From: Subject: issg Database: Impact Information for Acridotheres tristis Date: Wed, 16 Jul 2008 14:28:49 +1000 MIME-Version: 1.0 Content-Type: multipart/related; type="text/html"; boundary="----=_NextPart_000_0000_01C8E750.43AFE520" X-MimeOLE: Produced By Microsoft MimeOLE V6.00.2900.3198 This is a multi-part message in MIME format. ------=_NextPart_000_0000_01C8E750.43AFE520 Content-Type: text/html; charset="iso-8859-1" Content-Transfer-Encoding: quoted-printable Content-Location: http://www.issg.org/database/species/impact_info.asp?si=108&fr=1&sts=sss issg Database: Impact Information for Acridotheres = tristis
3D"List
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   Acridotheres tristis = (bird)  
Ecology=20 Distribution=20 Management=20
Info 		Impact =
Info 		References=20
and Links = 		Contacts=20


         Gen= eral=20 Impact

    Acridotheres = tristis may=20 prey on the eggs and nestlings of other = birds and=20 aggressively defend territories and nesting = sites,=20 which is obviously of great concern if = native bird=20 species are affected. This has been = particularly=20 concerning in Australia where hollows are in = short=20 supply (due to the clearing of large tracts = of bush=20 for agriculture) and there have even been=20 observations of mynas filling up any nearby = vacant=20 nesting hollows with rubbish to discourage = other=20 birds from nesting in their territory = (Tidemann=20 2005; Thomas 2004). In New Zealand feral = pigeons,=20 silver and southern black-backed or kelp = gulls and=20 small passerine species are affected = (Thomson 1922;=20 Oliver 1955; Wodzicki 1965). In Australia=20 Acridotheres tristis will even evict = large=20 birds, such as kookaburras and dollar birds = and=20 small mammals, such as sugar gliders, from = their=20 nests (Tidemann 2005). Mynas may also = exhibit=20 =93mobbing=94 behaviour against birds or = mammals (which=20 is a problem in Australia, where native = opossums are=20 affected) (Tidemann 2005).=20

    Mynas may consume grapes, apricots, = apples,=20 pears, strawberries, gooseberries and other = fruit,=20 damaging food crops (Heather and Robertson = 1997).=20

    Mynas may be a source of annoyance to = humans due=20 to their communal roosting behaviour; = especially in=20 highly populated areas. In Singapore, for = example,=20 the common myna and the white-vented myna = (A.=20 javanicus) form a combined estimated = population=20 of around 160,000 (Lim Sodhi Brook and Soh = 2003). In=20 such high densities mynas have proved to be = a human=20 nuisance. The disruptive noise and fouling = of the=20 environment through droppings and other = associated=20 mess cause a variety of problems (Yap et = al.=20 20002, in Lim Sodhi Brook and Soh 2003). In = Fiji=20 they have also proven to be a residential = nuisance=20 as they build nests in spouting and = drainpipes=20 (Stoner 1923). Mynas fearlessly steal food = from=20 plates in cafes and restaurants, which is a = hygiene=20 or general nuisance problem. It has been = considered=20 that they may also spread mites and diseases = that=20 affect people and farmstock (Tidemann 2005). = Specimens in Fiji have been identified as = carrying=20 owl flies, biting lice, thread worms (of a = species=20 of Oxyspirrura) and round worm = (Stoner 1923).=20 Presumably, populations of the bird may = provide=20 reservoirs of a disease that affects native = birds,=20 while themselves remaining largely=20 unaffected.




        &nbs= p;Location=20 Specific Impacts:
    Australia  
    Agricultural: Common = Indian=20 mynas (Acridotheres tristis) cause = some=20 depredation on fruit, especially figs (Frith = 1979)
    Mangaia Is. = (Cook=20 Islands)  
    Competition: Mynas = negatively=20 effect native biodiversity by competing for = nesting=20 holes, preying on chicks and eggs and = evicting small=20 mammals. The myna poses a particular threat = to=20 Mangaia=92s endemic vulnerable Mangaia = kingfisher (see=20 T= odiramphus=20 ruficollaris in the IUCN Red List of = Threatened=20 Species). Anecdotal evidence = indicates that=20 the kingfisher cannot breed successfully = outside the=20 small areas of Barringtonia asiatica = forest=20 on Mangaia because of interference from the=20 myna.
