Haramoep & Black Mountain Mine

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General Information

Status:

Global IBA (A1, A3)

Province:

Northern Cape

Protection:

Unprotected

Size:

116 070 ha

Number:

SA035

Additional Info

  • Site description

    Situated near Aggeneys, this IBA is characterised by an arid landscape of extensive sandy and gravel plains with sparse vegetation scattered between bare sand patches. Inselbergs form islands of rocky habitat in a sea of red sand. Large sand dunes fill the fossil course of the Koa River. The gravel plains are covered by sparse dwarf shrubs and short bushman grasses and they hide dwarf succulents. The dry riverbeds support taller woody vegetation, including smelly shepherd's tree Boscia foetida.

    The IBA falls within the Bushmanland Bioregion and three biomes (Desert, Nama Karoo and Succulent Karoo) are represented. Seven vegetation types are present, of which one is Endangered. One Endangered and two Vulnerable habitat units within these are considered irreplaceable.

    Although much of the land area remains natural, large areas are overgrazed and degraded. Approximately 90% of the land is natural and utilised for ranching. The rest has been transformed by agriculture, mining activities, homesteads, settlements, erosion, roads and power-line servitudes.

    Birds

    This IBA is one of only a few sites protecting the globally threatened Red Lark Calendulauda burra, which inhabits the red sand dunes and sandy plains with a mixed grassy dwarf shrub cover; and the near-threatened Sclater's Lark Spizocorys sclateri, on the barren stony plains. It also holds 16 of the 23 Namib-Karoo biome-restricted assemblage species as well as a host of other arid-zone birds.

    At the time of this IBA's assessment, its 27 pentads had been poorly atlased for SABAP2. The total number of species recorded for the IBA is 198.

    Ludwig's Bustard Neotis ludwigii and Kori Bustard Ardeotis kori are regularly seen. Martial Eagle Polemaetus bellicosus, Secretarybird Sagittarius serpentarius, Verreauxs' Eagle Aquila verreauxii, Booted Eagle Hieraaetus pennatus, Cape Eagle-Owl Bubo capensis and Spotted Eagle-Owl B. africanus are present. On occasion Hooded Vulture Necrosyrtes monachus can be spotted close to the Orange River.

    The IBA is seasonally important for nomadic larks, such as Stark's Lark Spizocorys starki, and sparrow-larks, which are abundant after good rains.

    This IBA is one of only a few sites protecting the globally threatened Red Lark Calendulauda burra, which inhabits the red sand dunes and sandy plains with a mixed grassy dwarf shrub cover; and the near-threatened Sclater’s Lark Spizocorys sclateri, on the barren stony plains. It also holds 16 of the 23 Namib-Karoo biome-restricted assemblage species as well as a host of other arid-zone birds.

    The SABAP2 coverage for the 27 pentads covering this IBA is poor (40%), with fewer than 20 atlas cards. The total number of species recorded for the IBA is 198, and 101 species have been recorded in SABAP2.

    Ludwig’s Bustard Neotis ludwigii and Kori Bustard Ardeotis kori are regularly seen. Martial Eagle Polemaetus bellicosus, Secretarybird Sagittarius serpentarius, Verreauxs’ Eagle Aquila verreauxii, Booted Eagle Hieraaetus pennatus, Cape Eagle-Owl Bubo capensis and Spotted Eagle-Owl B. africanus are present. On occasion Hooded Vulture Necrosyrtes monachus can be spotted close to the Orange River.

    The IBA is seasonally important for nomadic larks, such as Stark’s Lark Spizocorys starki, and sparrow-larks, which are abundant after good rains.

    IBA trigger species

    Globally threatened birds are Red Lark (450–1 980 birds; estimates by Tarboton and Jenkins pers. comm.), Sclater's Lark, Martial Eagle, Kori Bustard, Ludwig's Bustard and Secretarybird. Regionally threatened birds are Karoo Korhaan Eupodotis vigorsii and Verreauxs' Eagle. Restricted-range and biome-restricted birds are Stark's Lark, Karoo Long-billed Lark Certhilauda subcoronata, Black-eared Sparrow-lark Eremopterix australis, Tractrac Chat Cercomela tractrac, Sickle-winged Chat C. sinuata, Karoo Chat C. schlegelii, Layard's Tit-Babbler Sylvia layardi, Karoo Eremomela Eremomela gregalis, Cinnamon-breasted Warbler Euryptila subcinnamomea, Namaqua Warbler Phragmacia substriata, Sociable Weaver Philetairus socius, Pale-winged Starling Onychognathus nabouroup and Black-headed Canary Serinus alario.

