (Bridgeford 1982).
                  was 11 ± 16, with a maximum count of 50 (Simmons 2015).  Conservation status: The site is within SCNP.
                                                                    Species and numbers breeding:
                  Species and numbers breeding:                     Cape Cormorant
                  White-breasted Cormorant                               Year                 No. of pairs
                        Year                No. of pairs                     a
                       1981 a                   15                       1981                   c. 75
                                                                    a Cooper et al. (1982)
                  a Brooke et al. (1982)





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