the striated babbler ( turdoides earlei ) is a species of bird in the family leiothrichidae .

it is found in southern asia from pakistan to myanmar .

striated babbler

striated babbler : many types of calls given by an early morning foraging party of about 10 individuals .
babbler , nondescript in shades of pale brown and buff with heavy streaking above , lighter below . . . .
collar , n . & robson , c . ( 2018 ) . striated babbler ( argya earlei ) . in : del hoyo , j . , elliott , a . , sargatal , j . , christie , d . a . & de juana , e . ( eds . ) . handbook of the birds of the world alive . lynx edicions , barcelona . ( retrieved from urltoken on 9 july 2018 ) .
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del hoyo , j . , collar , n . j . , christie , d . a . , elliott , a . , fishpool , l . d . c . , boesman , p . and kirwan , g . m . 2016 . hbw and birdlife international illustrated checklist of the birds of the world . volume 2 : passerines . lynx edicions and birdlife international , barcelona , spain and cambridge , uk .
justification : this species has a very large range , and hence does not approach the thresholds for vulnerable under the range size criterion ( extent of occurrence < 20 , 000 km2 combined with a declining or fluctuating range size , habitat extent / quality , or population size and a small number of locations or severe fragmentation ) . despite the fact that the population trend appears to be decreasing , the decline is not believed to be sufficiently rapid to approach the thresholds for vulnerable under the population trend criterion ( > 30 % decline over ten years or three generations ) . the population size has not been quantified , but it is not believed to approach the thresholds for vulnerable under the population size criterion ( < 10 , 000 mature individuals with a continuing decline estimated to be > 10 % in ten years or three generations , or with a specified population structure ) . for these reasons the species is evaluated as least concern .
the global population size has not been quantified , but the species is reported to be locally common ( grewal et al . 2002 ) . trend justification : the population is suspected to be in decline owing to ongoing habitat destruction and fragmentation .
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( koelz , 1954 ) – pakistan ( r indus plains ) and nw india ( punjab ) .
( blyth , 1844 ) – n india ( haryana e to n bihar and from west bengal s to ne odisha , also in assam and manipur ) , s nepal , bangladesh and sw , c & s myanmar .
song thought to be a loud , repeated series of “tiew - tiew - tiew - tiew” , interspersed with “quip - quip - . . .
insects , snails and some vegetable matter . found in flocks of 7–10 or more individuals , even during breeding season . does not descend . . .
all year , mainly mar–oct ; multi - brooded . co - operative breeder . nest a rather massive but neat and compact cup ( smaller and more . . .
not globally threatened . common and widespread in pakistan , including in dera ismail khan district . locally common in e nepal , uncommon elsewhere in country . locally common . . .
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tentatively separated from turdoides # r ; genetic screening of at least some component taxa required .
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this species has a very large range , and hence does not approach the thresholds for vulnerable under the range size criterion ( extent of occurrence < 20 , 000 km2 combined with a declining or fluctuating range size , habitat extent / quality , or population size and a small number of locations or severe fragmentation ) . despite the fact that the population trend appears to be decreasing , the decline is not believed to be sufficiently rapid to approach the thresholds for vulnerable under the population trend criterion ( > 30 % decline over ten years or three generations ) . the population size has not been quantified , but it is not believed to approach the thresholds for vulnerable under the population size criterion ( < 10 , 000 mature individuals with a continuing decline estimated to be > 10 % in ten years or three generations , or with a specified population structure ) . for these reasons the species is evaluated as least concern .
recommended citation birdlife international ( 2018 ) species factsheet : argya earlei . downloaded from urltoken on 09 / 07 / 2018 . recommended citation for factsheets for more than one species : birdlife international ( 2018 ) iucn red list for birds . downloaded from urltoken on 09 / 07 / 2018 .
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adhemarius mexicanus is a species of moth in the family sphingidae .

it was described by balcázar-lara and beutelspacher , in 2001 , and is known from mexico , where it is found from oaxaca to jalisco .

adhemarius mexicanus

sphingidae , adhemarius sp . , in my eyes it is either adhemarius dariensis or adhemarius mexicanus . not really sure about the species , they look very similar . urltoken urltoken i try to get closer . . .
adhemarius globifer is a species of moth in the family sphingidae . it was described by dyar and 1912 , and is found from mexico to southern arizona . adults are probably on wing year round . . . .
: jalisco ; to puebla : patla ; veracruz : jalapa ; and oaxaca .
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indicate a specimen locale , and those which end in
i
, pronounced
eye
, honour a contempory friend / collector / etc .
, possibly chose the name from adhemarus , the fifth and last of the old counts of querci ( verdun , france ) who died in 880 ad .
probably produces at least two broods annually . hubert mayer reports a july flight in patla , puebla , mexico .
listed below are primary food plant ( s ) and alternate food plants . it is hoped that this alphabetical listing followed by the common name of the foodplant will prove useful . the list is not exhaustive . experimenting with closely related foodplants is worthwhile .
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the ouachita madtom ( noturus lachneri ) is a catfish of the family ictaluridae.the first specimens of the species were collected in 1952 it was not until 1969 that they were recognised as a species .

the ouachita madtom is similar to the tadpole madtom except the ouachita madtom has one internasal pore while the tadpole madtom has two , and 16 to 18 anal rays while the tadpole madtom has only 14 to 16 .

it is also similar to the slender madtom but differing in the sack of serrae on the pectoral spine , having more caudal rays , and usually eight pectoral rays while the slender madtom has 9 .

the maximum length of an ouachita madtom is about 2.7 inches .

