Int. J. Aquat. Biol. (2015) 3(5): 282-289 

E-ISSN: 2322-5270; P-ISSN: 2383-0956

Journal homepage: www.ij-aquaticbiology.com 

© 2015 Iranian Society of Ichthyology 

Review Article 

Review of the Silversides of Iran (Family Atherinidae) 

 
Brian W. Coad*1 

 
Canadian Museum of Nature, Ottawa, Ontario, K1P 6P4 Canada.

 
Article history: 
Received 2 May 2015 

Accepted 27 July 2015 

Available online 2 5 October 2015 

 

Keywords: Atherina, Biology, Morphology, Caspian Sea. 

Abstract: The silversides are found in coastal areas of temperate to tropical seas and in fresh water. 
There are about 14 genera and 68 species with only one native species in the Caspian Sea basin, 

Atherina caspia. In this review, the systematics, morphology, distribution, biology, economic 

importance and conservation of the Caspian silverside of Iran are described, the species is illustrated, 

and a bibliography on this fish in Iran is provided. 

 
 

Introduction 

The freshwater ichthyofauna of Iran comprises a 

diverse set of families and species. These form 

important elements of the aquatic ecosystem and a 

number of species are of commercial or other 

significance. The literature on these fishes is widely 

scattered, both in time and place. Summaries of the 

morphology and biology of these species were given 

in a website (www.briancoad.com) which is updated 

here for one family, while the relevant section of that 

website is now closed down. Other families will also 

being addressed in a similar fashion. 

 

Family Carcharhinidae 

The silversides or sand smelts are found in coastal 

areas of temperate to tropical seas and in fresh water. 

There are about 14 genera and 68 species (Nelson, 

2006; Eschmeyer and Fong, 2011) with only one 

reported from the Caspian Sea and Iran. Coad (1987, 

1998) and Coad and Abdoli (1996) place this species 

in context with the Iranian ichthyofauna. Most are 

small fishes with a maximum length of 60 cm.  

These small, silvery fishes have a moderately 

elongate body, usually cycloid and moderately large 

scales, no lateral line but sometimes a pit on each 

                                                           
* Corresponding author: Brian W. Coad 

E-mail address: bcoad@mus-nature.ca 

scale, small teeth in the jaws and sometimes on the 

roof of the terminal, upwardly-directed mouth, wide 

gill openings with branchiostegal membranes free of 

the isthmus, 5-6 branchiostegal rays, gill rakers 

usually long and slender, two well-separated dorsal 

fins, the first with 3-10 unbranched but flexible rays, 

and the second with 1-2 unbranched and the rest 

branched rays, anal fin long, pectoral fins high on the 

flank, no pyloric caeca, egg membranes with 

filamentous outgrowths, back bluish to greenish with 

small melanophores but translucent, and a silvery 

stripe along the flank, often distinctively outlined 

with black. 

Silversides can occur in vast schools in inshore 

waters and are an important item in the diet of other 

fishes. They have been used as bait but are too bony 

to be much used as food. Their food is plankton. 

Eggs are large and greenish. The sticky egg filaments 

entangle with plants, rocks or sand as anchors until 

hatching.  

Genus Atherina Linnaeus, 1758 
Members of this genus are found in fresh and 

brackish waters with a single representative in Iran. 

The record of Atherina hepsetus Linnaeus, 1758 in 
the Caspian Sea by Quignard and Pras in Whitehead 



283 
 

Coad/Silversides of Iran 

et al. (1984-1986) is an error (Vasil'eva, 1994).  

The body is compressed with a rounded belly, the 

mouth large and terminal, jaws large, reaching back 

to the anterior eye level or beyond, sides of the upper 

jaw are straight and premaxillaries protractile, the 

dentary bone has a high central portion, a 

preopercular notch is absent, rows of setiform teeth 

on the jaws, vomer and palatines, cycloid scales 

extending onto the head, short pectoral fins, vent 

nearer the pelvic fin origin than the anal fin, 

numerous gill rakers, 5-10 flexible rays in the first 

dorsal fin, and the second dorsal fin is similar in 

length to the anal fin with its origin above the anal 

fin. 

Atherina caspia Eichwald, 1831 
(Figs. 1-2) 

Common names: Shisheh mahi (= glass fish), gol 
azin mahi (= flower decoration fish), atrinka (from 

the Russian). [aterinka or xazar aterini in Azerbaijan; 

kaspi aterinasy in Turkmenian; Kaspiiskaya aterinka 

or Caspian silverside in Russian; Caspian silverside, 

Caspian sand smelt, big-scale sand smelt].  