    Other biodiversity

    Approximately 35 threatened, rare and endemic plant species occur in the IBA, most of which are dwarf succulents and geophytes. There are two known populations of the near-endemic halfmens Pachypodium namaquanum, as well as many quiver trees Aloe dichotoma (Vulnerable).

    Conservation issues

    Threats

    Renewable energy developments are a new threat placing pressure on this IBA. Four solar energy facilities and wind farms within and adjacent to it have been approved or are in the application phase. Little is known about the impacts of solar farms on the IBA’s trigger species. Possible impacts on birds are loss of habitat, breeding disturbance during construction and collisions with power lines and reflective solar panels. Concentrated solar plants with power towers may also result in solar flux injuries to birds. Wind farms can displace endemic larks. Large trigger species such as Ludwig’s Bustard, Martial Eagle and Verreauxs’ Eagle are highly susceptible to collisions with wind turbines.

    Haramoep BMM TAndersonThere is a history of overstocking in this region and within the IBA, which has led to degradation of habitat. Many ranchers trying to make a living on properties that are economically unviable overexploited the vegetation. Trampling by cattle added to the reduction in vegetation cover and caused erosion and the shifting of dunes. Approximately 75% of optimal habitat for the Red Lark has been lost over the past 100 years. The disappearance of the Red Lark from ranches where dune grassland has been replaced by ephemerals is probably linked to the reduction in grass awns for nesting, shelter and invertebrate and plant foods.

    In recent years, there has been a shift from cattle ranching to raising sheep and goats on many farms in the region. However, overstocking and overgrazing continue to pose a threat in large parts of the IBA.

    There is a serious threat from climate change. It is predicted that temperatures will increase and rainfall decrease sharply in arid areas such as Bushmanland. Locally resident endemic larks, in particular, are at risk. Vegetation change will have marked effects on species such as the restricted-range, habitat-specific Red Lark. Increased CO2 can lead to the increase of C3 plants (shrubs) at the expense of C4 plants (mainly grasses), causing a shift in vegetation diversity and structure and making habitat unsuitable for some species. It is expected that the Red Lark will not meet the challenge of global warming.

    Droughts are expected to become more severe as a result of climate change, and birds will have to cope with greater food variability, unsuitable habitats, different predators, parasites and diseases, and competition. Nomadic species, such as Stark’s Lark, may find it easier to cope, only having to decide where to go. But resident species, like Sclater’s Lark and Red Lark, are more likely to remain in their patch and use available resources as best they can. Large, mainly resident species that depend on rainfall are also at risk. They would include territorial eagles, such as Verreauxs’ Eagle and Martial Eagle. Certain behavioural traits of these birds, such as extended parental care and slow reproductive rates, are likely to increase their vulnerability to climate change.  

    Other significant threats are the development of new mines in and adjacent to the IBA, the expansion of irrigation along the Orange River, the extensive invasion of mesquite (Prosopis sp.) along the Orange River banks and drainage lines, and new power lines and transmission lines from substations to renewable energy facilities.

    The lack of monitoring, formal protection and a management plan for this IBA is cause for concern.

    Conservation action

    Currently no part of the IBA is formally conserved. Recommendations were made in 1992 that a bequest, under the administration of WWF-SA, be used to purchase land in this region for formal protection. However, this opportunity was lost.

    Sections of this IBA are privately protected in the Black Mountain Mine Nature Reserve and on the farm Haramoep, covering approximately 23 000 ha of mine holdings around Aggeneys. All livestock was removed from these farms to reduce grazing impact and game species were introduced into the nature reserve. However, these fragmented conservation areas are not sufficient to maintain viable populations of many of the trigger species represented.

    Black Mountain Mine, owned by Vedanta Resources, must establish a 30 000-ha biodiversity offset to compensate for the loss of biodiversity as a result of the mining of the neighbouring Gamsberg inselberg. The area recommended for this offset includes a large part of this IBA and it must be formally protected under NEM:PAA. Future considerations for conservation action include extensions to this IBA and linkages to the Mattheus-Gat Conservation Area (SA034) and Bitterputs Conservation Area (SA036) IBAs.

    Related webpages

    None.

    Contact

    If you have any information about the IBA, such as a new threat that could impact on it, please send an e-mail to iba@birdlife.org.za or call BirdLife South Africa +27 (11) 789 1122.

    Page last updated

    Wednesday, 28 January 2015

    Further Reading

    Barnes K (ed.). 1998. The Important Bird Areas of southern Africa. Johannesburg: BirdLife South Africa.

    BGIS online. 2014. Biodiversity GIS, SANBI. Available at www.bgis.sanbi.org [accessed September 2014].

    BirdLife International. 2014. Species factsheet:Certhilauda burra. Available at www.birdlife.org [accessed September 2014].