ouachita madtom

information on the ouachita madtom is currently being researched and written and will appear here shortly .
the ouachita madtom is classified as endangered ( en ) on the iucn red list ( 1 ) .
growth and reproduction in the ouachita madtom
by r . tumilson and j . o . hardage
feeding and reproductive biology of ouachita madtom ( joseph n . stoeckel , charles j . gagen , and richard w . standadge )
ouachita madtom noturus lachneri taylor 1969 identification : the ouachita madtom is similar to the tadpole madtom , noturus gyrinus , but can be distinguished by its shorter , flatter head and its more slender body . the body is tan , dark gray or brown above and white below . the fins sometimes have dark borders . to 4 in . ( 10 cm ) total length . range : the ouachita madtom is found in the upper saline river system and in an adjacent small tributary of the ouachita river in central arkansas . this species is uncommon . habitat : the ouachita madtom inhabits flowing rocky pools and runs of creeks and small rivers . similar species : the tadpole madtom , noturus gyrinus , has a longer and more rounded head , and a chubbier body .
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robison , h . w . , and g . l . harp . 1985 . distribution , habitat and food of the ouachita madtom , noturus lachneri , a ouachita river drainage endemic . copeia 1985 : 216 - 220 .
gagen , c . j . , r . w . standage , and j . n . stoeckel . 1998 . ouachita madtom ( noturus lachneri ) metapopulation dynamics in intermittent ouachita mountain streams . copeia 1998 : 874 - 882 .
( burr and warren 1986 ) . the least madtom is abundant and stable in
topminnow as from the ouachita r . dr . , louisiana , north to ( lake
the neosho madtom and the multifaceted nature of population limiting factors ( mark l . wildhaber )
scientists recently proposed that 17 species including the ouachita madtom , a whiskery fish found in arkansas , be removed from a petition that had called for its protection under the endangered species act .
filters and templates : stonefly ( plecoptera ) richness in ouachita mountains streams , u . s . a
status assessment of the carolina madtom : a rare north carolina epidemic ( christopher j . wood and robert b . nichols )
tumilson , r . and hardage , j . o . ( 2014 )
growth and reproduction in the ouachita madtom ( noturus lachneri ) at the periphery of its distribution ,
journal of the arkansas academy of science : vol . 68 , article 19 . available at : urltoken
[ conservation , management , and ecology of nongame catfish ] control of gonadal maturation of the margined madtom ( joseph n . stoeckel and richard j . neves )
the ouachita madtom was the only madtom from arkansas to be captively propagated at cfi . international paper funded an effort to determine whether this madtom species from the saline river system near hot springs was relatively more or less difficult to captively spawn than other species that cfi has attempted . three nests were spawned and the young reared with varying success to produce more than 60 young madtoms . these efforts reinforced previous findings that suggest that a wide range of variation exists in the ease with which different madtom species will spawn in captivity . most upland species have proven more difficult than larger river and lowland species , although the reasons are still unclear . many of the excess propagated individuals were utilized in 2008 for electrofishing injury experiments by russ bohl ( university of tennessee , knoxville ) . in fall 2009 , all surviving individuals ( n = 22 ) were transferred to the chattahoochee national fish hatchery , ga .
the ouachita madtom , noturus lachneri , is a small , uniformly - colored catfish endemic to the upper saline and ouachita river drainages in central arkansas ( robison and buchanan , 1988 ) , where it is often found in shallow pools associated with clear , high gradient , rock - bottomed streams ( robison and harp , 1985 ) . distribution , habitat , diet , and conservation status of n . lachneri . were examined by robison and harp ( 1985 ) . however , information on parasites of this endemic species has not been reported . herein , we report on species richness and mean abundance of hehninth parasites of n . lachneri .
the ouachita madtom ( noturus lachneri ) occurs primarily in drainages of the upper saline river and in a few small tributaries to the ouachita river in arkansas , usa . we collected specimens by hand and by use of aquarium dipnets on 29 occasions from 20 october 1999 through 25 july 2000 in cooper creek , presently a feeder creek into lake catherine on the ouachita river . total length was measured , reproductive attributes were noted , and individuals were released at the capture site ( with exception of 3 gravid females retained to assess fecundity ) . we recognized 2 age ( size ) classes during most of the year based on a plot of length - frequency distributions . regression of total length against time indicated a mean growth rate of 0 . 14 mm / day for the population , and 0 . 20 mm / day for juveniles during warmer months . hatchlings were found from 27 june through 4 november .
thomas , m . r . , burr , b . m . , 2004 . noturus gladiator , a new species of madtom ( siluriformes : ictaluridae ) from coastal plain streams of tennessee and mississippi . ichthyol . explor . freshwaters 15 : 351 - 368 .
ouachita madtoms ( noturus lachneri ) at conservation fisheries , a native stream fish breeding center in knoxville . this is a rare stream fish that has a limited range in arkansas and is listed as vulnerable on the iucn red list , but it still isn’t listed under the esa .
fiorillo , riccardo a . ; thomas , r . brent ; warren , melvin l . , jr . ; taylor , christopher m . 1999 . structure of the helminth assemblage of and endemic madtom catfish ( noturus lachneri ) . the southwestern naturalist , vol . 44 , no . 4 , december 1999
distinctive ; clearly differentiated by several characters ( see starnes 1995 ) . see grady and legrande ( 1992 ) for a study of phylogenetic relationships , modes of speciation , and historical biogeography of noturus madtom catfishes . see lundberg ( 1992 ) for a synthesis of recent work on the systematic relationships of ictalurid catfishes .
bridge repair and construction have decimated local populations . commercial gravel operations , stream channelization , and clearcut logging have degraded habitat ( robison and buchanan 1988 ) . impoundments for a water supply for little rock and benton are a potential threat ( robison and buchanan 1988 ) . ouachita madtoms and associated fishes apparently die in substantial numbers as streams dry in summer , so these communities potentially could be impacted by land management practices that increase the extent of stream drying , through alterations of the hydrologic regime ( e . g . , diversions for drinking water , irrigation ) ( gagen et al . 1998 ) . land management practices that increase sediment load may decrease pool depth thereby reducing source habitat for riffle - dwelling species as well as reducing habitat for pool - dwelling species such as the ouachita madtom ( gagen et al . 1998 ) . unintentional barriers to fish passage , such as low - water road crossings could significantly affect fish community structure by altering the natural recolonization dynamics in intermittent streams ( gagen et al . 1998 ) .
bridge repair and construction have decimated local populations . commercial gravel operations , stream channelization , and clearcut logging have degraded habitat ( robison and buchanan 1988 ) . impoundments for a water supply for little rock and benton are a potential threat ( robison and buchanan 1988 ) . ouachita madtoms and associated fishes apparently die in substantial numbers as streams dry in summer , so these communities potentially could be impacted by land management practices that increase the extent of stream drying , through alterations of the hydrologic regime ( e . g . , diversions for drinking water , irrigation ) ( gagen et al . 1998 ) . land management practices that increase sediment load may decrease pool depth thereby reducing source habitat for riffle - dwelling species as well as reducing habitat for pool - dwelling species such as the ouachita madtom ( gagen et al . 1998 ) . unintentional barriers to fish passage , such as low - water road crossings could significantly affect fish community structure by altering the natural recolonization dynamics in intermittent streams ( gagen et al . 1998 ) .
