bothrops alcatraz is a venomous pitviper species found only on an island off the coast of southeastern brazil .

no subspecies are currently recognized .

bothrops alcatraz

bothrops alcatraz marques , martins & sazima 2002 bothropoides alcatraz — fenwick et al . 2009 bothrops alcatraz — carrasco et al . 2012 bothropoides alcatraz — wallach et al . 2014 : 113
biological and immunological properties of the venom of bothrops alcatraz , an endemic species of pitviper from brazil .
biological and immunological properties of the venom of bothrops alcatraz , an endemic species of pitviper from brazil . - pubmed - ncbi
bothrops alcatraz is known only from alcatrazes island ( 1 . 35 km² ) , the largest of four small islands of alcatrazes archipelago , approximately 35 km from the coast of são paulo , southeastern brazil .
furtado , m . f . d . 2005 . biological and immunological properties of the venom of bothrops alcatraz , an endemic species of pitviper from brazil . comparative biochemistry and physiology . c , comparative pharmacology and toxicology , 141 : 117 - 123 . [ links ]
main distribution area south america . b . asper is the only bothrops species in central america and mexico . see link
distribution
at the top of the page for detailed information . map 46 bothrops spp .
phylogeography of the bothrops jararaca complex ( serpentes : viperidae ) : past fragmentation and island colonization in the brazilian atlantic forest .
in a clinical study from ecuador , around 60 % of verified bites were due to bothrops sp . ( kerrigan 1991 ) .
phylogeography of the bothrops jararaca complex ( serpentes : viperidae ) : past fragmentation and island colonization in the brazilian atlantic forest . - semantic scholar
genera and species of centipedes identified as prey of bothrops species . only the records for centipedes identified at least at genus level were included .
phylogeography of the bothrops jararaca complex ( serpentes : viperidae ) : past fragmentation and island colonization in the brazilian atlantic forest . - pubmed - ncbi
saldarriaga , m . m . ; otero , r . ; núñez , v . ; toro , m . f . ; díaz , a . ; gutiérrez , j . m . 2003 . ontogenetic variability of bothrops atrox and bothrops asper snake venoms from colombia . toxicon , 42 : 405 - 411 . [ links ]
andrade , d . v . ; abe , a . s . 1999 . relationship of venom ontogeny and diet in bothrops . herpetologica , 55 : 200 - 204 . [ links ]
valdujo , p . h . ; nogueira , c . c . ; martins , m . 2002 . ecology of bothrops neuwiedi pauloensis ( serpentes : viperidae : crotalinae ) in the brazilian cerrado . journal of herpetology , 36 : 169 - 176 [ links ]
marques , o . a . v . ; martins , m . ; sazima , i . 2002 . a new insular species of pitviper from brazil , with comments on evolutionary biology and conservation of the bothrops jararaca group ( serpentes , viperidae ) . herpetologica , 58 : 303 - 312 . [ links ]
marques , o . a . v . ; martins , m & sazima , i . 2002 . a new insular species of pitviper from brazil , with comments on evolutionary biology and conservation of the bothrops jararaca group ( serpentes , viperidae ) . herpetologica 58 ( 3 ) : 303 - 312 - get paper here
according to a study of the first half of this century for central and south america , of a total of 6 , 601 recorded cases of snakebite envenoming , 4 , 902 cases were attributed to various bothrops species ; of these , 3 , 446 cases were attributed to the species b . jararaca ( rosenfeld 1971 ) .
fenwick , allyson m . ; ronald l . gutberlet jr , jennafer a . evans , christopher l . parkinson 2009 . morphological and molecular evidence for phylogeny and classification of south american pitvipers , genera bothrops , bothriopsis , and bothrocophias ( serpentes : viperidae ) . zoological journal of the linnean society 156 ( 3 ) : 617 - 640 - get paper here
for the year 1989 , the brazilian ministry of health recorded a total of 20 , 748 snakebites , of which around 67 % were attributed to the bothrops genus ( cardoso 1990 ) . other data from brazil record 20 , 884 snakebites over a period of one and a half years ( 1986–87 ) , of which around 88 % were caused by bothrops sp . , with a mortality of 0 . 5 % . most accidents occur during the day in rural areas with basic agriculture ( ribeiro 1990b ) . in this context , the most significant species are b . atrox in the amazon region , b . moojeni in the central west , b . erythromelas in the northwest and b . jararaca in southeast brazil ( cardoso 1990 ) .
lacraias fazem parte da dieta de diversas espécies de serpentes do gênero bothrops . entretanto , informações importantes para estudos de história natural , como identificação da espécie e tamanho de presas , são raramente publicados . o objetivo desse trabalho é registrar a presença de uma lacraia scolopendra viridicornis , no trato digestivo de uma jararaca da amazônia , bothrops atrox . a serpente estudada é uma fêmea imatura , com 623 mm de comprimento rostro - cloacal , proveniente de aripuanã , estado de mato grosso , brasil . a lacraia é um adulto de scolopendra viridicornis parcialmente digerida , com aproximadamente 190 mm de comprimento . o sucesso na predação dessa grande e perigosa presa pode ser explicado pelas dimensões da serpente , que é grande o suficiente para dominar a presa , mas ainda retém características juvenis , como veneno com ação específica em determinados ítens alimentares .
barbo , < br / > fausto e . ; joão luiz gasparini , antonio p . almeida , hussam zaher , felipe g . grazziotin , rodrigo b . gusmão , josé mário g . ferrarini < br / > & ricardo j . sawaya 2016 . another new and threatened species of lancehead genus bothrops ( serpentes , viperidae ) from ilha dos franceses , southeastern brazil zootaxa 4097 ( 4 ) : 511–529 - get paper here
scolopendra viridicornis eaten by bothrops atrox . a . general view showing the centipede inside the dissected snake . b . same , detail . c . ventral view of the eaten centipede ' s head showing the two powerful forcipules used for venom inoculation . scales : 1 , 50 mm ; 2 , 10 mm ; 3 , 5 mm . photos : r . bertani . this figure is in color only in the electronic version .
martins , m . ; marques , o . a . v . ; sazima , i . 2002 . ecological and phylogenetic correlates of feeding habits in neotropical pitvipers of the genus bothrops . in : schuett , g . w . ; höggren , m . ; douglas , m . e . ; greene , h . w . ( ed . ) . biology of the pitvipers . eagle mountain publishing , eagle mountain , p . 307 - 328 . [ links ]
treatment summary this treatment advice is general for most bothrops species . bites will vary from minor to life threatening . therefore manage all bites as potentially major . look for moderate to severe local effects , including pain , swelling , potential for fluid shifts and hypovolaemic shock , blistering , necrosis , abscess formation . systemic effects may be minor or severe , possibly including coagulopathy and bleeding , kidney damage , even myolytic muscle damage . all cases with significant systemic effects require iv antivenom , as will most cases with significant local effects .
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home » resources » categories and criteria » 2001 iucn red list categories and criteria version 3 . 1
see below for the rules and requirements outlined in the iucn red list categories and criteria . version 3 . 1 ( second edition ) . for translations of this document into other languages , click here .
the iucn red list categories and criteria are intended to be an easily and widely understood system for classifying species at high risk of global extinction . the general aim of the system is to provide an explicit , objective framework for the classification of the broadest range of species according to their extinction risk . however , while the red list may focus attention on those taxa at the highest risk , it is not the sole means of setting priorities for conservation measures for their protection .
extensive consultation and testing in the development of the system strongly suggest that it is robust across most organisms . however , it should be noted that although the system places species into the threatened categories with a high degree of consistency , the criteria do not take into account the life histories of every species . hence , in certain individual cases , the risk of extinction may be under - or over - estimated .
to give people using threatened species lists a better understanding of how individual species were classified .
since their adoption by iucn council in 1994 , the iucn red list categories have become widely recognized internationally , and they are now used in a range of publications and listings produced by iucn , as well as by numerous governmental and non - governmental organizations . such broad and extensive use revealed the need for a number of improvements , and ssc was mandated by the 1996 world conservation congress ( wcc res . 1 . 4 ) to conduct a review of the system ( iucn 1996 ) . this document presents the revisions accepted by the iucn council .
the proposals presented in this document result from a continuing process of drafting , consultation and validation . the production of a large number of draft proposals has led to some confusion , especially as each draft has been used for classifying some set of species for conservation purposes . to clarify matters , and to open the way for modifications as and when they become necessary , a system for version numbering has been adopted as follows :
version 1 . 0 : mace and lande ( 1991 ) the first paper discussing a new basis for the categories , and presenting numerical criteria especially relevant for large vertebrates .
version 2 . 0 : mace et al . ( 1992 ) a major revision of version 1 . 0 , including numerical criteria appropriate to all organisms and introducing the non - threatened categories .
version 2 . 1 : iucn ( 1993 ) following an extensive consultation process within ssc , a number of changes were made to the details of the criteria , and fuller explanation of basic principles was included . a more explicit structure clarified the significance of the non - threatened categories .
version 2 . 2 : mace and stuart ( 1994 ) following further comments received and additional validation exercises , some minor changes to the criteria were made . in addition , the susceptible category present in versions 2 . 0 and 2 . 1 was subsumed into the vulnerable category . a precautionary application of the system was emphasised .
version 2 . 3 : iucn ( 1994 ) iucn council adopted this version , which incorporated changes as a result of comments from iucn members , in december 1994 . the initial version of this document was published without the necessary bibliographic details , such as date of publication and isbn number , but these were included in the subsequent reprints in 1998 and 1999 . this version was used for the 1996 iucn red list of threatened animals ( baillie and groombridge 1996 ) , the world list of threatened trees ( oldfield et al 1998 ) and the 2000 iucn red list of threatened species ( hilton - taylor 2000 ) .
version 3 . 0 : iucn / ssc criteria review working group ( 1999 ) following comments received , a series of workshops were convened to look at the iucn red list criteria following which , changes were proposed affecting the criteria , the definitions of some key terms and the handling of uncertainty .
version 3 . 1 : iucn ( 2001 ) the iucn council adopted this latest version , which incorporated changes as a result of comments from the iucn and ssc memberships and from a final meeting of the criteria review working group , in february 2000 .
all new assessments from january 2001 should use the latest adopted version and cite the year of publication and version number .
in the rest of this document , the proposed system is outlined in several sections . section ii , the preamble , presents basic information about the context and structure of the system , and the procedures that are to be followed in applying the criteria to species . section iii provides definitions of key terms used . section iv presents the categories , while section v details the quantitative criteria used for classification within the threatened categories . annex i provides guidance on how to deal with uncertainty when applying the criteria ; annex ii suggests a standard format for citing the red list categories and criteria ; and annex iii outlines the documentation requirements for taxa to be included on iucn ' s global red lists . it is important for the effective functioning of the system that all sections are read and understood to ensure that the definitions and rules are followed .
the information in this section is intended to direct and facilitate the use and interpretation of the categories ( critically endangered , endangered , etc . ) , criteria ( a to e ) , and subcriteria ( 1 , 2 , etc . ; a , b , etc . ; i , ii , etc . ) .
the criteria can be applied to any taxonomic unit at or below the species level . in the following information , definitions and criteria the term ' taxon ' is used for convenience , and may represent species or lower taxonomic levels , including forms that are not yet formally described . there is sufficient range among the different criteria to enable the appropriate listing of taxa from the complete taxonomic spectrum , with the exception of micro - organisms . the criteria may also be applied within any specified geographical or political area , although in such cases special notice should be taken of point 14 . in presenting the results of applying the criteria , the taxonomic unit and area under consideration should be specified in accordance with the documentation guidelines ( see annex 3 ) . the categorization process should only be applied to wild populations inside their natural range , and to populations resulting from benign introductions . the latter are defined in the iucn guidelines for re - introductions ( iucn 1998 ) as ' . . . an attempt to establish a species , for the purpose of conservation , outside its recorded distribution , but within an appropriate habitat and eco - geographical area . this is a feasible conservation tool only when there is no remaining area left within a species ' historic range ' .
extinction is a chance process . thus , a listing in a higher extinction risk category implies a higher expectation of extinction , and over the time - frames specified more taxa listed in a higher category are expected to go extinct than those in a lower one ( without effective conservation action ) . however , the persistence of some taxa in high - risk categories does not necessarily mean their initial assessment was inaccurate .
all taxa listed as critically endangered qualify for vulnerable and endangered , and all listed as endangered qualify for vulnerable . together these categories are described as ' threatened ' . the threatened categories form a part of the overall scheme . it will be possible to place all taxa into one of the categories ( see figure 1 ) .
for listing as critically endangered , endangered or vulnerable there is a range of quantitative criteria ; meeting any one of these criteria qualifies a taxon for listing at that level of threat . each taxon should be evaluated against all the criteria . even though some criteria will be inappropriate for certain taxa ( some taxa will never qualify under these however close to extinction they come ) , there should be criteria appropriate for assessing threat levels for any taxon . the relevant factor is whether any one criterion is met , not whether all are appropriate or all are met . because it will never be clear in advance which criteria are appropriate for a particular taxon , each taxon should be evaluated against all the criteria , and all criteria met at the highest threat category must be listed .