    BirdLife International and Durham University. 2014. Species climate change impacts factsheet: Certhilauda burra. Available at www.birdlife.org [accessed September 2014].

    Botha M, Desmet P, Brownlie S. 2013. Draft scope Gamsberg biodiversity offset. Report for Vedanta Resources.

    DEA. 2014. Renewable Energy EIA Application Database. Available at http://egis.environment.gov.za/frontpage.aspx?m=27 [accessed 5 October 2014].

    Dean WRJ. 1989. The nest, egg and nestlings of the Red Lark Certhilauda burra. Ostrich 60: 158.

    Dean WRJ. 1993. The Red Lark in the greenhouse world. African Wildlife 47(5): 211–214.

    Dean WRJ. 1995. Where birds are rare or fill the air: the protection of the endemic and nomadic avifaunas of the Karoo. PhD thesis. Percy FitzPatrick Institute of African Ornithology, University of Cape Town.

    Dean WRJ. 1997. The distribution and biology of nomadic birds in the Karoo, South Africa. Journal of Biogeography 24: 769–779.

    Dean WRJ, Barnard P, Anderson MD. 2009. When to stay and when to go: trade-offs for southern African arid-zone birds in times of drought. South African Journal of Science 105: 24–28.

    Dean WRJ, Hockey PAR. 1989. An ecological perspective of lark (Alaudidae) distribution and diversity in the southwest arid zone of Africa. Ostrich 60: 27–34.

    Dean WRJ, Lombard AT. 1994. The protection of nomadic birds in the semi-arid Karoo: the problems of stochastic rainfall and patchy habitat use by larks. Journal für Ornithologie 135: 281.

    Dean WRJ, Milton SJ, Watkeys MK, Hockey PAR. 1991. Distribution, habitat preference and conservation status of the Red Lark Certhilauda burra in Cape Province, South Africa. Biological Conservation 58: 257–274.

    Dean WRJ, Siegfried WR. 1997. The protection of endemic and nomadic avian diversity in the Karoo, South Africa. SA Journal of Wildlife Research 27: 11–21.

    Dean WRJ, Williams JB. 2004. Adaptations of birds for life in deserts with particular reference to larks (Alaudidae). Transactions of the Royal Society of South Africa 59(2): 79–91.

    Du Plessis MA. 1992. A strategic plan for the conservation of the avifauna of the Western Cape region, South Africa. A report to the Southern African Nature Foundation. Cape Town: Percy FitzPatrick Institute of African Ornithology.

    Githaiga-Mwicigi JMW, Fairbanks DHK, Midgley G. 2002. Hierarchical processes define spatial pattern of avian assemblages restricted and endemic to the arid Karoo, South Africa. Journal of Biogeography 29: 1067–1087.

    Hole DG, Willis SG, Pain DJ, Fishpool LD, Butchart SHM, Collingham YC, Rahbek C, Huntley B. 2009. Projected impacts of climate change on a continental-wide protected area network. Ecology Letters 12: 420–431.

    Jenkins AR, Shaw JM, Smallie JJ, Gibbons B, Visagie R, Ryan PG. 2011. Estimating the impacts of power line collisions on Ludwig’s Bustards Neotis ludwigii. Bird Conservation International 21: 303–310.

    Lloyd P. 1999. Rainfall as a stimulus to breeding and a determinant of clutch size in arid-zone birds. Ibis 141: 637–643.

    Midgley G, Rutherford M, Bond W. 2001. The heat is on… Impacts of climate change on plant diversity in South Africa. Cape Town: National Botanical Institute.

    Milton SJ, Dean WRJ. 2000. Disturbance, drought and dynamics of desert dune grassland, South Africa. Plant Ecology 150: 37–51.

    Mucina L, Rutherford MC (eds). 2006. The vegetation of South Africa, Lesotho and Swaziland. Strelitzia 19. Pretoria: South African National Biodiversity Institute.

    Namakwa District Biodiversity Sector Plan. 2008. Department of Tourism, Environment and Conservation Northern Cape, Conservation International SA & Botanical Society of SA.

    Pretorius M. 2014. Proposed 75MW AES photovoltaic installation near Aggeneys, Northern Cape Province. Avifaunal Impact Assessment. Unpublished report.

    Simmons RE, Barnard P, Dean WRJ, Midgley GF, Thuiller W, Hughes G. 2004. Climate change and birds: perspectives and prospects from southern Africa. Ostrich 75(4): 295–308.

    Todd S, Milton SJ, Dean WRJ, Carrick P, Meyer A. 2009. Ecological best-practice livestock production guidelines for the Namakwa District. Botanical Society of SA and CEPF.

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