total adult population size is unknown but likely exceeds 10 , 000 . this species has been reported as never abundant at any locality within its range ( robison and harp 1985 ) , or rare to uncommon ( page and burr 2011 ) , but gagen et al . ( 1998 ) found high population densities of ouachita madtoms in several tributaries to the alum fork of the saline river .
grady , j . m . , and w . h . legrande . 1992 . phylogenetic relationships , modes of speciation , and historical biogeography of the madtom catfishes , genus noturus rafinesque ( siluriformes : ictaluridae ) . pages 747 - 777 in r . l . mayden , editor . systematics , historical ecology , and north american freshwater fishes . stanford university press , stanford , california . xxvi + 969 pp .
the small , discontinuous range is restricted to the upper saline river system and a small unnamed tributary of the ouachita river below remmel dam , in central arkansas ( robison and buchanan 1988 , page and burr 2011 . see robison and harp ( 1985 ) for localities . range extent is not more than a couple hundred square kilometres ( e . g . , see map in robison and harp 1985 ) . range may be severely fragmented .
the small , discontinuous range is restricted to the upper saline river system and a small unnamed tributary of the ouachita river below remmel dam , in central arkansas ( robison and buchanan 1988 , page and burr 2011 . see robison and harp ( 1985 ) for localities . range extent is not more than a couple hundred square kilometers ( e . g . , see map in robison and harp 1985 ) . range may be severely fragmented .
( 250 - 1000 square km ( about 100 - 400 square miles ) ) the small , discontinuous range is restricted to the upper saline river system and a small unnamed tributary of the ouachita river below remmel dam , in central arkansas ( robison and buchanan 1988 , page and burr 2011 . see robison and harp ( 1985 ) for localities . range extent is not more than a couple hundred square kilometers ( e . g . , see map in robison and harp 1985 ) . range may be severely fragmented .
this species is represented by a small number of occurrences ( subpopulations ) . robison and harp ( 1985 ) mapped 17 collection sites that represent probably more than 10 but not more than 15 distinct occurrences . total adult population size is unknown but probably exceeds 10 , 000 . this species has been reported as never abundant at any locality within its range ( robison and harp 1985 ) , or rare to uncommon ( page and burr 2011 ) , but gagen et al . ( 1998 ) found high population densities of ouachita madtoms in several tributaries to the alum fork of the saline river . extent of occurrence , area of occupancy , and number of subpopulations apparently have not decreased by more than 25 % compared to the historical situation . trend in population size is unknown . warren et al . ( 2000 ) and jelks et al . ( 2008 ) categorized the status as
threatened
( not
currently stable
) . trends are not well documented , but this species may be declining . some local extirpations may be temporary . for example , madtoms can rapidly recolonize from large , deep pools stream reaches from which they have been extirpated as a result of drought ( gagen et al . 1998 ) .
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taylor , w . r . 1969 . a revision of the catfish genus noturus ( rafinesque ) with an analysis of higher groups in the ictaluridae . smithsonian institution , u . s . national museum bulletin 282 : 1 - 315 .
justification : this species is listed as endangered because its extent of occurrence is less than 1 , 000 sq km , area of occupancy is less than 500 sq km , distribution may be severely fragmented , and habitat quality is subject to ongoing degradation .
this species is characteristic of pools , backwaters , and runs of creeks and small rivers ( page and burr 2011 ) of moderate to high gradient , with clear , cool water , gravel - rubble - sand bottoms , and alternating pools and riffles . usually it occurs in shallow pools , buried in gravel / cobble or in debris and vegetation along edges , sometimes in very shallow riffles under large rocks ( robison and allen 1995 ) . it may seek smaller tributaries for spawning . young have been found in a pool over shale bedrock in a small tributary ( robison and harp 1985 ) .
better information on abundance and population trend is needed . unpolluted , unsilted habitats should be maintained .
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r . tumilson , henderson state university follow j . o . hardage , henderson state university
robins , c . r . , r . m . bailey , c . e . bond , j . r . brooker , e . a . lachner , r . n . lea , and w . b . scott . 1991 . common and scientific names of fishes from the united states and canada . american fisheries society , special publication 20 . 183 pp .
small , fragmented range in arkansas ; threatened by degradation and loss of habitat from logging , commercial gravel operations , housing developments , and bridge / road building .
due to latency between updates made in state , provincial or other natureserve network databases and when they appear on natureserve explorer , for state or provincial information you may wish to contact the data steward in your jurisdiction to obtain the most current data . please refer to
known area of occupancy may be less than 100 square kilometers or not much more than this , particularly during periods of stream drying . .
this species is represented by a small number of occurrences ( subpopulations ) . robison and harp ( 1985 ) mapped 17 collection sites that represent probably more than 10 but not more than 15 distinct occurrences .
warren et al . ( 2000 ) and jelks et al . ( 2008 ) categorized the status as
threatened
( not
currently stable
) . trends are not well documented , but this species may be declining . some local extirpations may be temporary . for example , madtoms can rapidly recolonize from large , deep pools stream reaches from which they have been extirpated as a result of drought ( gagen et al . 1998 ) .
extent of occurrence , area of occupancy , and number of subpopulations apparently have not decreased by more than 25 % compared to the historical situation . trend in population size is unknown .
a slender , brownish to gray catfish with an adnate adipose fin , terminal mouth , nearly equal jaws , 10 preoperculomandibular pores , and a single internasal pore ( robison and allen 1995 ) .
differs from noturus gyrinus in having one internasal pore ( vs . 2 ) and 16 - 18 anal rays ( vs . 14 - 16 ) ( robison and allen 1995 ) . differs from n . exilis in lacking serrae on the pectoral spine , and in having more caudal rays and typically 8 pectoral rays ( vs . 9 ) ( robison and allen 1995 ) .
density was 17 . 2 - 204 ( mean 95 ) per 100 sq m in riffle and pool habitats at six sites ; density ranges up to 32 per sq m in pools along dried up stream reaches ( gagen et al . 1998 ) .
mayflies and chironomids are primary food items ( smith 1982 , robison and harp 1985 ) ; also eats beetles , caddisflies , isopods , copepods , and gastropods .
occurrences are based on evidence of historical presence , or current and likely recurring presence , at a given location . such evidence minimally includes collection or reliable observation and documentation of one or more individuals ( including eggs and larvae ) in appropriate habitat .