    Fiji  
    Competition: Mynas = are great=20 adaptors to local food sources, which they = can=20 exploit very effectively to their advantage. = In=20 Fiji, the seashore along the main street in = Suva=20 (the capital) attracts hundreds of mynas at = low=20 tide, that proceed to feast on worms, = molluscs,=20 crustaceans and other seafood that has been = stranded=20 on the mud flats (Stoner 1923). Presumably = this=20 limits potential sources of food for native=20 seabirds.
    Disease=20 transmission: Mynas in Fiji have been = identified=20 as carrying owl flies, biting lice, thread = worms (of=20 a species of Oxyspirrura) and round = worm=20 (Stoner 1923). Presumably, populations of = the bird=20 may provide reservoirs of a disease that = affects=20 native birds, while themselves remaining = largely=20 unaffected.
    Human=20 nuisance: Described as =93thrifty=94 and = =93pugnacious=94 the myna has the annoying = habit of=20 building nests in and around human = habitations which=20 may cause house keeping problems, for = example when=20 they construct nests in spouting and drain=20 pipes.
    Predation:=20 Common Indian mynas (Acridotheres = tristis)=20 have been reported to predate on the eggs = and young=20 of terns (Sterna spp.) and noddies=20 (Anous spp.) as recorded by Pernetta = and=20 Watling (1978). They also recorded agonistic = behaviour by naturalised red-vented bulbuls = (Pycnonotus=20 cafer) with the common myna (amongst = other=20 species, including jungle myna (Acridotheres=20 fuscus). In a form of role-reversal, = the two=20 mynas were themselves observed initiating = attacks on=20 bulbuls.
    Hiva Oa Is. = (French=20 Polynesia (Polyn=E9sie Fran=E7aise))  
    Other: It is = possible that=20 common mynas may have contributed to the = decline of=20 the red-moustached fruit dove and the = Marquesas=20 warbler by stealing their nests. Cave = swiftlets=20 (Collocalia spp.), on whose eggs = common mynas=20 are known to prey, are rare or absent = (Holyoak and=20 Thibault 1984, Seitre and Seitre = 1992).
    Predation
    French Polynesia = (Polyn=E9sie=20 Fran=E7aise)    
    Interaction with other = invasive=20 species: Acridotheres tristis is=20 suspected of contributing to the spread of = invasive=20 alien plants by consuming their = fruit.
    Predation: = Acridotheres=20 tristis is able of consuming the eggs or = young=20 native birds such as the Tahiti swiftlet=20 (Collocalia leucocephalus) (Holyoak = and=20 Thibault 1984, Seitre and Seitre = 1992).
    Threat to endangered = species:=20 Acridotheres tristis is suspected of = having=20 contributed to the exclusion of certain = species that=20 are endemic to the Marquesas such as = Acrocephalus=20 caffer mendanae or Ptilinopus=20 dupetitthouarsii. It represents a major = threat=20 to the Tahiti monarch, a species classified = as=20 Critically Endangered by IUCN (see Pomar= ea=20 nigra in the IUCN Red List of Threatened = Species) (Blanvillain et al.,=20 2003).
    Moorea Is. = (French=20 Polynesia (Polyn=E9sie Fran=E7aise))  
    Predation: Cave = swiftlets=20 (Collocalia spp.), on whose eggs = common mynas=20 are known to prey, are rare or absent = (Holyoak and=20 Thibault 1984, Seitre and Seitre = 1992).
    Reduction in native=20 biodiversity: Mynas may have contributed = to the=20 decline of the long-billed reed warbler = (Holyoak and=20 Thibault 1984)
    Tahiti Is. = (French=20 Polynesia (Polyn=E9sie Fran=E7aise))  
    Agricultural: In = Tahiti, mynas=20 eat cultivated fruits (Holyoak = 1974).
    Predation: Cave = swiftlets=20 (Collocalia spp.), on whose eggs = common mynas=20 are known to prey, are rare or absent = (Holyoak and=20 Thibault 1984, Seitre and Seitre = 1992).
    Tel Aviv = (Israel)  
    Competition: Mynas = were=20 observed taking over an active nest of a = Syrian=20 woodpecker (Dendrocopus=20 syriacus).