the different criteria ( a - e ) are derived from a wide review aimed at detecting risk factors across the broad range of organisms and the diverse life histories they exhibit . the quantitative values presented in the various criteria associated with threatened categories were developed through wide consultation , and they are set at what are generally judged to be appropriate levels , even if no formal justification for these values exists . the levels for different criteria within categories were set independently but against a common standard . broad consistency between them was sought .
the criteria for the threatened categories are to be applied to a taxon whatever the level of conservation action affecting it . it is important to emphasise here that a taxon may require conservation action even if it is not listed as threatened . conservation actions which may benefit the taxon are included as part of the documentation requirements ( see annex 3 ) .
the criteria are clearly quantitative in nature . however , the absence of high - quality data should not deter attempts at applying the criteria , as methods involving estimation , inference and projection are emphasised as being acceptable throughout . inference and projection may be based on extrapolation of current or potential threats into the future ( including their rate of change ) , or of factors related to population abundance or distribution ( including dependence on other taxa ) , so long as these can reasonably be supported . suspected or inferred patterns in the recent past , present or near future can be based on any of a series of related factors , and these factors should be specified as part of the documentation .
taxa at risk from threats posed by future events of low probability but with severe consequences ( catastrophes ) should be identified by the criteria ( e . g . small distributions , few locations ) . some threats need to be identified particularly early , and appropriate actions taken , because their effects are irreversible or nearly so ( e . g . , pathogens , invasive organisms , hybridization ) .
the data used to evaluate taxa against the criteria are often estimated with considerable uncertainty . such uncertainty can arise from any one or all of the following three factors : natural variation , vagueness in the terms and definitions used , and measurement error . the way in which this uncertainty is handled can have a strong influence on the results of an evaluation . details of methods recommended for handling uncertainty are included in annex 1 , and assessors are encouraged to read and follow these principles .
in general , when uncertainty leads to wide variation in the results of assessments , the range of possible outcomes should be specified . a single category must be chosen and the basis for the decision should be documented ; it should be both precautionary and credible .
when data are very uncertain , the category of ' data deficient ' may be assigned . however , in this case the assessor must provide documentation showing that this category has been assigned because data are inadequate to determine a threat category . it is important to recognize that taxa that are poorly known can often be assigned a threat category on the basis of background information concerning the deterioration of their habitat and / or other causal factors ; therefore the liberal use of ' data deficient ' is discouraged .
listing in the categories of not evaluated and data deficient indicates that no assessment of extinction risk has been made , though for different reasons . until such time as an assessment is made , taxa listed in these categories should not be treated as if they were non - threatened . it may be appropriate ( especially for data deficient forms ) to give them the same degree of attention as threatened taxa , at least until their status can be assessed .
all assessments should be documented . threatened classifications should state the criteria and subcriteria that were met . no assessment can be accepted for the iucn red list as valid unless at least one criterion is given . if more than one criterion or subcriterion is met , then each should be listed . if a re - evaluation indicates that the documented criterion is no longer met , this should not result in automatic reassignment to a lower category of threat ( downlisting ) . instead , the taxon should be re - evaluated against all the criteria to clarify its status . the factors responsible for qualifying the taxon against the criteria , especially where inference and projection are used , should be documented ( see annexes 2 and 3 ) . the documentation requirements for other categories are also specified in annex 3 .
the category of threat is not necessarily sufficient to determine priorities for conservation action . the category of threat simply provides an assessment of the extinction risk under current circumstances , whereas a system for assessing priorities for action will include numerous other factors concerning conservation action such as costs , logistics , chances of success , and other biological characteristics of the subject .
re - evaluation of taxa against the criteria should be carried out at appropriate intervals . this is especially important for taxa listed under near threatened , data deficient and for threatened taxa whose status is known or suspected to be deteriorating .
a taxon may be moved from a category of higher threat to a category of lower threat if none of the criteria of the higher category has been met for five years or more .
if the original classification is found to have been erroneous , the taxon may be transferred to the appropriate category or removed from the threatened categories altogether , without delay ( but see point 10 above ) .
the term ' population ' is used in a specific sense in the red list criteria that is different to its common biological usage . population is here defined as the total number of individuals of the taxon . for functional reasons , primarily owing to differences between life forms , population size is measured as numbers of mature individuals only . in the case of taxa obligately dependent on other taxa for all or part of their life cycles , biologically appropriate values for the host taxon should be used .
subpopulations are defined as geographically or otherwise distinct groups in the population between which there is little demographic or genetic exchange ( typically one successful migrant individual or gamete per year or less ) .
the number of mature individuals is the number of individuals known , estimated or inferred to be capable of reproduction . when estimating this quantity , the following points should be borne in mind :
mature individuals that will never produce new recruits should not be counted ( e . g . densities are too low for fertilization ) .
in the case of populations with biased adult or breeding sex ratios , it is appropriate to use lower estimates for the number of mature individuals , which take this into account .
where the population size fluctuates , use a lower estimate . in most cases this will be much less than the mean .
reproducing units within a clone should be counted as individuals , except where such units are unable to survive alone ( e . g . corals ) .
in the case of taxa that naturally lose all or a subset of mature individuals at some point in their life cycle , the estimate should be made at the appropriate time , when mature individuals are available for breeding .
re - introduced individuals must have produced viable offspring before they are counted as mature individuals .
generation length is the average age of parents of the current cohort ( i . e . newborn individuals in the population ) . generation length therefore reflects the turnover rate of breeding individuals in a population . generation length is greater than the age at first breeding and less than the age of the oldest breeding individual , except in taxa that breed only once . where generation length varies under threat , the more natural , i . e . pre - disturbance , generation length should be used .
a reduction is a decline in the number of mature individuals of at least the amount ( % ) stated under the criterion over the time period ( years ) specified , although the decline need not be continuing . a reduction should not be interpreted as part of a fluctuation unless there is good evidence for this . the downward phase of a fluctuation will not normally count as a reduction .
a continuing decline is a recent , current or projected future decline ( which may be smooth , irregular or sporadic ) which is liable to continue unless remedial measures are taken . fluctuations will not normally count as continuing declines , but an observed decline should not be considered as a fluctuation unless there is evidence for this .
extreme fluctuations can be said to occur in a number of taxa when population size or distribution area varies widely , rapidly and frequently , typically with a variation greater than one order of magnitude ( i . e . a tenfold increase or decrease ) .
the phrase ' severely fragmented ' refers to the situation in which increased extinction risk to the taxon results from the fact that most of its individuals are found in small and relatively isolated subpopulations ( in certain circumstances this may be inferred from habitat information ) . these small subpopulations may go extinct , with a reduced probability of recolonization .
extent of occurrence is defined as the area contained within the shortest continuous imaginary boundary which can be drawn to encompass all the known , inferred or projected sites of present occurrence of a taxon , excluding cases of vagrancy ( see figure 2 ) . this measure may exclude discontinuities or disjunctions within the overall distributions of taxa ( e . g . large areas of obviously unsuitable habitat ) ( but see ' area of occupancy ' , point 10 below ) . extent of occurrence can often be measured by a minimum convex polygon ( the smallest polygon in which no internal angle exceeds 180 degrees and which contains all the sites of occurrence ) .
figure 2 . two examples of the distinction between extent of occurrence and area of occupancy . ( a ) is the spatial distribution of known , inferred or projected sites of present occurrence . ( b ) shows one possible boundary to the extent of occurrence , which is the measured area within this boundary . ( c ) shows one measure of area of occupancy which can be achieved by the sum of the occupied grid squares .
the term ' location ' defines a geographically or ecologically distinct area in which a single threatening event can rapidly affect all individuals of the taxon present . the size of the location depends on the area covered by the threatening event and may include part of one or many subpopulations . where a taxon is affected by more than one threatening event , location should be defined by considering the most serious plausible threat .
a quantitative analysis is defined here as any form of analysis which estimates the extinction probability of a taxon based on known life history , habitat requirements , threats and any specified management options . population viability analysis ( pva ) is one such technique . quantitative analyses should make full use of all relevant available data . in a situation in which there is limited information , such data as are available can be used to provide an estimate of extinction risk ( for instance , estimating the impact of stochastic events on habitat ) . in presenting the results of quantitative analyses , the assumptions ( which must be appropriate and defensible ) , the data used and the uncertainty in the data or quantitative model must be documented .
extinct ( ex ) a taxon is extinct when there is no reasonable doubt that the last individual has died . a taxon is presumed extinct when exhaustive surveys in known and / or expected habitat , at appropriate times ( diurnal , seasonal , annual ) , throughout its historic range have failed to record an individual . surveys should be over a time frame appropriate to the taxon ' s life cycle and life form .
extinct in the wild ( ew ) a taxon is extinct in the wild when it is known only to survive in cultivation , in captivity or as a naturalized population ( or populations ) well outside the past range . a taxon is presumed extinct in the wild when exhaustive surveys in known and / or expected habitat , at appropriate times ( diurnal , seasonal , annual ) , throughout its historic range have failed to record an individual . surveys should be over a time frame appropriate to the taxon ' s life cycle and life form .
critically endangered ( cr ) a taxon is critically endangered when the best available evidence indicates that it meets any of the criteria a to e for critically endangered ( see section v ) , and it is therefore considered to be facing an extremely high risk of extinction in the wild .
endangered ( en ) a taxon is endangered when the best available evidence indicates that it meets any of the criteria a to e for endangered ( see section v ) , and it is therefore considered to be facing a very high risk of extinction in the wild .
vulnerable ( vu ) a taxon is vulnerable when the best available evidence indicates that it meets any of the criteria a to e for vulnerable ( see section v ) , and it is therefore considered to be facing a high risk of extinction in the wild .
near threatened ( nt ) a taxon is near threatened when it has been evaluated against the criteria but does not qualify for critically endangered , endangered or vulnerable now , but is close to qualifying for or is likely to qualify for a threatened category in the near future .
least concern ( lc ) a taxon is least concern when it has been evaluated against the criteria and does not qualify for critically endangered , endangered , vulnerable or near threatened . widespread and abundant taxa are included in this category .
data deficient ( dd ) a taxon is data deficient when there is inadequate information to make a direct , or indirect , assessment of its risk of extinction based on its distribution and / or population status . a taxon in this category may be well studied , and its biology well known , but appropriate data on abundance and / or distribution are lacking . data deficient is therefore not a category of threat . listing of taxa in this category indicates that more information is required and acknowledges the possibility that future research will show that threatened classification is appropriate . it is important to make positive use of whatever data are available . in many cases great care should be exercised in choosing between dd and a threatened status . if the range of a taxon is suspected to be relatively circumscribed , and a considerable period of time has elapsed since the last record of the taxon , threatened status may well be justified .
not evaluated ( ne ) a taxon is not evaluated when it is has not yet been evaluated against the criteria .
note : as in previous iucn categories , the abbreviation of each category ( in parenthesis ) follows the english denominations when translated into other languages ( see annex 2 ) .
( e ) the effects of introduced taxa , hybridization , pathogens , pollutants , competitors or parasites .
e . quantitative analysis showing the probability of extinction in the wild is at least 50 % within 10 years or three generations , whichever is the longer ( up to a maximum of 100 years ) .
a . severely fragmented or known to exist at no more than five locations .
e . quantitative analysis showing the probability of extinction in the wild is at least 20 % within 20 years or five generations , whichever is the longer ( up to a maximum of 100 years ) .
a . severely fragmented or known to exist at no more than 10 locations .
1 . population size estimated to number fewer than 1 , 000 mature individuals .