madtoms are generally regarded as sedentary , at least over the short term , but dispersal characteristics are unknown . separation distance is arbitrary but reflects the likely low probability that two occupied locations separated by less than several kilometers of aquatic habitat would represent truly independent populations over the long term . because of the difficulty in defining suitable versus unsuitable habitat , especially with respect to dispersal , and to simplify the delineation of occurrences , a single separation distance is used regardless of habitat quality .
use the generic guidelines for the application of occurrence ranks ( 2008 ) . the key for ranking species occurrences using the generic approach provides a step - wise process for implementing this method .
zoological data developed by natureserve and its network of natural heritage programs ( see local programs ) and other contributors and cooperators ( see sources ) .
jelks , h . l . , s . j . walsh , n . m . burkhead , s . contreras - balderas , e . díaz - pardo , d . a . hendrickson , j . lyons , n . e . mandrak , f . mccormick , j . s . nelson , s . p . platania , b . a . porter , c . b . renaud , j . jacobo schmitter - soto , e . b . taylor , and m . l . warren , jr . 2008 . conservation status of imperiled north american freshwater and diadromous fishes . fisheries 33 ( 8 ) : 372 - 407 .
lee , d . s . , c . r . gilbert , c . h . hocutt , r . e . jenkins , d . e . mcallister , and j . r . stauffer , jr . 1980 . atlas of north american freshwater fishes . north carolina state museum of natural history , raleigh , north carolina . i - x + 854 pp .
lundberg , j . g . 1992 . the phylogeny of ictalurid catfishes : a synthesis of recent work . pages 392 - 420 in r . l . mayden , editor . systematics , historical ecology , and north american freshwater fishes . stanford university press , stanford , california . xxvi + 969 pp .
nelson , j . s . , e . j . crossman , h . espinosa - perez , l . t . findley , c . r . gilbert , r . n . lea , and j . d . williams . 2004 . common and scientific names of fishes from the united states , canada , and mexico . american fisheries society , special publication 29 , bethesda , maryland . 386 pp .
page , l . m . , h . espinosa - pérez , l . t . findley , c . r . gilbert , r . n . lea , n . e . mandrak , r . l . mayden , and j . s . nelson . 2013 . common and scientific names of fishes from the united states , canada , and mexico . seventh edition . american fisheries society , special publication 34 , bethesda , maryland .
page , l . m . , and b . m . burr . 1991 . a field guide to freshwater fishes : north america north of mexico . houghton mifflin company , boston , massachusetts . 432 pp .
page , l . m . , and b . m . burr . 2011 . peterson field guide to freshwater fishes of north america north of mexico . second edition . houghton mifflin harcourt , boston . xix + 663 pp .
petersen , j . c . , and b . g . justus . 2005 . the fishes of hot springs national park arkansas , 2003 . u . s . geological survey scientific investigations report 2005 - 5126 . 13 pp .
robison , h . w . and t . m . buchanan . 1988 . fishes of arkansas . the university of arkansas press , fayetteville , arkansas . 536 pp .
robison , h . w . and r . t . allen . 1995 . only in arkansas : a study of the endemic plants and animals of the state . university of arkansas press , fayetteville , arkansas .
starnes , w . c . 1995 . taxonomic validation for fish species on the u . s . fish and wildlife service category 2 species list . 28 pp .
taylor , w . r . 1969 . a revision of the catfish genus noturus ( rafinesque ) with an analysis of higher groups in the ictaluridae . smithsonian institution , u . s . national museum bulletin 282 . 315 pp .
state natural heritage data centers . 1996a . aggregated element occurrence data from all u . s . state natural heritage programs , including the tennessee valley authority , navajo nation and the district of columbia . science division , the nature conservancy .
state natural heritage data centers . 1996b . aggregated element occurrence data from all u . s . state natural heritage programs , including the tennessee valley authority , navajo nation and the district of columbia : export of freshwater fish and mussel records west of the mississippi river in 1997 . science division , the nature conservancy .
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ridgely , r . s . , t . f . allnutt , t . brooks , d . k . mcnicol , d . w . mehlman , b . e . young , and j . r . zook . 2003 . digital distribution maps of the birds of the western hemisphere , version 1 . 0 . natureserve , arlington , virginia , usa .
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using molecular genetic tools to identify extremophile bacteria from deep in arkansas’s blanchard caverns .
studies of non–native species of invasive trees and shrubs that occur naturalized in arkansas , their ability to become established in the local flora , and what factors influence this process .
tungoil tree ( aleurites fordii hemsl . ) ( euphorbiaceae ) new to the arkansas flora .
negundo chaste tree ( vitex negundo l . ) ( verbenaceae ) new to the arkansas flora .
chinese flame tree ( koelreuteria bipinnata franch . ) new to the arkansas flora .
effects of agriculture and indigenous villages on coral reef composition in kuna yala , panama .
ichthyofaunal assemblages in three proximate but ecologically diverse streams in clark county , arkansas .
geographic variation within an isolated population of big - eared bats in oklahoma , kansas and texas .
recovery of sea urchin populations , st . ann ' s bay , jamaica .
diversity of lamium ( lamiaceae ) in arkansas , including occurrences of lamium hybridum and flower color forms .
comment suwannee river , florida to the mississippi river ( etnier and starnes 1993 ) .
comment enters kentucky’s waters during the spawning run ( burr and warren 1986 ) .
life history from january - march . eggs are deposited over coarse sand and gravel
between mid - july and early october ( pflieger 1975 ) . juveniles stay in fresh
comment and southern illinois to the gulf of mexico in the mississippi river basin .
to veracruz , mexico . the species is now extirpated or very rare in the
comment county near maysville ( trautman 1981 ) . j . p . kirtland noted this species
habitat / this species is one of the largest freshwater fishes in the u . s . . the largest
life history known gar collected in louisiana was 9 feet 8 . 5 inches and weighed 302
rivers and their bayous , oxbows , and backwaters . the have been known to
life history current below and above riffles and in pools up to 1 . 75 meters deep ( burr
substrates and boulders , tree snags , or water willow as cover . spawning is
supporting aquatic life ranges from 51 . 5 % to 90 . 0 % of stream miles
comment species of buffalo ( etnier and starnes 1993 ) . some authorities regard this
mississippi and ohio rivers . in the ohio river , pearson and krumholz ( 1984 )
history environments ( burr and warren 1986 ) . the species has also been reported to
being a large dietary component ( becker 1983 , minckley et al . 1970 ) . spawning
substrates from bedrock to gravel ( piller et al . 2003 ) . piller et al . ( 2003 )
2008 , 17 records ) , 05140206 lower ohio ( 1996 - 2008 , 13 records ) . although
were fully supporting of aquatic life use ( kentucky division of water 2008 ) . the
g - trend the blackfin sucker is endemic to the barren river drainage basin . the
comment and a portion of northern tennessee ( etnier and starnes 1993 ) . in
life history or rubble substrates in creeks and medium sized rivers ( natureserve 2004 ) .
early spring ( march and april ) . after hatching , the young are found in
key currently exists only in the upper barren river ( huc 05110002 ) . nearly
2b gravel / sand removal or quarrying ( e . g . , mineral excavation )
life history 5 m in width ( burr and warren 1986 ) . typically found in sluggish pools of
60 : 40 ( burr and warren 1986 ) . this species is usually also associated with
species is broadly distributed in the southeastern u . s . and often abundant in
( mettee et al . 1996 ) . according to natureserve ( 2004 ) , this species is