    Human=20 nuisance: One roosting site included = around 200=20 mynas, as well as other bird species, = situated in a=20 botanical garden over a public footpath = (causing=20 fouling problems).
    Unknown: Since mynas = are a=20 relatively new invasive species to the = region, and=20 most of the population is in man-made = habitat, it is=20 too early to evaluate the actual and future=20 impacts.
    Mauritius  
    Competition: In = Mauritius,=20 where they are now the most adundant bird = species,=20 common mynas compete successfully for = nesting sites=20 with the endangered and endemic Mauritius or = echo=20 parakeet (see Psittacula=20 eques in IUCN Red List of Threatened=20 Species) (Long 1981, Lever = 1987).
    Grand Terre Is. (New=20 Caledonia) (New Caledonia = (Nouvelle=20 Cal=E9donie))    
    Competition: = Acridotheres=20 tristis is believed to compete with = local bird=20 species for food and nesting sites (Pascal = et=20 al., 2006).
    Interaction with other = invasive=20 species: Acridotheres tristis = probably=20 played a key role in the massive extension = of Lantana=20 camara (Virot, 1956 in Gargominy = et=20 al., 1996)
    New = Zealand  
    Competition: In New = Zealand=20 mynas prey on the eggs and nestlings of = feral=20 pigeons, silver and southern black-backed or = kelp=20 gulls, as well as those of the small native = and=20 introduced passerines (Thomson 1922, Oliver = 1955,=20 Wodzicki 1965).
    Reunion (La=20 R=E9union)  
    Economic/Livelihoods: Mynas=20 cause damage to fruits and affect=20 production.
    Interaction with other = invasive=20 species: Concerns have been raised on = the role=20 of mynas in the dissemination of exotic=20 weeds.
    Reunion (La=20 R=E9union)    
    Interaction with other = invasive=20 species: Acridotheres tristis is=20 suspected of contributing to the spread of = invasive=20 alien plants by consuming their = fruit.
    Ascension Is. = (Saint=20 Helena)  
    Predation: = Acridotheres=20 tristis predate extensively on sooty = tern eggs=20 (Sterna fuscuta) (Hughes, 2004 in = Varnham,=20 2006), there are reports that probably they = cause=20 more predation on sooty tern eggs than=20 rats.
    Saint = Helena  
    Competition: = Acridotheres=20 tristis competes with endemic wirebird=20 (Chardrius sanctae helenae) for = invertebrate=20 prey (McCulloch and Norris, undated in = Varnham,=20 2006).
    Interaction=20 with other invasive species: = Acridotheres=20 tristis depredates fruit trees and other = crops.=20 It is a major dispersal agent for invasive = exotic=20 plant species such as Opuntia=20 stricta and Lantana=20 camara. A. tristis is = implicated in=20 the spread of the invasive shrub wild = currant=20 (Ashmole and Ashmole, 2000 in Varnham, 2006) = and in=20 the spread of non-native Bermuda cedar = (Rowlands=20 et al., 1998 in Varnham, = 2006).
    Predation: = Acridotheres=20 tristis may raid wirebird (Chardrius = sanctae=20 helenae) nests and eat hatchlings and = eggs=20 (known to predate nests of other small = birds)=20 (McCulloch and Norris, undated in Varnham,=20 2006).
    Seychelles  
    Threat to endangered = species:=20 Newton (1867) suggested that competition = with mynas=20 may have contributed to the decline of the=20 Seychelles magpie robin (see Copsychus=20 sechellarum in IUCN Red List of = Threatened=20 Species).
    Singapore  
    Fouling: Large = communal roosts=20 of mynas in urban environments cause = problems; the=20 noisy cheeky and intelligent bird increases = noise=20 pollution and also fouls the environment by=20 depositing unhygienic droppings and creating = other=20 litter (Yap et al.. 20002, in Lim = Sodhi Brook=20 and Soh 2003).
    Reduction in native=20 biodiversity: The decline of the native=20 hole-nesting oriental magpie robin = (Copsychus=20 saularis) in Singapore has been = hypothesised to=20 be linked to the presence of exotic mynas = (Huong=20 & Sodhi 1997, in Lim Sodhi Brook and Soh = 2003).