2 . population with a very restricted area of occupancy ( typically less than 20 km 2 ) or number of locations ( typically five or fewer ) such that it is prone to the effects of human activities or stochastic events within a very short time period in an uncertain future , and is thus capable of becoming critically endangered or even extinct in a very short time period .
e . quantitative analysis showing the probability of extinction in the wild is at least 10 % within 100 years .
the red list criteria should be applied to a taxon based on the available evidence concerning its numbers , trend and distribution . in cases where there are evident threats to a taxon through , for example , deterioration of its only known habitat , a threatened listing may be justified , even though there may be little direct information on the biological status of the taxon itself . in all these instances there are uncertainties associated with the available information and how it was obtained . these uncertainties may be categorized as natural variability , semantic uncertainty and measurement error ( akçakaya et al . 2000 ) . this section provides guidance on how to recognize and deal with these uncertainties when using the criteria . more information is available in the guidelines for using the iucn red list criteria .
natural variability results from the fact that species ' life histories and the environments in which they live change over time and space . the effect of this variation on the criteria is limited , because each parameter refers to a specific time or spatial scale . semantic uncertainty arises from vagueness in the definition of terms or lack of consistency in different assessors ' usage of them . despite attempts to make the definitions of the terms used in the criteria exact , in some cases this is not possible without the loss of generality . measurement error is often the largest source of uncertainty ; it arises from the lack of precise information about the parameters used in the criteria . this may be due to inaccuracies in estimating the values or a lack of knowledge . measurement error may be reduced or eliminated by acquiring additional data . for further details , see akçakaya et al . ( 2000 ) and burgman et al . ( 1999 ) .
one of the simplest ways to represent uncertainty is to specify a best estimate and a range of plausible values . the best estimate itself might be a range , but in any case the best estimate should always be included in the range of plausible values . when data are very uncertain , the range for the best estimate might be the range of plausible values . there are various methods that can be used to establish the plausible range . it may be based on confidence intervals , the opinion of a single expert , or the consensus opinion of a group of experts . whichever method is used should be stated and justified in the documentation .
when interpreting and using uncertain data , attitudes toward risk and uncertainty may play an important role . attitudes have two components . first , assessors need to consider whether they will include the full range of plausible values in assessments , or whether they will exclude extreme values from consideration ( known as dispute tolerance ) . an assessor with a low dispute tolerance would include all values , thereby increasing the uncertainty , whereas an assessor with a high dispute tolerance would exclude extremes , reducing the uncertainty . second , assessors need to consider whether they have a precautionary or evidentiary attitude to risk ( known as risk tolerance ) . a precautionary attitude will classify a taxon as threatened unless it is certain that it is not threatened , whereas an evidentiary attitude will classify a taxon as threatened only when there is strong evidence to support a threatened classification . assessors should resist an evidentiary attitude and adopt a precautionary but realistic attitude to uncertainty when applying the criteria , for example , by using plausible lower bounds , rather than best estimates , in determining population size , especially if it is fluctuating . all attitudes should be explicitly documented .
an assessment using a point estimate ( i . e . single numerical value ) will lead to a single red list category . however , when a plausible range for each parameter is used to evaluate the criteria , a range of categories may be obtained , reflecting the uncertainties in the data . a single category , based on a specific attitude to uncertainty , should always be listed along with the criteria met , while the range of plausible categories should be indicated in the documentation ( see annex 3 ) .
where data are so uncertain that any category is plausible , the category of ' data deficient ' should be assigned . however , it is important to recognize that this category indicates that the data are inadequate to determine the degree of threat faced by a taxon , not necessarily that the taxon is poorly known or indeed not threatened . although data deficient is not a threatened category , it indicates a need to obtain more information on a taxon to determine the appropriate listing ; moreover , it requires documentation with whatever available information there is .
under section v ( the criteria for critically endangered , endangered and vulnerable ) there is a hierarchical alphanumeric numbering system of criteria and subcriteria . these criteria and subcriteria ( all three levels ) form an integral part of the red list assessment and all those that result in the assignment of a threatened category must be specified after the category . under the criteria a to c and d under vulnerable , the first level of the hierarchy is indicated by the use of numbers ( 1 - 4 ) and if more than one is met , they are separated by means of the ' + ' symbol . the second level is indicated by the use of the lower - case alphabet characters ( a - e ) . these are listed without any punctuation . a third level of the hierarchy under criteria b and c involves the use of lower case roman numerals ( i - v ) . these are placed in parentheses ( with no space between the preceding alphabet character and start of the parenthesis ) and separated by the use of commas if more than one is listed . where more than one criterion is met , they should be separated by semicolons . the following are examples of such usage :
all assessments published on the iucn red list are freely available for public use . to ensure assessments are fully justified and to allow red list assessment data to be analysed , thus making the iucn red list a powerful tool for conservation and policy decisions , a set of supporting information is required to accompany every assessment submitted for publication on the iucn red list of threatened species ™ :
required supporting information under specific conditions ( e . g . taxa assessed under specific red list categories or criteria , plant assessments , reassessed taxa , etc . ) .
tools available for preparing and submitting assessments for the iucn red list , including the iucn species information service ( sis ) and ramas® red list ( akçakaya and ferson 2001 ) .
note that the documentation standards and consistency checks for iucn red list assessments and species accounts will be updated on a regular basis .
click here for a summary of the five criteria ( a - e ) used to evaluate if a taxon belongs in an iucn red list threatened category ( critically endangered , endangered or vulnerable ) .
akçakaya , h . r . and ferson , s . 2001 . ramas ® red list : threatened species classifications under uncertainty . version 2 . 0 . applied biomathematics , new york .
akçakaya , h . r . , ferson , s . , burgman , m . a . , keith , d . a . , mace , g . m . and todd , c . a . 2000 . making consistent iucn classifications under uncertainty . conservation biology 14 : 1001 - 1013 .
baillie , j . and groombridge , b . ( eds ) . 1996 . 1996 iucn red list of threatened animals . iucn , gland , switzerland .
burgman , m . a . , keith , d . a . and walshe , t . v . 1999 . uncertainty in comparative risk analysis of threatened australian plant species . risk analysis 19 : 585 - 598 .
fitter , r . and fitter , m . ( eds ) . 1987 . the road to extinction . iucn , gland , switzerland .
gärdenfors , u . , hilton - taylor , c . , mace , g . , and rodríguez , j . p . , 2001 . the application of iucn red list criteria at regional levels . conservation biology 15 : 1206 - 1212 .
hilton - taylor , c . ( compiler ) . 2000 . 2000 iucn red list of threatened species . iucn , gland , switzerland and cambridge , uk .
iucn . 1993 . draft iucn red list categories . iucn , gland , switzerland .
iucn . 1994 . iucn red list categories . prepared by the iucn species survival commission . iucn , gland , switzerland .
iucn . 1996 . resolution 1 . 4 . species survival commission . resolutions and recommendations , pp . 7 - 8 . world conservation congress , 13 - 23 october 1996 , montreal , canada . iucn , gland , switzerland .
iucn . 1998 . guidelines for re - introductions . prepared by the iucn / ssc re - introduction specialist group . iucn , gland , switzerland and cambridge , uk .
iucn . 2001 . iucn red list categories and criteria : version 3 . 1 . iucn species survival commission . iucn , gland , switzerland and cambridge , uk .
iucn . 2003 . guidelines for application of iucn red list criteria at regional levels : version 3 . 0 . iucn species survival commission . iucn , gland , switzerland and cambridge , uk .
iucn . 2012 . guidelines for application of iucn red list criteria at regional and national levels : version 4 . 0 . gland , switzerland and cambridge , uk : iucn .
iucn / ssc criteria review working group . 1999 . iucn red list criteria review provisional report : draft of the proposed changes and recommendations . species 31 - 32 : 43 - 57 .
mace , g . m . , collar , n . , cooke , j . , gaston , k . j . , ginsberg , j . r . , leader - williams , n . , maunder , m . and milner - gulland , e . j . 1992 . the development of new criteria for listing species on the iucn red list . species 19 : 16 ? 22 .
mace , g . m . and lande , r . 1991 . assessing extinction threats : toward a re - evaluation of iucn threatened species categories . conservation biology 5 : 148 ? 157 .
mace , g . m . and stuart , s . n . 1994 . draft iucn red list categories , version 2 . 2 . species 21 - 22 : 13 - 24 .
oldfield , s . , lusty , c . and mackinven , a . 1998 . the world list of threatened trees . world conservation press , cambridge .
carrasco , p . a . , mattoni , c . i . , leynaud , g . c . and scrocchi , g . j . 2012 . morphology , phylogeny and taxonomy of south american bothropoid pitvipers ( serpentes , viperidae ) . zoologica scripta 41 : 1 - 15 .
critically endangered b1ab ( iii ) + 2ab ( iii ) ver 3 . 1
hilton - taylor , c . & pollock , c . m . ( red list programme office )
justification : the alcatrazes lancehead is known only from one location : a small island off southeastern brazil ( total area 1 . 35 km² ) . although the species is relatively common on the island , its highly restricted range and continuing decline in habitat quality , as a result of the island being used target practice by the brazilian navy , qualify the species for the critically endangered category .
current population size is unknown , although the species is relatively common on the island .
the species is active both on the ground and on low vegetation within the atlantic forest covering alcatrazes island .
alcatrazes island is currently used as a naval target practice area . such activities are threatening the habitat of the island , which in turn poses a threat to the species present on the island . since this snake is known only from this area , habitat disturbance is a particular threat to the population .
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note : tdwg regions are generated automatically from the text in the distribution field and not in every cases it works well . we are working on it .
venomous ! conservation : one of the 30 most endangered viper species ( maritz et al . 2016 ) .
carrasco , p . a . , c . i . mattoni , g . c . leynaud , and g . j . scrocchi . 2012 . morphology , phylogeny and taxonomy of south american bothropoid pitvipers ( serpentes , viperidae ) . zoologica scripta 41 : 109 - 124 - get paper here
maritz , bryan ; johannes penner , marcio martins , jelka crnobrnja - isailović , stephen spear , laura r . v . alencar , jesús sigala - rodriguez , kevin messenger , rulon w . clark , pritpal soorae , luca luiselli , chris jenkins , harry w . greene 2016 . identifying global priorities for the conservation of vipers biological conservation , doi : 10 . 1016 / j . biocon . 2016 . 05 . 004 - get paper here
wallach , van ; kenneth l . williams , jeff boundy 2014 . snakes of the world : a catalogue of living and extinct species . taylor and francis , crc press , 1237 pp .
this database is maintained by peter uetz ( database content ) and jakob hallermann , zoological museum hamburg ( new species and updates ) .
is known only from alcatrazes island ( 1 . 35 km ) , the largest of four small islands of alcatrazes archipelago , approximately 35 km from the coast of so paulo , southeastern brazil .
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warning : the ncbi web site requires javascript to function . more . . .
comp biochem physiol c toxicol pharmacol . 2005 jun ; 141 ( 2 ) : 117 - 23 .
laboratório de herpetologia , instituto butantan , av . vital brasil , 1500 , 05503 - 900 , são paulo , sp , brazil . fatifurtado @ urltoken
general shape small in length , moderately slender bodied pitviper . can grow to a maximum of about 0 . 58 metres . head is broad , flattened , lance shaped when viewed from above and distinct from narrow neck . snout is not elevated . eyes are medium in size with vertically elliptical pupils . dorsal scales are strongly keeled .
habitat lowland atlantic forest island habitat . the island has an area of about 1 . 35 square kilometers and maximum elevation about 266 metres above sea level .
habits mainly a terrestrial and nocturnal snake with arboreal tendencies . often found in low vegetation .
general : dangerousness unknown , but potentially lethal envenoming , though unlikely , cannot be excluded .
general : cardiotoxicity no case reports for this species , but related species can cause hyperkalaemic cardiotoxicity secondary to myolysis .
description : first aid for bites by viperid snakes likely to cause significant local injury at the bite site ( see listing in comments section ) .
general approach to management all cases should be treated as urgent & potentially lethal . rapid assessment & commencement of treatment including appropriate antivenom ( if indicated & available ) is mandatory . admit all cases .
antivenom therapy antivenom is the key treatment for systemic envenoming . multiple doses may be required .
address : contiguo a la plaza de deportes , dulce nombre de coronado . san josé costa rica
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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 .
disclaimer : the animal diversity web is an educational resource written largely by and for college students . adw doesn ' t cover all species in the world , nor does it include all the latest scientific information about organisms we describe . though we edit our accounts for accuracy , we cannot guarantee all information in those accounts . while adw staff and contributors provide references to books and websites that we believe are reputable , we cannot necessarily endorse the contents of references beyond our control .
this material is based upon work supported by the national science foundation grants drl 0089283 , drl 0628151 , due 0633095 , drl 0918590 , and due 1122742 . additional support has come from the marisla foundation , um college of literature , science , and the arts , museum of zoology , and information and technology services .
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it was described by lower in 1920 .