habitat / little is known about the biology of this species . spawning occurs in mid -
life history to late spring in shoal areas of small streams ( etnier and starnes 1993 ) . in
portion ( approximately 10 % ) of the species’ range ( natureserve 2008 ) .
history and around submerged logs and stumps . less frequently , or more sporadically , it
or gravel in current ( burr and warren 1986 ) . the blackfin shiner is a schooling
( robison and buchanan 1988 , ross 2001 ) . in tennessee , the spawning period
observations of males in breeding condition ( etnier and starnes 1993 ) . eggs are
breeding males ( heins 1990 , pfleiger 1997 , boschung and mayden 2004 ) .
some degree ( burr and warren 1986 , woods et al . 2002 ) .
comment caney fork , tennessee , to rockcastle river , kentucky ( natureserve 2004 ) .
and little south forks , and buck creek ( burr and warren 1986 ) .
comment cumberland river ( below the falls ) where it is known from five localities . it
streams ( etnier and starnes 1993 ) . spawning occurs in mid - april through
early may as water temperature approaches 15 c ( 60f ) . sexual maturity is
reached at age - 1 . life span is 2 . 5 years . food consists of about half
mayflies . maximum total length is 100 mm sl ( etnier and starnes 1993 ) .
huc8 are good as 73 . 1 % of assessed streams were found to be fully
supporting aquatic life . a total of 43 . 7 miles of streams in this huc8 are
comment mississippi river from obion creek south ( etnier and starnes 1993 ) . it
life history in raceways and riffles on the coastal plain ( burr and warren 1986 ) . this
include 27 . 8 % ( bayou du chien - mayfield huc8 ) and 37 . 0 % ( obion creek
2f riparian zone removal ( agriculture / development ) . burr and warren ( 1986 )
comment was elevated to species status by etnier and starnes ( 1986 ) . this species is
( etnier and starnes , 1993 ) . although species continues to be common in
s - trend in kentucky , this species is confined to terrapin creek in graves county .
aquatic vegetation is present ( etnier and starnes , 1993 ) . bell and timmons
from 33 - 116 to 65 - 201 mature ova per age - 1 female . although bell and
comment creeks , graves county ( burr and warren 1986 ) . within terrapin creek , it
1984 ( burr and warren 1986 , d . eisenhour , morehead state university ,
life history to fast current ( natureserve 2004 ) . specific habitat includes sand - gravel
comment degrees n ( lee and gilbert 1980 ) . in the eastern hemisphere , it occurs
kentucky , missouri , wyoming , and oregon ( page and burr 1991 ) . the species
in depths greater than 1 . 5 m with substrates of rock , sand , and mud ( burr and
habits ( lee and gilbert 1980 , becker 1983 ) . in the great lakes and areas to the
bays over and or on gravel shoals ( becker 1983 , holm et al . 2009 ) . in rivers ,
side channels behind deposition bars ( u . s . fish and wildlife service 2003 ) . the
lower ohio - bay , and 05140206 lower ohio . pre - 1967 records are available for
the lower kentucky river ( 05100205 ) and licking river ( 05100101 ) . the most
brush - whiteoak ( 1993 , photo record ) ( compton et al . 2004 ) . although the ohio
g - trend the central mudminnow occurs in north central north america in the st .
creek and running slough , fulton county ( burr and warren 1986 ) . it is
coastal plain ( clay 1975 ) . this species usually prefers non - turbid water
shallow water during the spring water temperatures reach 13° c ( 55° f ) .
supporting aquatic life range from 27 % ( obion creek huc ) to 74 . 9 %
none ( kentucky lake huc ) to 124 . 4 ( bayou du chien - mayfield creek
comment river drainage ( burr and warren 1986 ) . it has been collected both above
life history may be taken in medium sized streams ( burr and warren 1986 ) . it occurs in
associated with large , flat stones ( page 1983 ) . spawning takes place in
april when water temperatures are around 13° c . ( etnier and starnes 1993 ) .
common food items include mayflies , midges , and stoneflies ( page 1983 ) .
1986 ) . sexual maturity is reached at one year of age . spawning occurs from
mid - march to early june . females contain 26 - 116 eggs and deposit them
on dead leaves , twigs , rock and filamentous algae . eggs are not guarded and
hatch in 5 - 13 days based on temperature . life span is 1 . 5 years . principal
chien – mayfield ( huc 08010201 ) , and obion creek ( huc 08010202 ) .
mississippi – memphis huc ) to 74 . 9 % ( lower tennessee - kentucky lake
easternmost records from the state ( burr and warren 1986 ) . it is considered
habitat records predate 1984 . the bayou du chien - mayfield ( huc 08010201 )
contains the largest number of records ( 17 ) , only one of which is post - 1984 .
life history streams , and sloughs ( burr and warren 1986 ) . it occurs over substrates of
sand or clay overlain with silt and organic debris ( burr and warren 1986 ) .
et al . 1996 ) and april to september in florida ( natureserve 2004 ) . nest
growth is fairly slow and lifespan is approximately six years ( mettee et al .
watersheds have fewer than ten ( kentucky division of water 2002 , 2004 ) .
and tennessee and the fish to be rare and extremely localized . jenkins , in
darter is presented in etnier and starnes ( 1993 ) as etheostoma sp . ( this
darter was officially describes after their book went to press ) . at that time
of the duskytail darter to be confined to 4 . 3 stream miles of the big south
in kentucky was only about a 4 . 8 - mile reach between the mouth
troublesome creek ( the majority ) and the mouth of oil well branch . the
well ) occurred under slab shaped stones during april - june . eggs are laid in
with complement of eggs ranging from 79 - 103 per “nest rock” . these nests
supporting aquatic life include 90 . 0 % of the 75 . 5 miles of stream assessed
drainage from red river upstream ( burr and warren 1986 ) . it is common in
life history starnes 1993 ) . spawning occurs from april to june at temperatures of
about 18 - 20°c in gravel - cobble raceways . this species may be an
supporting aquatic life ranges from 48 . 4 % to 90 . 0 % of streams surveyed
within these watersheds , in which up to 404 . 4 stream miles have been
4a acid mine drainage other coal mining impacts . burr and warren ( 1986 )
4b waste water discharge ( e . g . , sewage treatment ) . burr and warren ( 1986 )
4d oil and gas drilling operations associated runoff . burr and warren ( 1986 )
also be found in pools adjacent to habitat . eggs are thought be to attached
age range of breeding females is 1 - 2 years ( natureserve 2004 ) . eggs are laid
singly on horizontal and vertical surface and they hatch in 6 – 8 days . life
span is 3 years . diet consists primarily of midge larvae ( etnier and starnes
17 states in the u . s . ( natureserve 2004 ) . over its range it is common and
comment in the mississippi river at cairo , illinois ( burr and warren 1986 ) . burr and
and crossman 1973 ; pflieger 1975 ) . it relies on flood flows to spawn
peak flows , when the temperature is warmer and the bottom is more stable .
into smaller streams to spawn ( scott and crossman 1973 ; pflieger 1975 ) .
comment small portion of north - central tennessee . in kentucky , it is considered
comment river , and the south fork of the kentucky river ( natureserve 2004 ) . it is
life history gradients ( natureserve 2004 ) . inhabits quiet water areas , especially slow
spring and peaks from mid - march through mid - april . this species may be
barren river drainages are 80 . 0 % and 92 . 6 % ( respectively ) of stream miles
comment to trinity r . dr . , texas ; former mississippi embayment north to
elsewhere ( page and burr 1991 ) . as the golden topminnow is secure in
most of its range , natureserve indicates g5 as its global status . however ,
comment 1970 from reelfoot lake , ( sisk 1973 ) . the first notable population
( 1973 ) reported a series of 14 ( each date ) from open pond , fulton county .
special concern category ( branson et al . 1981 ) . both open fork and
shoreline ( burr and warren 1986 ) . as are most fundulus , the golden
topminnow is a surface dweller . etnier and starnes ( 1993 ) report it to
