Page 67 - Atlas Sea Birds Ver1
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2.2.3.2 Coastal breeding localities of seabirds between Ugab River

                  Mouth and Mile 4, Swakopmund


                  Authors: RJM Crawford, RJ Braby, J Braby, and DB Tom

                  Abstract:
                  Four species of seabird have bred at 22 localities along that portion of the coastal zone of the Dorob National Park (DNP), Namibia, that
                  extends from the Ugab River at the southern border of Skeleton Coast National Park (SCNP) to, but not including, Mile 4 Saltworks at the
                  north of Swakopmund. They were: Cape Cormorant (Phalacrocorax capensis), White-breasted Cormorant (P. lucidus), Kelp Gull (Larus
                  dominicanus) and Damara Tern (Sternula balaenarum). This chapter collates estimates of numbers of all species breeding at each locality.
                  Wooden platforms in Cape Cross Lagoon, from which seabird guano was harvested, provided important breeding habitat for nesting
                  by Cape and White-breasted cormorants. The most up-to-date estimates of Damara Terns suggest 122 pairs, or c. 16% of the global
                  population, bred in DNP in 2021/22.
                  Introduction:
                  Records exist of breeding by four species of seabird at 22 localities along that portion of the coastal zone of Dorob National Park (DNP),
                  Namibia, which extends from the Ugab River at the southern border of Skeleton Coast National Park (SCNP) to the north of Swakopmund
                  (excluding Mile 4 Saltworks at the north of Swakopmund). DNP was gazetted as a national park under the Nature Conservation Ordinance
                  No. 4 of 1975 on 1 December 2010 and sites falling within it are protected in terms of regulations promulgated for DNP. The species that
                  breed in this region are the same as those that breed in the coastal zone of SCNP: Cape Cormorant (Phalacrocorax capensis), White-
                  breasted Cormorant (P. lucidus), Kelp Gull (Larus dominicanus) and Damara Tern (Sternula balaenarum), except that Grey-headed Gull
                  (Chroicocephalus cirrocephalus) has not been recorded to bred in the region. The sites include a wrecked ship, three groups of wooden
                  platforms, which were erected at Cape Cross Lagoon to collect guano deposited by the two cormorant species (on which Kelp Gulls also
                  nested) and 18 locations where Damara Terns bred. The positions of these localities are shown in Figure 1.
                     Records of breeding are collated below with brief descriptions of localities. ‘√’ signifies breeding occurred at the locality but the numbers
                  were not ascertained. A  short summary of  methods used to  obtain counts is given in the chapter ‘Introduction to  Seabird Breeding
                  Localities’. The localities used by the cormorants and gulls are dealt with first and then followed by accounts of those used by Damara
                  Terns. In both instances, the localities are ordered from north to south.
                     Where data were available, the numbers 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. 2023).
                     In 1998, the Cape Cross Lagoon was considered a Namibian, southern African and globally Important Bird Area (Simmons et al.
                  1998). In addition to the seabirds, it hosts large numbers of other waterbirds, including Black-necked Grebe (Podiceps nigricollis), Greater
                  (Phoenicopterus ruber) and Lesser (Phoeniconaias minor) Flamingo, Chestnut-banded Plover (Chadarius pallidus) and other shorebirds
                  (Simmons et al. 1998).

                  Conservation status: Despite regulations promulgated for   (Rand 1963). Cape Cormorants have nested on platforms
                  DNP, seabirds at some breeding sites may be subject to   in the northern (21.8174; 14.0129 and 21.8235; 14.0188)
                  unintentional disturbance by humans.              and central (21.8379 S;  14.0381 E)  regions (Cooper et
                                                                    al. 1982) and White-breasted Cormorants on platforms
                  1. Cormorant and gull breeding localities         in all three regions (Brooke et al. 1982). Kelp Gulls have
                                                                    bred on or in the vicinity of platforms in all three regions
                  Winston shipwreck, 10 km south of Durissa Bay     (Crawford et al. 1982) and large numbers have roosted at
                  Coordinates: 21.27 S; 13.68 E                     the most southern of the northern platforms (Rand 1963)
                  Description:  A shipwreck  10 km south of Durissa  Bay   that appears to be no longer used by cormorants. Lagoon
                  (Brooke  et al. 1982)  that has broken  up since  White-  water is deepest in the central region (Rand 1963), so those
                  breasted Cormorants nested at it.                 platforms are best protected from mammal predators.
                  Species and numbers breeding:                     Additionally, fences running  into the lagoon  have been
                  White-breasted Cormorant                          constructed around some platforms. The platforms in the
                        Year                No. of pairs            southern region (21.8522 S; 14.0510 E) were incompletely
                                                                    constructed and in close proximity to land on three sides in
                       1977 a                   16                  1963 (Rand 1963). They have since disintegrated and their
                       1979 a                   27                  scaffolds  have  become  joined  to  land.  Seabirds  stopped
                       1980 a                   28                  breeding at this site in 2020 or earlier. The platforms were
                                                                    built to  encourage nesting and roosting of  seabirds and
                       1981 a                   32                  deposition of guano (Rand 1963).
                       2007 b                   0                     Gevers (1936, cited by Cooper  et al. 1982) noted
                                                                    ‘The  lagoon  is  inhabited  by  thousands  of  flamingos  and
                  a Brooke et al. (1982)                            hundreds of thousands of cormorants which roost on low
                  b RJM Crawford (unpublished record)               islets in the lagoon and are the cause of the accumulation
                                                                    of quantities  of guano.’ A total of 200,000  short tons [c.
                  Cape Cross Lagoon                                 197,300  metric tons] of guano  was removed  from these
                  Description:                                      islets between 1895 and 1903, but it was uncertain if the
                  A variety of low  wooden  platforms having  a total area   deposits were old or relatively new (Rand 1952, cited in
                  of 68,000 m  are situated in three regions of the lagoon   Cooper et al. 1982). Guano at the central platforms was later
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