the wingspan is about 10 mm .

the forewings are white , faintly tinged with ochreous and with ochreous-fuscous markings .

the hindwings are pale fuscous .

notodryas encrita

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machaeritis encrita lower , 1920 ; trans . proc . r . soc . s . aust . 44 : 65
notodryas encrita is a moth in the family epermeniidae . it was described by lower in 1920 . it is found in australia , where it has been recorded from south australia and victoria .
notodryas is a genus of moths in the epermeniidae family . its species all occur in australia .
notodryas callierga meyrick , 1906 ; trans . r . soc . s . aust . 30 : 56
notodryas aeria meyrick , 1897 ; proc . linn . soc . n . s . w . 22 ( 2 ) : 427
notodryas vallata meyrick , 1897 ; proc . linn . soc . n . s . w . 22 ( 2 ) : 428
notodryas meyrick , 1897 ; proc . linn . soc . n . s . w . 22 ( 2 ) : 427 ; ts : notodyras aeria meyrick
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lower , o . b . 1920 ,
new australian lepidoptera
, transactions of the royal society of south australia , vol . 44 , pp . 58 - 70
urn : lsid : biodiversity . org . au : afd . taxon : 619dab83 - 64a0 - 4a87 - ba1f - 77f4b7a9adaf
urn : lsid : biodiversity . org . au : afd . taxon : 3ef08d39 - f19f - 4541 - 82a8 - 2e64c03199b6
urn : lsid : biodiversity . org . au : afd . name : 330552
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meyrick , 1906 descriptions of australian tineina trans . r . soc . s . aust . 30 : 33 - 66
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the wingspan is about 10 mm . the forewings are white , faintly tinged with ochreous and with ochreous - fuscous markings . the hindwings are pale fuscous .
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dichomeris argentaria is a moth in the gelechiidae family .

it was described by meyrick in 1913 .

it is found in south africa ( mpumalanga ) .

the wingspan is 13-14 mm .

the forewings are light yellow-ochreous with the costal edge slenderly suffused with dark fuscous from the base almost to the apex , beneath this with a faint pale iridescent-silvery streak from the base to two-third .