habitat kentucky ( huc - 8 ) are located within huc 08010202 ( obion creek ) . of
the 28 . 7 miles of stream assessed within this huc , 27 . 8 % of the waters
were fully supporting , 56 . 0 % partially supporting , 16 . 2 % not supporting ,
division of water 2002 ) . however , one of the current and primary known
( pg . 74 , kentucky atlas and gazetteer , 1997 ) . this refuge should help
population occurring above the fall line . it is reported to be c \ common in
s - trend in kentucky , this species is sporadic and seasonally rare . its known
habitat / restricted to small lowland creeks , ditches , and wetlands . in small gravel
supporting aquatic life include 27 . 8 % ( obion creek huc ) and 56 . 0 %
comment from terrapin creek in graves county . burr and mayden ( 1979 ) reported
comment over a large part of the central united states . recently recognized as a
flowing riffles and runs . during periods of low water , when riffles and runs
key known to occur only in the barren river ( huc 05110002 ) . habitat
( page and burr 1991 ; pflieger 1975 ) . spawning occurs during late spring
emergent vegetation and hatch in 4 - 30 days at temperatures of 13 - 34 c .
s - trend this species is endemic to the upper kentucky river system . it is
life history may be taken in streams . this species usually occupies sluggish pools and
sexual maturity is reached at age 1 . females contain 67 - 265 mature eggs .
dipterans , caddisflies , stoneflies , and beetle larvae ( etnier and starnes 1993 ) .
habitat basin . habitat conditions fully supporting aquatic life range from 48 . 4 %
( north fork kentucky river huc 05100201 ) to 88 . 5 % ( upper kentucky
comment tributary ) , kentucky . in the upper green river drainage , it is common in
pitman , and goose creeks . in the gasper river drainage , it is most common
habitat few records also in the barren river ( huc 05110002 ) . habitat conditions
in the upper green river and 92 . 6 % in the barren river watersheds .
113 . 1 in the the upper green and 14 . 7 for the barren river drainages
rarely enters creeks , streams , or rivers ( burr and warren 1986 ) . spawning
20 , 000 eggs per female . food consists of microcrustacea and midge larva .
life span is 5 or 6 years . maximum size to 394 mm ( 15 . 5 inches ) total
length and nearly 1 kg ( 2 . 2 lbs ) ( etnier and starnes 1993 ) .
habitat loss , construction of dams , and pollution . over the years , this
comment mississippi , cumberland , and tennessee rivers ( burr and warren 1986 ) .
the lake sturgeon ( trautman 1981 ) . burr and warren ( 1986 ) reported eight
river , 3 ; cumberland river , 1 ) for this species in kentucky . since 1984 ,
feet over firm sand , gravel , or rock ( pflieger 1975 ) . the oldest individual
was reported to be 154 years of age and weighing 207 pounds . . spawning
outside bends over rocks / boulders in water between 1 and 15 feet in depth .
habitat river that lie within four different huc8 units . the most recent record is
supporting aquatic life range from none ( highland - pigeon huc ) to 51 . 5 %
terrapin creek , although confined to a small range ( d . eisenhour , morehead
habitat / occurs in lowland creeks and small rivers across its range ( natureserve ) . in
life history the south , it occupies relatively shallow , clear riffles with moderate current .
occurs from mid - june through early - july ( etnier and starnes 1993 ) .
snags or similar organic cover ( etnier and starnes 1993 ) . if available , they
life history and warren 1986 ; jenkins and burkhead 1993 ; natureserve 2004 ) . primary
( etnier and starnes 1993 ) . spawning occurs in shallow , gravel / cobble riffles
where eggs can be buried in the gravel / cobble substrate ( natureserve 2004 ) .
supporting aquatic life range include 55 . 8 % of stream miles surveyed in the
upper green river and 92 . 6 % in the barren river watersheds . number of
found between pre - 1984 and post - 1984 data ( d . eisenhour , morehead state
sand / silt substrates in pools ( burr and warren 1986 ) . such habitats are
eggs and young are carried in the gill chamber for 4 to 5 months . only 10 %
habitat ( huc 05110001 ) , and rough river ( huc 05110004 ) drainages . habitat
2004 ) , with good populations in the licking river ( d . eisenhour , morehead
river drainages ( etnier and starnes 1993 ) . this species has been collected in
maturation , it is now limited to the upper reaches ( etnier and starnes 1993 ) .
comment south fork of the cumberland river drainage . ( burr and warren 1986 ;
river has turned up only two specimens ( m . compton , ky division of
life history upland river systems ( burr and warren 1986 ; natureserve 2004 ) . typical
late - july ( etnier and starnes 1993 ) . lifespan is approximately 4 years .
drainages , and formerly in lake erie ( etnier and starnes 1993 ) . because the
rare fishes ( branson et al . 1981 ) , but was later removed because it was thought
to be more common that previously believed ( burr and warren 1986 ) . although
history zooplankton on which it feeds . adults must have access to gravel bars subject to
the species prefers depths greater than 1 . 5 m , seeking deeper water in late fall
artificial structures ( e . g . , below dams ) that create eddies and reduce current
velocity ( southall and hubert 1984 ) . paddlefish have been reported to spawn in
below upstream impoundments ( e . g . , stancill et al . 2002 ) . in the lower
( 08010100 ) , and bayou du chien - mayfield ( 08010201 ) watershed units . sections
kentucky lake ( 06040005 ) , and lower tennessee river ( 06040006 ) . habitat
three records are available for the licking river ( 05100101 ) . the licking river
comment cumberland river in wayne county . it was judged to be most abundant in
a 6 - mile reach of the little south fork ( u . s . fish and wildlife service
cobble , pebble , and gravel mixed with clean sand ( u . s . fish and wildlife
service 1997 ) . peak spawning occurs from june to early july ( u . s . fish
palezone shiner for 20 years , very little is known about its biology ( u . s .
habitat in the south fork cumberland ( huc 0513014 ) watershed , wayne county .
comment south to louisiana and west to the guadaloupe river in texas ( clemmer 1980 ) .
skelly and sule 1983 , warren and burr 1988 , kwak 1991 , pflieger 1997 ) .
reduction of the species’ habitat or range ( jelks et al . 2008 ) .
comment and upper cumberland basins in kentucky ( burr and warren 1986 ) . until
recent collections because of its close similarity to other minnows ( e . g . , bigeye
history collected along the margin of the stream lined with water willow ( justicia sp . ) ;
warren 1986 ) . biology and life history of populations in kentucky are unknown .
river , habitat conditions fully supporting aquatic life include 90 % of the 75 . 5
miles of stream assessed within the watershed , and 52 . 3 stream miles are
s - trend there is only one substantiated record for the pallid sturgeon in kentucky .
life history pounds ) with a large flat shovel - like snout ( natureserve 2004 ) . it inhabits
spawning runs . life span has been estimated to be up to 50 years . the
oldest individual to - date was a 41 - year - old female weighing 37 . 5 pounds
mollusks , annelids , eggs of other fishes , and other fishes ( natureserve 2004 ) .
within this huc is able to fully support aquatic life . most ( 64 . 2 % ) can
only partially support aquatic life , while 35 . 8 % are considered to be non -
life history and small to large rivers . it is common and can be very abundant in the
great plains ( page and burr 1991 ) . it lives in schools near the bottom and
and flathead chubs , and the red , sand and emerald shiners ( pflieger 1975 ) . in
west ( gilbert 1980 , page and burr 1991 , natureserve 2008 ) . in canada , it
huron in southern ontario ( parker et al . 1988 , natureserve 2008 ) . recently , the
and red river ( burr and warren 1986 , meade et al . 1986 ) . although these small ,
makes them vulnerable to habitat loss and degradation . in wisconsin , lyons et al .
portion of its diet consists of terrestrial insects ( schwartz and norvell 1958 ) .