Systematics: Formerly called Atherina mochon 
pontica natio caspia Eichwald, 1831 or Atherina 
mochon caspia in Caspian Sea literature.  
Atherina mochon Cuvier, 1829 was described 
originally from Ivasa and Atherina presbyter pontica 
Eichwald, 1831 from near Odessa, Ukraine. The 

Caspian Sea taxon was also known as Atherina 
boyeri Risso, 1810. Atherina boyeri was originally 
described from the sea shore and lower course of 

rivers in the Département du Var, France. 

Reshetnikov et al. (1997) give the date for this 

species as 1826.  

Atherina presbyter var. caspia Eichwald, 1831 
described from "in Caspii maris littore australiore, 

sinu balchanensi" (i.e., southern shore of the Caspian 

Sea, Balkhan Bay) was considered a synonym of 

Atherina boyeri. Naseka and Bogutskaya (2009) 
consider caspia to be a full species and this is 
followed by Esmaeili et al. (2014). 

Syntypes of A. boyeri are in the Muséum national 
d'Histoire naturelle, Paris under MNHN A-4342 (2) 

and MNHN B-860 (1) (Eschmeyer's "Catalog of 

Fishes", downloaded 29 August 2007). No types are 

known for Atherina presbyter var. caspia. 
Bamber and Henderson (1985) demonstrated how 

the morphology of Atherina presbyter around Britain 
varies according to temperature and salinity during 

embryonic development. Isolation of populations 

results in local selection and random genetic drift 

and thus recognisable morphologies but these were 

not recognised as distinct. Kottelat (1997) reviewed 

literature reports of variation in this species in the 

Mediterranean and Black seas and neighbouring 

fresh waters and concludes that lacustrine 

populations should be called A. boyeri while marine 
populations are A. mochon. The status of Caspian 
populations was not commented on. These studies 

showed how variable these related silversides are 

and why the definition and limitation of species has 

been varied.  

The silverside in the Caspian Sea was referred to as 

Atherina boyeri caspia by Savenkova and Asanov 
(1991) and by Vasil'eva (1994, 1996) and this 

seemed a reasonable step as the population is 

isolated from other populations in the Atlantic Ocean 

and Mediterranean Sea. The subspecies was 

Figure 1. Line drawing of Atherina caspia by S. Laurie-Bourque. 



284 
 

Int. J. Aquat. Biol. (2015) 3(5): 282-289 

characterised by a reduced number of infraorbital 

bones (3 bones in Caspian Sea fish as opposed to 4 

in Black Sea fish; apparently infraorbital bones 2 and 

3 fuse), a reduced number of gill rakers (generally 

19-27 as opposed to 27-37), and the form of the 

maxilla (the inferior margin in Caspian Sea fish is 

always smooth while in the Black Sea and Sea of 

Azov a "wing" is usually developed). However, 

Kiener and Spillman (1972) allocated Caspian 

populations to this subspecies on the basis of larger 

size, hardly an adequate criterion. Vasil'eva (1994) 

makes the allocation based on a reduced number of 

gill rakers, reduction of the number of bones around 

the eye to three (preorbital, infraorbital and 

postorbital) and a smooth lower margin to the 

maxilla without a wing protuberance.  

Dobrovolov and Ivanova (1999) studied two non-

enzymatic proteins and 11 enzymes for putative 

Atherina boyeri and A. mochon pontica. They 
concluded that these are distinct species and indeed 

the Black Sea fish are a distinct species, A. pontica. 
They diverged 2.316 MYA. These authors did not 

examine Caspian Sea material. Miller in Miller 

(2003) followed a conservative approach, regarding 

the various named and wide-ranging populations as 

representing a single polymorphic species.  

Key characters: The two dorsal fins, cycloid scales, 
pectoral fin high on the flank and the vent remote 

from the anal fin are characteristic.  

Morphology: First dorsal fin spines 5-10, second 
dorsal fin with 1-2 spines and 8-15 soft rays, anal fin 

with 1-2 spines and 9-18 soft rays, pectoral branched 

rays 10-17, usually 12-15, pelvic fin with 1 spine 5-

7, usually 5, branched rays, lateral series scales 37-

53 (possibly to 61, see Vasil'eva (1994)), total gill 

rakers 19-29 in the Caspian Sea, spinulose on the 

interior surface, and long and reaching about 7 rakers 

along the arch when appressed, and vertebrae 39-52. 