a similar slender silvery streak is found along the fold from the base to one-fourth , and two silvery streaks from the costa before and beyond the middle converging towards the dorsum beyond the middle .

the dorsal area beneath the fold is deep ferruginous , paler towards the base , the dorsum suffused with dark fuscous on the posterior half .

there is a dark brown trapezoidal blotch resting on the dorsum and reaching half across the wing , its upper edge excavated , the corners of this excavation marked with two black dots .

there is also a slender dark grey terminal fascia crossed by four black marks .

the hindwings are grey , rather darker posteriorly .

dichomeris argentaria

this is the place for argentaria definition . you find here argentaria meaning , synonyms of argentaria and images for argentaria copyright 2017 © urltoken
here you will find one or more explanations in english for the word argentaria . also in the bottom left of the page several parts of wikipedia pages related to the word argentaria and , of course , argentaria synonyms and on the right images related to the word argentaria .
dichomeris argentaria meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 304 ; tl : barberton
dichomeris acmodeta ; ponomarenko , 1997 , far east . ent . 50 : 12
dichomeris agorastis ; ponomarenko , 1997 , far east . ent . 50 : 13
dichomeris albula ; ponomarenko , 1997 , far east . ent . 50 : 13
dichomeris apicispina ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris apludella ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris bifurca ; ponomarenko , 1997 , far east . ent . 50 : 15
dichomeris bomiensis ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris bucinaria ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris consertella ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris cuprea ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris cuspis ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris diffurca ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris fareasta ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris fuscahopa ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris fuscanella ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris gansuensis ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris hodgesi ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris jiangxiensis ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris lativalvata ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris lespedezae ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris lutilinea ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris manticopodina ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris menglana ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris millotella viette , 1956 ; nat . malgache 8 ( 2 ) : 212
dichomeris minutia ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris mitteri ; ponomarenko , 1997 , far east . ent . 50 : 27
dichomeris molybdoterma meyrick , 1933 ; exotic microlep . 4 ( 12 ) : 353
dichomeris ningshanensis ; ponomarenko , 1997 , far east . ent . 50 : 27
dichomeris nivalis ; ponomarenko , 1997 , far east . ent . 50 : 27
dichomeris paulianella viette , 1956 ; nat . malgache 8 ( 2 ) : 213
dichomeris polygona ; ponomarenko , 1997 , far east . ent . 50 : 29
dichomeris polypunctata ; ponomarenko , 1997 , far east . ent . 50 : 29
dichomeris qingchengshanensis ; ponomarenko , 1997 , far east . ent . 50 : 30
dichomeris quadratipalpa ; ponomarenko , 1997 , far east . ent . 50 : 30
dichomeris quadrifurca ; ponomarenko , 1997 , far east . ent . 50 : 30
dichomeris sexafurca ; ponomarenko , 1997 , far east . ent . 50 : 31
dichomeris shenae ; ponomarenko , 1997 , far east . ent . 50 : 31
dichomeris spicans ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris spuracuminata ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris stasimopa meyrick , 1937 ; exotic microlep . 5 ( 3 ) : 94
dichomeris strictella ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris synergastis ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris tersa ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris varifurca ; ponomarenko , 1997 , far east . ent . 50 : 34
dichomeris violacula ; ponomarenko , 1997 , far east . ent . 50 : 34
dichomeris wuyiensis ; ponomarenko , 1997 , far east . ent . 50 : 34
dichomeris yuebana ; ponomarenko , 1997 , far east . ent . 50 : 34
dichomeris yunnanensis ; ponomarenko , 1997 , far east . ent . 50 : 35
dichomeris zymotella viette , 1956 ; nat . malgache 8 ( 2 ) : 215
dichomeris fuliginella ( costa , 1836 ) , described as rhinosia fuliginella from italy .
dichomeris junisonensis matsumura , 1931 ; 6000 illust . insects japan . - empire : 1082
dichomeris acritopa meyrick , 1935 ; mat . microlep . fauna chin . prov . : 72
dichomeris dolichaula meyrick , 1931 ; exotic microlep . 4 ( 2 - 4 ) : 67
dichomeris loxonoma meyrick , 1937 ; exotic microlep . 5 ( 4 - 5 ) : 123
dichomeris nyingchiensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 254
dichomeris fuscahopa li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 242
dichomeris fuscusitis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 243
dichomeris gansuensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 247
dichomeris hodgesi li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 232
dichomeris jiangxiensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 244
dichomeris junisonis [ sic ] ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris yunnanensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 254
dichomeris cuspis park , 1994 ; insecta koreana 11 : 19 ; tl : gangweon prov . , korea
dichomeris derasella ; ponomarenko , 1997 , far east . ent . 50 : 19 ; [ fe ]
dichomeris fareasta park , 1994 ; insecta koreana 11 : 15 ; tl : gangweon prov . , korea
dichomeris lamprostoma ; ponomarenko , 1997 , far east . ent . 50 : 23 ; [ fe ]
dichomeris mitteri park , 1994 ; insecta koreana 11 : 17 ; tl : gangweon prov . , korea
dichomeris praevacua ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 :
dichomeris strictella park , 1994 ; insecta koreana 11 : 11 ; tl : gangweon prov . , korea
dichomeris acritopa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 12
dichomeris adelocentra ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 13
dichomeris albiscripta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 13
dichomeris allantopa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 13
dichomeris amphichlora ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 13
dichomeris ampliata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris anisospila ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris antiloxa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris antisticta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris asodes ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 15
dichomeris barymochla ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 15
dichomeris brachygrapha ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris brachyptila ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris caerulescens ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris cellaria ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris centracma ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris ceponoma ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris charonaea ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris chartaria ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris chinganella ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris chlanidota ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris cinnabarina ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris citharista ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris clarescens ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris cocta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 17
dichomeris contentella ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris corniculata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris crepitatrix ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris deceptella ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 19
dichomeris deltoxyla ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 19
dichomeris diacrita ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 19
dichomeris dicausta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 19
dichomeris doxarcha ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris eridantis ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris eucomopa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris excoriata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris ferrata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris ferruginosa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris frenigera ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris fungifera ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris geochrota ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris horoglypta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris ignorata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris illicita ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris illucescens ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris imbricata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris immerita ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris indiserta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris intensa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris isoclera ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris leptosaris ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris leucothicta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 24
dichomeris levigata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 24
dichomeris lissota ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 24
dichomeris litoxyla ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 24
dichomeris lupata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris macroxyla ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris malachias ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris malacodes ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris melanortha ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris melitura ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris mesoglena ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris metatoxa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris metuens ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris microdoxa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 26