labrisomus philippii , the chalapo clinid , is a species of labrisomid blenny native to the pacific coast of south america from peru to chile .

this species can reach a length of 35 centimetres ( 14 in ) tl and the greatest recorded weight for a specimen of this fish was 635 grams ( 22.4 oz ) .

labrisomus philippii

spawning cycles of labrisomus philippii
by stephen r . goldberg and marie c . pizzorno
goldberg , stephen r . and pizzorno , marie c . ( 1986 )
notes on the spawning cycles of labrisomus philippii ( labrisomidae ) and trachinotus paitensis ( carangidae ) from peru ,
bulletin of the southern california academy of sciences : vol . 85 : iss . 2 . available at : urltoken
( of clinus philippii steindachner , 1866 ) froese , r . & d . pauly ( editors ) . ( 2018 ) . fishbase . world wide web electronic publication . , available online at urltoken [ details ]
html public
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urltoken
html public
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urltoken
thank you for taking the time to provide feedback on the iucn red list of threatened species website , we are grateful for your input .
eschmeyer , w . n . ( ed . ) . 2014 . catalog of fishes . updated 27 august 2014 . available at : urltoken . ( accessed : 27 august 2014 ) .
justification : this is a widespread species that is locally abundant with no well - documented major threats and is therefore considered least concern . however , because of its shallow depth distribution and potential for impacts from coastal development and pollution , further research is needed to monitor this species .
this species is found along the coast of chile and peru in the southeast pacific .
represented between 0 . 06 and 1 . 1 percent of the fish assemblage at different study sites ( perez - matus et al . 2007 ) .
this species occurs in the intertidal zone , and feeds on polychaetes , amphipods and small fish ( berrios and vargas 2004 ) .
it is a shallow water species and therefore could be impacted by coastal development and pollution . however , there is no current evidence that this constitutes a major threat for this species .
no species - specific conservation measures are in place for this species , but it may occur in protected areas .
to make use of this information , please check the < terms of use > .
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1 . research - > 1 . 1 . taxonomy 1 . research - > 1 . 2 . population size , distribution & trends 1 . research - > 1 . 3 . life history & ecology 1 . research - > 1 . 5 . threats
anonymous . 1996 . fish collection database of the university of british columbia fish museum . university of british columbia , vancouver , canada .
anonymous . 2001 . fish collection database of the national museum of natural history ( smithsonian institution ) . smithsonian institution - division of fishes . , washington , dc .
berrios , v , and vargas f . , m . 2004 . estructura trofica de la associacion de peces intermareales de la costa rocosa del norte de chile . rev . biol . trop . 52 ( 1 ) .
garcía - godos naveda , i . 2001 . patrones morfológicos del otolito sagitta de algunos peces óseos del mar peruano . .
iucn . 2014 . the iucn red list of threatened species . version 2014 . 3 . available at : urltoken . ( accessed : 13 november 2014 ) .
medina , m . , m . araya and c . vega . 2004 . alimentación y relaciones tróficas de peces costeros de la zona norte de chile . invest . mar . 32 ( 1 ) : 33 - 47 .
pequeño , g . 1989 . peces de chile . lista sistematica revisada y comentada . rev . biol . mar . , valparaiso 24 ( 2 ) : 1 - 132 .
pérez - matus , a . , ferry - graham , l . a . , cea , a . and vásquez , j . a . 2007 . community structure of temperate reef fishes in kelp - dominated subtidal habitats of northern chile . marine and freshwater research 58 : 1069 - 1085 .
wu , h . l . , k . - t . shao and c . f . lai ( eds . ) . 1999 . latin - chinese dictionary of fishes names . the sueichan press , taiwan .
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froese , r . & d . pauly ( editors ) . ( 2018 ) . fishbase . world wide web electronic publication . , available online at urltoken [ details ]
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to cite this page : myers , p . , r . espinosa , c . s . parr , t . jones , g . s . hammond , and t . a . dewey . 2018 . the animal diversity web ( online ) . accessed at https : / / animaldiversity . org .
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stephen r . goldberg , department of biology , whittier college marie c . pizzorno , department of biology , whittier college
natural environment : inhabits shallow coral and rocky reefs and usually found between depths of 3 – 15 feet ( 1 – 5 m ) where it feeds upon small crustaceans .
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costabieta horrida is a species of sea snail , a marine gastropod mollusk in the family pyramidellidae , the pyrams and their allies .