    Hawaii (Hawai=91i) = Is.=20 (United States (USA))  
    Interaction with other = invasive=20 species: The common myna has aided the = spread of=20 lantana (Lantana=20 camara) seeds - which is an invasive = plant=20 threatening the sustainability of native = Hawaiian=20 flora.
    Hawaiian = Islands (United=20 States (USA))  
    Interaction with other = invasive=20 species: Mynas indirectly affect the=20 environment, largely through the dispersal = of seeds.=20 In 1858 the ornamental plant Lantana=20 camara was introduced from Mexico = (where it=20 is harmless) to gardens in the Hawai=91ian = Islands,=20 where before long, common mynas were eating = the=20 berries (which were ignored by native = species) to=20 such an extent that correlative fluctuations = were=20 noticed in the abundance of fruits and = mynas, the=20 latter spreading the seeds (the germination = of which=20 is said to be increased by their passage = through the=20 bird) until rank growths of lantana became = an=20 agricultural nuisance (notes from Lever = 1987:=20 497=96498).
    Predation: Byrd = (1979)=20 considered that common mynas may be = significant=20 predators of the eggs of wedge-tailed = shearwaters=20 (see Puffinus=20 pacificus in IUCN Red List of Threatened = Species) in the Hawai=91ian Islands, = where in his=20 study on Kauai some 23% of shearwater eggs = were=20 destroyed (notes from Lever 1987:=20 = 497=96498).


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3DISSG3D"Landcare3DIUCN=20 The Global Invasive Species = Database is=20 managed by the Invasive Species Specialist Group = (ISSG)=20 of the IUCN Species Survival Commission. It was=20 developed as part of the global initiative on = invasive=20 species led by the Global Invasive Species = Programme=20 (GISP) and is supported through partnerships = with the=20 National Biological Information Infrastructure, = Manaaki=20 Whenua-Landcare Research and the University of = Auckland.=20 Conditions of=20 = use.
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BORDER-LEFT-COLOR: white; = BORDER-BOTTOM-COLOR: white; COLOR: teal; BORDER-TOP-COLOR: white; = FONT-STYLE: italic; FONT-FAMILY: "arial" sans-serif small; = BACKGROUND-COLOR: white; BORDER-RIGHT-COLOR: white } .Body { BACKGROUND-COLOR: #f0f8ff } .unnamed1 { FONT-SIZE: 11px; LINE-HEIGHT: 19px; FONT-FAMILY: Verdana, Arial, = Helvetica, sans-serif } .unnamed2 { FONT-SIZE: 11px; LINE-HEIGHT: 8px; FONT-FAMILY: Verdana, Arial, = Helvetica, sans-serif } .footer { FONT-SIZE: 10px; COLOR: #f1f1f1; FONT-FAMILY: Verdana, Arial, = Helvetica, sans-serif } ------=_NextPart_000_0000_01C8E750.43AFE520 Content-Type: application/octet-stream Content-Transfer-Encoding: quoted-printable Content-Location: http://www.issg.org/database/js/ISSG.js /* DESC: Javascript routines for ISSG website AUTH: RP VERS: 1.0 DATE: 21 Mar 2000 To use the functions provided in this file add the following inside the section of your HTML page: */ function showPopupImage(imageID,imageWidth,imageHeight,imageTypeCode) { newWindow =3D window.open('../image.asp?ii=3D' + imageID + '&ic=3D' + = imageTypeCode, 'issgimage' + imageID, = "toolbar=3D0,"+"location=3D0,"+"directories=3D0,"+"status=3D0,"+"menubar=3D= 0,"+"scrollbars=3D0,"+"resizable=3D0,"+"width=3D"+imageWidth+",height=3D"= +(imageHeight+50)+",left=3D100,top=3D180") } ------=_NextPart_000_0000_01C8E750.43AFE520 Content-Type: application/octet-stream Content-Transfer-Encoding: 7bit Content-Location: http://www.issg.org/database/js/list.js /* DESC: Javascript list handling routines AUTH: RP VERS: 1.0 DATE: 11 Oct 99 To use the functions provided in this file add the following inside the section of your HTML page: */ function selectListItem(lst, sValue) //selects the item on the list with value=sValue if it exists. { var i; i = getListItemIndex(lst, sValue); if (i > -1) lst.selectedIndex = i; } function getListItemIndex(lst, sValue) //returns the index of the item on the list with value=sValue { var i; for (i=0 ;i