Note narrower ranges for all preceding meristic 

characters for Iranian material given below. The 

anus is 4-5 scales in advance of the anal fin. Scales 

are higher than broad, with slight indentations on the 

otherwise straight dorsal and ventral margins, a 

rounded posterior margin, and a wavy to rounded 

anterior margin with a protuberant central point. 

There are no radii. Circuli are restricted to the 

anterior third of the scale with a central and vertical 

roughened area posterior to the circuli, presumably 

made up of fragmented circuli. The focus is central. 

The lower jaw symphysis fits into a notch in the 

upper jaws. The haemal arches of the anterior 4-7 

caudal vertebrae are expanded around the gas 

bladder. The gut is s-shaped. The chromosome 

number is 2n=48 (Klinkhardt et al., 1995).  

Meristic values for Iranian specimens are: first dorsal 

fin spines 8(28), 9(5) or 10(1); second dorsal fin soft 

rays 11(10), 12(21), 13(2) or 14(1), anal fin soft rays 

13(7), 14(15), 15(9) or 16(3), pectoral fin branched 

rays 12(1), 13(12), 14(14) or 15(6), pelvic fin 

branched rays 5 (34), caudal fin branched rays 13(1), 

15(30), 16(2) or 17(1), lateral series scales 50(1), 

51(10), 52(5), 53(3), 54(8), 55(3), 56(3) or 57(1), 

predorsal scales 17(1), 18(2), 19(12), 20(8), 21(3), 

22(3), 23(1), 24(3) or 26(1), caudal peduncle scales 

12(31), 13(2) or 14(1), transverse scales from anal 

fin antero-dorsally 10(2), 11(6), 12(23) or 13(3), 

total gill rakers 24(3), 25(4), 26(14), 27(8), 28(4) or 

29(1), and total vertebrae 45(1), 46(19), 47(7) or 

Figure 2. Atherina caspia, Anzali Shore, December 2009, courtesy of K. Abbasi. 



285 
 

Coad/Silversides of Iran 

48(7).  

Sexual dimorphism: Females tend to be larger than 
males and there are some differences in 

morphometrics and meristics (Ghoorbanalidoost et 

al., 2003).  

Colour: General colour is given in the family 
account. The lateral band is strongly developed and 

bright in Caspian Sea specimens. The belly is white, 

fins are pale to translucent grey. Lagoon specimens 

are brownish or grey-brown on the back. The 

peritoneum is brown to black, eggs being encased in 

a black peritoneum while the abdomen wall is a light 

brown.  

Size: Reaches 11.8 cm and 17.6 g in the Atrak River 
(Savenkova and Asanaov, 1991), to 14.5 cm 

standard length in the Caspian Sea basin generally 

(Henderson and Bamber, 1987). Kiener and 

Spillman (1972) found a maximum of 15.4 cm in 

their Caspian Sea sample and Patimar et al. (2009) 

found 12.8 cm total length for their sample of 2256 

fish in the Gomishan Wetland.  

Distribution: Found in the Caspian Sea and the 
Uzboi Valley of Turkmenistan. In Iran, it is reported 

along the whole Caspian Sea coast, and from the 

Safid, Tajan, Tonekabon, Havigh, Karkan, Chalus, 

Farahabad, Langarud, Siahrud, Sheikan, Shafa, Talar 

and Atrak rivers, Gomishan Lagoon or Wetland, 

Boojagh Wetland, Anzali Lagoon and the Sowsar 

Roga outlet of the lagoon seasonally, the Caspian 

Sea at Bandar Anzali breakwater and beach, Hasan 

Kiadeh, Kazian Beach and west of Chalus, Gorgan 

Bay, Alma-Gol, Adji-Gol and Ala-Gol (Savenkova 

and Asanov, 1991; Holčík and Oláh, 1992; Roshan 

Tabari, 1997; Karimpour, 1998; Abbasi et al., 1999; 

Kiabi et al., 1999; Afraie and Lalooie, 2000; Khara 

et al., 2004; Abbasi, 2006; Patimar, 2008b; Abdoli 

and Naderi, 2009; Patimar et al., 2009; Esmaeili et 

al., 2014).  

Zoogeography: This species probably entered the 
Caspian Sea from the Black Sea during Khvalyn 

transgression (10-70,000 years B.P.) via the Kumo-

Manych Depression (Kosarev and Yablonskaya, 

1994). Berg (1948-1949) contends that it entered the 

Caspian from the Black Sea in post-glacial times 

while most other Caspian fishes are relicts of earlier 

transgressions or migrants from northern waters.  