this species has three synonyms , most of these synonyms are within the rissiona genus of gastropods , while one happens to be of a species within the identical genus as this mollusk .

costabieta horrida

id : 293173 original name : costabieta _ horrida . jpg size 111x178 - 7443 bytes image manager : jan delsing directory : 2234 created : 2016 - 05 - 26 15 : 38 : 58 - user jan delsing url : urltoken text function : [ [ i : 293173 ; image ] ] , [ [ it : 293173 ] ] ( thumbnail )
( of costabieta paucina laseron , 1956 ) ponder w . f . ( 1985 ) a review of the genera of the rissoidae ( mollusca : mesogastropoda : rissoacea ) . records of the australian museum supplement 4 : 1 - 221 . [ 12 february 1985 ] , available online at urltoken page ( s ) : 108 [ details ]
( of rissoina horrida garrett , 1873 ) garrett a . , 1873 . descriptions of new species of marine shells inhabiting the south sea islands . proceedings of the academy of natural sciences of philadelphia , 25 : 209 - 231 , plates 2 - 3 , available online at urltoken page ( s ) : 210 , pl . 2 , fig . 5 [ details ]
ponder w . f . ( 1985 ) a review of the genera of the rissoidae ( mollusca : mesogastropoda : rissoacea ) . records of the australian museum supplement 4 : 1 - 221 . [ 12 february 1985 ] , available online at urltoken page ( s ) : 108 [ details ]
peñas a . & rolán e . ( 2017 ) . deep water pyramidelloidea from the central and south pacific . the tribe chrysallidini . ecimat ( estación de ciencias mariñas de toralla ) , universidade de vigo . 412 pp . [ details ]
( of pyrgulina favrei hornung & mermod , 1925 ) peñas a . & rolán e . ( 2017 ) . deep water pyramidelloidea from the central and south pacific . the tribe chrysallidini . ecimat ( estación de ciencias mariñas de toralla ) , universidade de vigo . 412 pp . [ details ]
garrett a . , 1873 . descriptions of new species of marine shells inhabiting the south sea islands . proceedings of the academy of natural sciences of philadelphia , 25 : 209 - 231 , plates 2 - 3 , available online at urltoken page ( s ) : 210 , pl . 2 , fig . 5 [ details ]
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fiji , source : garrett , a . 1873 . descriptions of new species of marine shells inhabiting the south sea islands ( original figure )
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rissoina is a large genus of minute sea snails , marine gastropod mollusks or micromollusks in the family rissoinidae .
rissoina abnormis g . nevill & h . nevill , 1875 : synonym of stosicia abnormis ( g . nevill & h . nevill , 1875 )
rissoina bellardii issel , 1869 : synonym of pyramidelloides mirandus ( a . adams , 1861 )
rissoina bellula a . adams , 1851 : synonym of phosinella bellula ( a . adams , 1851 )
rissoina clathrata a . adams , 1853 : synonym of phosinella clathrata ( a . adams , 1853 )
rissoina congenita e . a . smith , 1890 : synonym of schwartziella congenita ( e . a . smith , 1890 )
rissoina conica ( c . b . adams , 1850 ) : synonym of vitreolina conica ( c . b . adams , 1850 )
rissoina detrita boettger , 1893 : synonym of rissoina dorbignyi a . adams , 1851
rissoina dimidiata jickeli , 1882 : synonym of rissoina dorbignyi a . adams , 1851
rissoina eucosmia bartsch , 1915 : synonym of pyramidelloides mirandus ( a . adams , 1861 )
rissoina evanida nevill , 1874 : synonym of zebinella evanida ( g . nevill & h . nevill , 1881 )
rissoina firmata ( c . b . adams , 1852 ) : synonym of schwartziella firmata ( c . b . adams , 1852 )
rissoina floridana olsson , a . a . & a . harbison , 1953 : synonym of schwartziella floridana ( olsson , a . a . & a . harbison , 1953 )
rissoina gemmulata turton , 1932 : synonym of pyramidelloides mirandus ( a . adams , 1861 )
rissoina helenae e . a . smith , 1890 : synonym of schwartziella helenae ( e . a . smith , 1890 )
rissoina hystrix souverbie , 1877 : synonym of pyramidelloides mirandus ( a . adams , 1861 )
rissoina insolita deshayes , 1863 : synonym of pyramidelloides mirandus ( a . adams , 1861 )
rissoina miranda a . adams , 1861 : synonym of pyramidelloides mirandus ( a . adams , 1861 )
rissoina montrouzieri souverbie , 1862 : synonym of rissoina dorbignyi a . adams , 1851
rissoina nitida a . adams , 1853 : synonym of phosinella nitida ( a . adams , 1853 )
rissoina nodicincta a . adams , 1853 : synonym of phosinella nodicincta ( a . adams , 1853 )
rissoina princeps ( c . b . adams , 1850 ) : synonym of zebinella princeps ( c . b . adams , 1850 )
rissoina pulchra ( c . b . adams , 1850 ) : synonym of phosinella pulchra ( c . b . adams , 1850 )
rissoina samoensis weinkauff , 1881 : synonym of stosicia abnormis ( g . nevill & h . nevill , 1875 )
rissoina smithii tryon , 1887 : synonym of eatoniella caliginosa ( e . a . smith , 1875 )
rissoina striosa ( c . b . adams , 1850 ) : synonym of zebinella striosa ( c . b . adams , 1850 )
rissoina turricula pease , 1860 : synonym of rissoina costata a . adams , 1851
rissoina turtoni e . a . smith , 1890 : synonym of schwartziella turtoni ( e . a . smith , 1890 )
studies on west indian marine molluscs 45 the caribbean marine gastropods described by otto andreas lawson mørch . 1 : some type specimens and identifications ( gastropoda : prosobranchia ) | marien faber - urltoken
studies on west indian marine molluscs 45 the caribbean marine gastropods described by otto andreas lawson mørch . 1 : some type specimens and identifications ( gastropoda : prosobranchia )
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