dichomeris microsphena meyrick , 1921 ; zool . meded . leyden 6 : 166 ; tl : java , buitenzorg
dichomeris oceanis ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 27
dichomeris olivescens ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 28
dichomeris ostracodes ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 28
dichomeris pelitis ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 28
dichomeris petalodes ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 28
dichomeris planata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 29
dichomeris polyaema ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 29
dichomeris praealbescens ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 29
dichomeris procrossa ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 29
dichomeris pseudometra ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 30
dichomeris ptychosema ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 30
dichomeris sciodora ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 31
dichomeris semnias ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 31
dichomeris siranta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 31
dichomeris summata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris synclepta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris tephroxesta ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris testudinata ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris tetraschema ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris thyrsicola ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris toxolyca ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris traumatias ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris uranopis ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris viridella ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 34
dichomeris indigna ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 54 ( note )
dichomeris ceratomoxantha ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 63 ( note )
dichomeris adelocentra meyrick , 1920 ; exotic microlep . 2 ( 10 ) : 305 ; tl : java , butenzorg
dichomeris albula park & hodges , 1995 ; insecta koreana 12 : 22 ; tl : taipei co . , taiwan
dichomeris baccata meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 621 ; tl : brazil , teffé
= dichomeris bisignella ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 16
dichomeris brachygrapha meyrick , 1920 ; exotic microlep . 2 ( 10 ) : 305 ; tl : assam , khasis
dichomeris bucinaria park , 1996 ; tinea 14 ( 4 ) : 230 ; tl : pintung co . , taiwan
dichomeris chalcophaea meyrick , 1921 ; exotic microlep . 2 ( 14 ) : 434 ; tl : queensland , brisbane
dichomeris fida meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 620 ; tl : brazil , para
dichomeris fusca park & hodges , 1995 ; insecta koreana 12 : 49 ; tl : taichung co . , taiwan
dichomeris fuscalis park & hodges , 1995 ; insecta koreana 12 : 16 ; tl : taipei co . , taiwan
dichomeris harmonias meyrick , 1922 ; exotic microlep . 2 ( 16 ) : 504 ; tl : china , shanghai
dichomeris horiodes meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 620 ; tl : brazil , parintins
dichomeris horoglypta meyrick , 1932 ; exotic microlep . 4 ( 7 ) : 202 ; tl : hasimoto , japan
dichomeris ingloria meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 621 ; tl : peru , lima
dichomeris leptosaris meyrick , 1932 ; exotic microlep . 4 ( 7 ) : 202 ; tl : hokkaido , japan
dichomeris leucothicta meyrick , 1919 ; exotic microlep . 2 ( 8 ) : 235 ; tl : bombay , dharwar
dichomeris lucrifuga meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 620 ; tl : brazil , para
dichomeris lutivittata meyrick , 1921 ; exotic microlep . 2 ( 14 ) : 434 ; tl : queensland , brisbane
dichomeris mesoctenis meyrick , 1921 ; exotic microlep . 2 ( 14 ) : 434 ; tl : queensland , brisbane
dichomeris mesoglena meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 619 ; tl : coorg , pollibetta
dichomeris metuens meyrick , 1932 ; exotic microlep . 4 ( 7 ) : 201 ; tl : seneng , java
dichomeris ochthophora meyrick , 1936 ; exotic microlep . 5 ( 2 ) : 46 ; tl : taihoku , formosa
dichomeris orientis park & hodges , 1995 ; insecta koreana 12 : 36 ; tl : kaohsiung co . , taiwan
dichomeris praevacua meyrick , 1922 ; exotic microlep . 2 ( 16 ) : 504 ; tl : china , shanghai
dichomeris quercicola meyrick , 1921 ; exotic microlep . 2 ( 14 ) : 433 ; tl : punjab , kangra
dichomeris saturata meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 621 ; tl : brazil , obidos
dichomeris sciodora meyrick , 1922 ; exotic microlep . 2 ( 16 ) : 504 ; tl : assam , khasis
dichomeris symmetrica park & hodges , 1995 ; insecta koreana 12 : 20 ; tl : taitung co . , taiwan
dichomeris syndias [ sic , recte syndyas ] ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris thermodryas meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 621 ; tl : peru , iquitos
dichomeris trilobella park & hodges , 1995 ; insecta koreana 12 : 42 ; tl : pingtung co . , taiwan
dichomeris anisospila meyrick , 1934 ; dt . ent . z . iris 48 : 34 ; tl : guangdong , china
dichomeris cotifera meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 303 ; tl : barberton
dichomeris cuprea li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 237 ; tl : shaanxi
dichomeris exsecta meyrick , 1927 ; exot . microlep . 3 ( 12 ) : 354 ; tl : rhodesia , mazoe
dichomeris ignorata meyrick , 1921 ; zool . meded . leyden 6 : 165 ; tl : java , preangor , 5000ft
dichomeris melanortha meyrick , 1929 ; exot . microlep . 3 ( 16 ) : 510 ; tl : bombay , poona
dichomeris monorbella viette , 1988 ; bull . soc . ent . fr . 93 ( 3 - 4 ) : 104
dichomeris squalens meyrick , 1914 ; trans . ent . soc . lond . 1914 : 282 ; tl : british guiana
resupina omelko , 1999 ; keys ins . russian far east 5 ( 2 ) : 107 ; ts : dichomeris okadai moriuti
dichomeris tactica meyrick , 1918 ; exotic microlep . 2 ( 5 ) : 152 ; tl : ecuador , huigra , 4500ft
dichomeris acrolychna meyrick , 1922 ; trans . ent . soc . lond . 1922 : 112 ; tl : brazil , para
dichomeris allantopa meyrick , 1934 ; exotic microlep . 4 ( 16 - 17 ) : 512 ; tl : nilambur , madras
dichomeris alogista meyrick , 1935 ; mat . microlep . fauna chin . prov . : 72 ; tl : hunan , china
dichomeris brachymetra meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 620 ; tl : peru , chosica , 2800m
dichomeris brachyptila meyrick , 1916 ; exot . microlep . 1 ( 19 ) : 584 ; tl : upper burma , myitkyina
dichomeris ceponoma meyrick , 1918 ; exotic microlep . 2 ( 5 ) : 151 ; tl : coorg , dibidi , 3500ft
dichomeris davisi park & hodges , 1995 ; insecta koreana 12 : 35 ; tl : taiwan , taipei co . , sirin
dichomeris ellipsias meyrick , 1922 ; trans . ent . soc . lond . 1922 : 114 ; tl : peru , iquitos
dichomeris lushanae park & hodges , 1995 ; insecta koreana 12 : 22 ; tl : taiwan , taipei co . , sozan
dichomeris moriutii ; li , zhen , kendrick & sterling , 2010 , shilap revta lepid . 38 ( 149 ) : 73
dichomeris physocoma meyrick , 1926 ; exot . microlep . 3 ( 9 ) : 286 ; tl : sierra leone , mabang
dichomeris procyphodes meyrick , 1922 ; trans . ent . soc . lond . 1922 : 115 ; tl : brazil , parintins
dichomeris rhodophaea meyrick , 1920 ; in alluaud & jeannel , voyage afr . orientale , ins . lép . 2 : 73
dichomeris simaoensis ; li , zhen , kendrick & sterling , 2010 , shilap revta lepid . 38 ( 149 ) : 74
dichomeris stratigera meyrick , 1922 ; trans . ent . soc . lond . 1922 : 111 ; tl : brazil , parintins
dichomeris subdentata meyrick , 1922 ; trans . ent . soc . lond . 1922 : 113 ; tl : brazil , santarem
dichomeris testudinata meyrick , , 1934 ; dt . ent . z . iris 48 : 34 ; tl : guangdong , china
dichomeris thalamopa meyrick , 1922 ; trans . ent . soc . lond . 1922 : 112 ; tl : brail , téffe
dichomeris xanthodeta meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 305 ; tl : three sisters
dichomeris zonata ; li , zhen , kendrick & sterling , 2010 , shilap revta lepid . 38 ( 149 ) : 74
dichomeris liui li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 234 ; tl : jiangxi , china
dichomeris qinlingensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 235 ; tl : shaanxi , china
dichomeris aequata meyrick , 1914 ; trans . ent . soc . lond . 1914 : 282 ; tl : british guiana , bartica
dichomeris agathopa meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 85 ; tl : rhodesia , umtali
dichomeris anisacuminata li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 231 ; tl : china , jiangxi
dichomeris antizyga meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 303 ; tl : barberton , pretoria
dichomeris aphanopa meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 83 ; tl : rhodesia , umtali
dichomeris apicispina li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 241 ; tl : jiangxi , china
dichomeris asteropis meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 83 ; tl : rhodesia , umvuma
dichomeris attenta meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 84 ; tl : rhodesia , umvuma
dichomeris bifurca li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 251 ; tl : jiangxi , china
dichomeris bodenheimeri ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 16 ; [ afromoths ]
dichomeris bomiensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 238 ; tl : china , xizang
dichomeris cachrydias meyrick , 1914 ; trans . ent . soc . lond . 1914 : 283 ; tl : british guiana , mallali
dichomeris decusella ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 19 ; [ afromoths ]
dichomeris diffurca li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 253 ; tl : fujian , china
dichomeris eustacta meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 84 ; tl : rhodesia , umtali
dichomeris excepta meyrick , 1914 ; exot . microlep . 1 ( 9 ) : 279 ; tl : nyassaland , mt . mlanje
dichomeris hylurga meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 83 ; tl : rhodesia , salisbury
dichomeris impigra meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 305 ; tl : barberton , haenertsburg
dichomeris indiserta meyrick , 1926 ; exot . microlep . 3 ( 9 ) : 285 ; tl : malay states , kuala lumpur
dichomeris lativalvata li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 248 ; tl : jiangxi , china
dichomeris manticopodina li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 239 ; tl : shaanxi , china
dichomeris menglana li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 257 ; tl : yunnan , china
dichomeris ningshanensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 245 ; tl : shaanxi , china
dichomeris nivalis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 249 ; tl : jiangxi , china
dichomeris opsonoma meyrick , 1914 ; trans . ent . soc . lond . 1914 : 281 ; tl : british guiana , bartica
dichomeris pladarota meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 84 ; tl : rhodesia , umtali
dichomeris polygona li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 243 ; tl : sichuan , china
dichomeris qingchengshanensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 245 ; tl : sichuan , china
dichomeris quadratipalpa li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 238 ; tl : shaanxi , china
dichomeris quadrifurca li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 252 ; tl : fujian , china
dichomeris sexafurca li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 249 ; tl : jiangxi , china
dichomeris shenae li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 246 ; tl : jiangxi , china
dichomeris spicans li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 247 ; tl : jiangxi , china
dichomeris spuracuminata li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 230 ; tl : shaanxi , china
dichomeris stromatias meyrick , 1918 ; ann . transv . mus . 6 ( 2 ) : 23 ; tl : zululand , nkwaleni
dichomeris tersa li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 241 ; tl : shaanxi , china
dichomeris varifurca li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 250 ; tl : jiangxi , china
dichomeris violacula li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 237 ; tl : gansu , china
dichomeris wuyiensis li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 255 ; tl : jiangxi , china
dichomeris xestobyrsa meyrick , 1921 ; ann . transv . mus . 8 ( 2 ) : 82 ; tl : rhodesia , salisbury
dichomeris yuebana li & zheng , 1996 ; shilap revta lepid . 24 ( 95 ) : 236 ; tl : shaanxi , china
dichomeris obscura li & zheng , 1997 ; entomologia sin . 4 ( 3 ) : 223 ; tl : fengxian , shaanxi , 1600m
dichomeris angustiptera li & zheng , 1997 ; entomologia sin . 4 ( 3 ) : 228 ; tl : fengxian , shaanxi , 1600m
dichomeris acrogypsa turner , 1919 ; proc . r . soc . qd 31 ( 10 ) : 168 ; tl : queensland , rosewood
dichomeris aculata ; ponomarenko & ueda , 2004 , trans . lepid . soc . japan 55 ( 3 ) : 147 ( note )
dichomeris ampliata meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 175 ; tl : khasis
dichomeris cirrhostola turner , 1919 ; proc . r . soc . qd 31 ( 10 ) : 169 ; tl : queensland , adavale
dichomeris deltaspis ; ponomarenko & ueda , 2004 , trans . lepid . soc . japan 55 ( 3 ) : 155 ( note )
dichomeris excoriata meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 174 ; tl : khasis
dichomeris ferrata meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 174 ; tl : khasis
dichomeris ferrogra li & wang , 1997 ; entomologia sin . 4 ( 3 ) : 225 ; tl : mengla , yunnan , 630m
dichomeris ferruginosa meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 173 ; tl : khasis
dichomeris heteracma meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 622 ; tl : brazil , teffé ; peru , iquitos
dichomeris instans meyrick , 1923 ; exotic microlep . 2 ( 20 ) : 619 ; tl : peru , iquitos ; brazil , teffé
dichomeris lividula park & hodges , 1995 ; insecta koreana 12 : 57 ; tl : taiwan , hualien co . , pianau - col
dichomeris oleata meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 305 ; tl : barberton , three sisters
dichomeris ostracodes meyrick , 1916 ; exot . microlep . 1 ( 19 ) : 583 ; tl : upper burma , lashio , 3000ft
dichomeris petalodes meyrick , 1934 ; exotic microlep . 4 ( 16 - 17 ) : 512 ; tl : nilambur , madras , india
dichomeris pleuroleuca turner , 1919 ; proc . r . soc . qd 31 ( 10 ) : 169 ; tl : queensland , eidsvold
dichomeris ptychosema meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 175 ; tl : khasis
dichomeris rectifascia li & zheng , 1997 ; entomologia sin . 4 ( 3 ) : 220 ; tl : kangxian , gansu , 800m
dichomeris simaoensis li & wang , 1997 ; entomologia sin . 4 ( 3 ) : 221 ; tl : simao , yunnan , 325m
dichomeris summata meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 172 ; tl : khasis
dichomeris varronia busck , 1913 ; ins . inscit . menstr . 1 ( 7 ) : 89 ; tl : kitty , british guiana
dichomeris ventosa meyrick , 1913 ; ann . transv . mus . 3 ( 4 ) : 304 ; tl : barberton , three sisters
dichomeris zonata li & wang , 1997 ; entomologia sin . 4 ( 3 ) : 222 ; tl : simao , yunnan , 325m
dichomeris tostella ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 72 ( note ) ; [ nhm card ]
dichomeris amphicoma meyrick , 1912 ; trans . ent . soc . lond . 1911 ( 4 ) : 695 ; tl : brazil , santos
dichomeris antisticha meyrick , 1926 ; exot . microlep . 3 ( 9 ) : 285 ; tl : costa rica , vulkan irazu , 4000ft
dichomeris fluitans meyrick , 1920 ; ann . s . afr . mus . 17 ( 4 ) : 284 ; tl : natal , howick
dichomeris litoxyla meyrick , 1937 ; exotic microlep . 5 ( 4 - 5 ) : 123 ; tl : yakovlevka , primorkii krai , russia
dichomeris nessica walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 95 ; tl : panama , la chorrera
dichomeris taiwana park & hodges , 1995 ; insecta koreana 12 : 48 ; tl : taiwan , nantou co . , sunmoon lake , 760m
dichomeris zomias meyrick , 1914 ; trans . ent . soc . lond . 1914 : 283 ; tl : british guiana , bartica and mallali
dichomeris hirculella busck , 1909 ; proc . ent . soc . wash . 11 ( 2 ) : 89 ; tl : east river , connecticut
dichomeris clarescens meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 174 ; tl : maskeliya , ceylon
dichomeris dysorata turner , 1919 ; proc . r . soc . qd 31 ( 10 ) : 170 ; tl : new south wales , syndey
dichomeris elegans park , 2001 ; insecta koreana 18 ( 4 ) : 308 ; tl : taiwan , pingtung co . , kenting park , 50m
dichomeris jugata walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 97 ; tl : mexico , tabasco , teapa
dichomeris mengdana li & zheng , 1997 ; entomologia sin . 4 ( 3 ) : 227 ; tl : mengda , xunhua , qinghai , 2240m
dichomeris miltophragma meyrick , 1922 ; trans . ent . soc . lond . 1922 : 115 ; tl : brazil , para , obidos , parintins
dichomeris ptilocompa meyrick , 1922 ; trans . ent . soc . lond . 1922 : 113 ; tl : brazil , teffé ; peru , jurimaguas
dichomeris substratella walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 93 ; tl : mexico , tabasco , teapa
dichomeris vadonella viette , 1955 ; ann . soc . ent . fr . 123 : 108 ; tl : ne . madagascar , maroantsetra , ambodivoangy
dichomeris xerodes walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 100 ; tl : mexico , tabasco , teapa
= dichomeris setosella ; sattler , 1973 , bull . br . mus . nat . hist . ( ent . ) 28 ( 4 ) : 221
dichomeris glenni clarke , 1947 ; proc . ent . soc . wash . 49 ( 7 ) : 187 ; tl : putnam co . , illinois
dichomeris aomoriensis ; ponomarenko , 1997 , far east . ent . 50 : 14 ; ponomarenko , 1998 , far east . ent . 67 : 12
dichomeris ardesiella walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 96 ; tl : mexico , vera cruz , cordova
dichomeris arotrosema walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 95 ; tl : mexico , vera cruz , atoyac
dichomeris asodes meyrick , 1939 ; trans . r . ent . soc . lond . 89 ( 4 ) : 54 ; tl : telawa , java
dichomeris erixantha ; meyrick , 1921 , ann . transv . mus . 8 ( 2 ) : 83 ; [ nhm card ] ; [ afromoths ]
dichomeris eucomopa meyrick , 1939 ; trans . r . ent . soc . lond . 89 ( 4 ) : 54 ; tl : telawa , java
dichomeris loxospila ; [ nhm card ] ; li , zhen , kendrick & sterling , 2010 , shilap revta lepid . 38 ( 149 ) : 77
dichomeris lypetica walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 91 ; tl : mexico , guerrero , amula , 6000ft
dichomeris crepitatrix meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 173 ; tl : n . coorg , 3500ft
dichomeris dignella walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 91 ; tl : mexico , guerrero , amula , 6000ft
dichomeris excavata busck , 1914 ; proc . u . s . nat . mus . 47 ( 2043 ) : 18 ; tl : porto bello , panama
dichomeris hexasticta walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 94 ; tl : mexico , guerrero , amula , 6000ft
dichomeris imbricata meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 175 ; tl : n . coorg , 3500ft
dichomeris lutea park & hodges , 1995 ; insecta koreana 12 : 59 ; tl : taiwan , nantou co . , meifeng , 30km s tayuling , 2200m
dichomeris lutilinea ponomarenko & park , 1996 ; korean j . appl . ent . 35 ( 2 ) : 118 ; tl : chuncheon , kangweon prov .
dichomeris metrodes meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 172 ; tl : hambantota , ceylon ; bombay
dichomeris olivescens meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 175 ; tl : kandy and maskeliya , ceylon
dichomeris thalpodes meyrick , 1922 ; trans . ent . soc . lond . 1922 : 111 ; tl : brazil , para ; peru , r . napo
dichomeris tristicta busck , 1914 ; proc . u . s . nat . mus . 47 ( 2043 ) : 17 ; tl : trinidad river , panama
dichomeris melanophylla ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 114 ( note ) ; [ nhm card ] ; [ aucl ]
dichomeris angulata ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 14 ; ponomarenko , 1997 , far east . ent . 50 : 14
dichomeris bulawskii ponomarenko & park , 1996 ; korean j . appl . ent . 35 ( 2 ) : 114 ; tl : 27km sw slavjanka , primorskii krai
dichomeris fusca ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 60 ; ponomarenko , 1997 , far east . ent . 50 : 49
dichomeris linealis ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 83 ; ponomarenko , 1997 , far east . ent . 50 : 24
dichomeris lividula ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 83 ; ponomarenko , 1997 , far east . ent . 50 : 24
dichomeris lushanae ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 86 ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris lutea ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 86 ; ponomarenko , 1997 , far east . ent . 50 : 25
dichomeris ochreata ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 102 ; ponomarenko , 1997 , far east . ent . 50 : 27
dichomeris taiwana ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 135 ; ponomarenko , 1997 , far east . ent . 50 : 32
dichomeris trilobella ; brown , adamski , hodges & bahr , 2004 , zootaxa 510 : 141 ; ponomarenko , 1997 , far east . ent . 50 : 33
dichomeris illusio hodges , 1986 ; moths amer . n of mexico 7 . 1 : 101 , pl . 2 , f . 38 ; tl : hastings , florida
dichomeris imitata hodges , 1986 ; moths amer . n of mexico 7 . 1 : 104 , pl . 3 , f . 5 ; tl : devers , texas
dichomeris angulata park & hodges , 1995 ; insecta koreana 12 : 43 ; tl : taiwan , nantou co . , leinhauchi forest station , 15km sw puli , 750m
dichomeris aprica ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 15 ; li & sattler , 2012 , zootaxa 3373 : 57
dichomeris enoptrias ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 20
dichomeris hoplocrates ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 22
dichomeris issikii ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 23
dichomeris ochreata park & hodges , 1995 ; insecta koreana 12 : 32 ; tl : taiwan , nantou co . , mei - feng , 30km s tayuling , 2200m
dichomeris pyrrhoschista ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 30
dichomeris sciritis ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 31 ; li & sattler , 2012 , zootaxa 3373 : 57
dichomeris synergastis ponomarenko & park , 1996 ; korean j . appl . ent . 35 ( 2 ) : 116 ; tl : yong - in , kyunggi prov .
dichomeris viridescens ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 34
dichomeris offula hodges , 1986 ; moths amer . n of mexico 7 . 1 : 117 , pl . 3 , f . 21 ; tl : ithaca , new york
dichomeris crepida hodges , 1986 ; moths amer . n of mexico 7 . 1 : 118 , pl . 3 , f . 22 ; tl : mcclellanville , south carolina
dichomeris santarosensis hodges , 1985 ; proc . ent . soc . wash . 87 ( 2 ) : 456 ; tl : santa rosa national park , guanacaste , costa rica
dichomeris nenia hodges , 1986 ; moths amer . n of mexico 7 . 1 : 40 , pl . 4 , f . 2 ; tl : bandera co . , texas
dichomeris hypochloa walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 102 , pl . 3 , f . 23 ; tl : mexico , sonora
dichomeris caia hodges , 1986 ; moths amer . n of mexico 7 . 1 : 62 , pl . 4 , f . 7 ; tl : putnam co . , illinois
dichomeris laetitia hodges , 1986 ; moths amer . n of mexico 7 . 1 : 88 , pl . 2 , f . 22 ; tl : putnam co . , illinois
dichomeris aleatrix hodges , 1986 ; moths amer . n of mexico 7 . 1 : 91 , pl . 2 , f . 27 ; tl : putnam co . , illinois
dichomeris furia hodges , 1986 ; moths amer . n of mexico 7 . 1 : 93 , pl . 2 , f . 30 ; tl : putnam co . , illinois
dichomeris baxa hodges , 1986 ; moths amer . n of mexico 7 . 1 : 105 , pl . 3 , f . 10 ; tl : presidio of monterey , california
dichomeris cinnamicostella ; walsingham , 1911 , biol . centr . - amer . lep . heterocera 4 : 103 ; [ nhm card ] ; [ sangmi lee & richard brown ]
dichomeris costalis busck , 1914 ; proc . u . s . nat . mus . 47 ( 2043 ) : 18 ; tl : tabogilla i . and porto bello , panama
dichomeris habrochitona walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 102 , pl . 3 , f . 26 ; tl : panama , tabernilla
dichomeris quercicola ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 30 ; ponomarenko , 1998 , far east . ent . 67 : 13
dichomeris carycina ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 43 ( note ) ; [ nhm card ] ; [ sangmi lee & richard brown ]
dichomeris caryophragma ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 43 ( note ) ; [ nhm card ] ; [ sangmi lee & richard brown ]
dichomeris diacnista ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 43 ( note ) ; [ nhm card ] ; [ sangmi lee & richard brown ]
dichomeris lypetica ; [ nhm card ] ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 54 ( note ) ; [ sangmi lee & richard brown ]
dichomeris tactica ; [ nhm card ] ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 60 ( note ) ; [ sangmi lee & richard brown ]
dichomeris latescens ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 63 ( note ) ; [ nhm card ] ; [ sangmi lee & richard brown ]
dichomeris siren hodges , 1986 ; moths amer . n of mexico 7 . 1 : 64 , pl . 4 , f . 9 ; tl : henson creek , oxon hill , maryland
dichomeris vindex hodges , 1986 ; moths amer . n of mexico 7 . 1 : 83 , pl . 2 , f . 9 - 10 ; tl : putnam co . , illinois
dichomeris gleba hodges , 1986 ; moths amer . n of mexico 7 . 1 : 87 , pl . 2 , f . 18 - 20 ; tl : putnam co . , illinois
dichomeris legnotoa hodges , 1986 ; moths amer . n of mexico 7 . 1 : 101 , pl . 4 , f . 10 ; tl : largo , pinellas co . , florida
dichomeris mimesis hodges , 1986 ; moths amer . n of mexico 7 . 1 : 101 , pl . 2 , f . 39 ; tl : salmon , anderson co . , texas
dichomeris simulata hodges , 1986 ; moths amer . n of mexico 7 . 1 : 104 , pl . 3 , f . 4 ; tl : canadian , hemphill co . , texas
dichomeris percnopolis walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 93 , pl . 3 , f . 11 ; tl : guatemala , zapote , 2000ft
dichomeris renascens walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 96 , pl . 3 , f . 14 ; tl : mexico , tabasco , teapa
dichomeris xuthostola walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 101 , pl . 3 , f . 18 ; tl : mexico , tabasco , teapa
dichomeris sylphe hodges , 1986 ; moths amer . n of mexico 7 . 1 : 58 , pl . 1 , f . 22 ; tl : archbold biological staion , lake placid , florida
dichomeris ardelia hodges , 1986 ; moths amer . n of mexico 7 . 1 : 62 , pl . 4 , f . 8 ; tl : archbold biological station , lake placid , florida
dichomeris kimballi hodges , 1986 ; moths amer . n of mexico 7 . 1 : 71 , pl . 1 , f . 30 ; tl : archbold biological staion , lake placid , florida
dichomeris aglaia hodges , 1986 ; moths amer . n of mexico 7 . 1 : 85 , pl . 2 , f . 15 ; tl : lake placid , florida , archbold biological station
dichomeris anisacuminata ; ponomarenko , 1997 , far east . ent . 50 : 14 ; li , zhen , kendrick & sterling , 2010 , shilap revta lepid . 38 ( 149 ) : 74
dichomeris argigastra walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 99 , pl . 3 , f . 16 ; tl : mexico , vera cruz , atoyac
dichomeris autometra ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 15 ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 )
dichomeris crambaleas ; [ nhm card ] ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 18
dichomeris melanota walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 94 , pl . 3 , f . 13 ; tl : mexico , vera cruz , cordova
dichomeris okadai ; [ nhm card ] ; park & hodges , 1995 , insecta koreana 12 : ( 1 - 101 ) ; ponomarenko , 1997 , far east . ent . 50 : 28
dichomeris prensans meyrick , 1922 ; trans . ent . soc . lond . 1922 : 111 ; tl : brazil , para , parintins , manaos ; peru , iquitos ; british guiana , bartica
dichomeris sciastes walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 90 , pl . 3 , f . 10 ; tl : mexico , vera cruz , atoyac
dichomeris gausapa hodges , 1986 ; moths amer . n of mexico 7 . 1 : pl . 1 , f . 8 ; tl : madera canyon , 4880 ' , santa rita mts , arizona
= dichomeris acuminata ; ponomarenko , 1997 , far east . ent . 50 : 13 ; [ sangmi lee & richard brown ] ; lee , hodges & brown , 2009 , zootaxa 2231 : 34
dichomeris solatrix hodges , 1986 ; moths amer . n of mexico 7 . 1 : 48 , pl . 1 , f . 15 ; tl : peña blanca canyon , santa cruz co . arizona
= dichomeris punctidiscella ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 56 ; [ nhm card ] ; lee , hodges & brown , 2009 , zootaxa 2231 : 36
dichomeris copa hodges , 1986 ; moths amer . n of mexico 7 . 1 : 92 , pl . 2 , f . 28 ; tl : snyder heights 1100 ' , ithaca , new york
dichomeris achne hodges , 1986 ; moths amer . n of mexico 7 . 1 : 87 , pl . 2 , f . 34 ; tl : parker is . , highlands co . , florida
dichomeris euprepes hodges , 1986 ; moths amer . n of mexico 7 . 1 : 110 , pl . 4 , f . 11 ; tl : big black mnts , letcher co . , kentucky
dichomeris carinella walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 99 , pl . 3 , f . 20 ; tl : mexico , guerrero , amula , 6000ft
dichomeris fuscusitis ; ponomarenko , 1997 , far east . ent . 50 : 21 ; zhao , park , bae & li , 2017 , zootaxa 4273 ( 2 ) : ( 216 - 234 )
dichomeris intensa meyrick , 1913 ; j . bombay nat . hist . soc . 22 ( 1 ) : 173 ; tl : maskeliya and puttalam , ceylon ; cuddapah , 4000ft , n . coorg
dichomeris leucostena walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 94 , pl . 3 , f . 12 ; tl : mexico , guerrero , amula , 6000ft
dichomeris blanchardorum hodges , 1986 ; moths amer . n of mexico 7 . 1 : 43 , pl . 1 , f . 10 - 11 ; tl : laguna atascosa , cameron co . , texas
dichomeris gnoma hodges , 1986 ; moths amer . n of mexico 7 . 1 : 106 , pl . 3 , f . 11 ; tl : shingle creek road , keremeos , british columbia , canada
dichomeris mercatrix hodges , 1986 ; moths amer . n of mexico 7 . 1 : 110 , pl . 3 , f . 15 ; tl : mclean bogs reserve , tompkins co . , new york
dichomeris bulawskii ; ponomarenko , 1997 , far east . ent . 50 : 16 ; ponomarenko & ueda , 2004 , trans . lepid . soc . japan 55 ( 3 ) : 151 ( note )
dichomeris diva hodges , 1986 ; moths amer . n of mexico 7 . 1 : 57 , pl . 1 , f . 21 ; tl : 1 mi s patagonia , santa cruz co . , arizona
dichomeris fistuca hodges , 1986 ; moths amer . n of mexico 7 . 1 : 68 , pl . 1 , f . 25 ; tl : wedge plantation , mccellanville , charleston co . , south carolina
dichomeris atomogypsa ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 72 ( note ) ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 15
dichomeris alphito hodges , 1986 ; moths amer . n of mexico 7 . 1 : 88 , pl . 2 , f . 21 ; tl : madera canyon , 4880 ' , santa rita mts , arizona
dichomeris pelta hodges , 1986 ; moths amer . n of mexico 7 . 1 : 99 , pl . 2 , f . 36 ; tl : wedge plantation , mcclellanville , charleston co . , south carolina
dichomeris acrochlora ; hodges , 1986 , moths amer . n of mexico 7 . 1 : 112 ( note ) ; [ nhm card ] ; ponomarenko , 1997 , far east . ent . 50 : 12
dichomeris sybilla hodges , 1986 ; moths amer . n of mexico 7 . 1 : 121 , pl . 3 , f . 24 ; tl : madera canyon , 4880 ' , santa rita mts , arizona
dichomeris evitata walsingham , 1911 ; biol . centr . - amer . lep . heterocera 4 : 99 , pl . 3 , f . 15 ; tl : panama , volcan de chiriqui , 2000 - 3000ft
dichomeris harmonias ; [ nhm card ] ; park , 1991 , ann . hist . - nat . mus . hung . 83 : 121 ; ponomarenko , 1997 , far east . ent . 50 : 21
dichomeris xanthoa hodges , 1986 ; moths amer . n of mexico 7 . 1 : 102 , pl . 3 , f . 2 ; tl : ft . niobrara national wildlife refuge , cherry co . , nebraska
dichomeris bolize hodges , 1986 ; moths amer . n of mexico 7 . 1 : 100 , pl . 2 , f . 37 ; tl : hackberry lake , valentine national wildlife refuge , cherry co . , nebraska
dichomeris isa hodges , 1986 ; moths amer . n of mexico 7 . 1 : 103 , pl . 3 , f . 3 ; tl : tenkiller lake , 3 mi w blackgum , sequoyah co . , oklahoma