Habitat: The Caspian silverside is a schooling fish 
found at depths exceeding 100 m but is concentrated 

at 10-20 m. Salinity tolerance is high, up to 77‰ 

(Miller in Miller, 2003), up to 60‰ in the Atrak 

River (Savenkova and Asanov, 1991). Reproduction 

can occur up to 42‰ while preferred levels are 3-

12‰. A wide temperature range is tolerated, 0-31ºC 

(Miller in Miller, 2003). It is also found in lagoons 

and river mouths, and enters rivers to spawn, against 

currents up to 1.2 m/sec. It is the dominant species in 

the Gomishan Wetland in spring, summer and 

autumn (Patimar et al., 2009). Holčík and Oláh 

(1992) report its apparent recent occurrence in the 

Anzali Lagoon in response to increased salinity 

there. It is also known from fresh water in Lenkoran. 

It can rapidly adjust its life history to a range of 

environments, from fresh water to coastal water.  

Age and growth: Maturity is attained in the first year 
and life span varies from 1 to 5 years, 4-5 years 

usually in the Caspian Sea basin (Henderson and 

Bamber, 1987). Ghoorbanalidoost et al. (2003) 

found populations in the south Caspian Sea to be 

73.82 mm long on average and 3.15 g in weight, with 

age  groups 1-3 years, average 1.7 years, total length 

and length-weight relationship W=0.00000615L3.02 

and a sex ratio of male:female=0.47:0.53. 

Heydarnejad (2009) gave the length-weight 

relationship for an Iranian sample as 

W=0.0326TL3.033. Patimar (1995) and Patimar et al. 

(2009) found 2256 fish from the Gomishan Wetland 

had a 4-year life cycle (to age 4+ years). Length-

weight relationships were W=0.0053TL3.0181 for 

males and W=0.0050TL3.063 for females, both 

allometrically positive. The von Bertalanffy 

equation was Lt=155.17[1-exp-0.28(t+0.738)] for 
males and Lt=162.77[1-exp-0.27(t+0.727)] for 
females. The sex ratio was male:female 1:1.3 and 

females dominated in the older age classes. Amri 

Sahebi et al. (2015) examined 191 fish from the 

southeast coast of the Caspian Sea and found an 

average fork length of 7.7 cm, weight 3.64 g and age 

2 years. 



286 
 

Int. J. Aquat. Biol. (2015) 3(5): 282-289 

Food: Savenkova and Asanov (1991) report 
plankton, eggs and juvenile fishes to be food items 

in the Atrak River of Turkmenistan. Some 

populations also eat benthic organisms such as 

amphipods, worms and molluscs. Some Iranian 

specimens contained encysted cladocerans and 

beetles in their guts. It has a trophic plasticity, 

adapting to whatever conditions obtain (Miller in 

Miller, 2003). Amri Sahebi et al. (2015) examined 

this fish in the southeast coastal waters of the 

Caspian Sea, finding it to be an opportunistic and 

carnivorous fish and a relatively voracious feeder. 

Benthic Gammarus and the zooplankton Daphnia 
were favoured foods and various other cladocerans 

along with copepods, ostracods, nematodes and 

dipterans were taken. 

Reproduction: Spawning in this species is 
intermittent and occurs along the coast from May to 

July, peaking in mid-May to mid-June (Savenkova 

and Asanov, 1991) or from April to August 

(Henderson and Bamber, 1987). Preserved Iranian 

fish samples have relatively large eggs from April to 

September, e.g., 1.4 mm on 27 April, 1.6 mm on 14 

May. Savenkova and Asanov (1991) also studied the 

annual spawning migration into the Atrak River 

(lower reaches in Turkmenistan, upper reaches 

shared with Iran). Fish are caught in a fish ladder 18-

19 km from the sea and in the river. The first schools 

appear in the Atrek mouth as early as mid-February 

at water temperatures of 8-10°C but the mass 

migration takes place in mid to late March and the 

first half of April at 14-22°C. Spawning occurs in 

March, April and May but most intensively in April 

at flood water temperatures of 13.7-23.0°C. There is 

a larger migration in high-water years. Sex ratio is 

about 1:1. A female may be able to spawn 5-6 times 

in one season so that egg numbers and diameters 

vary within each individual for different generations 

of eggs. Egg deposition in the Caspian Sea is 

associated with the alga Cladophora to which the 
eggs are attached or entangled by long filaments (up 

to 15) and this plant is present in the Atrak. Egg 

diameters may reach up to 2.0 mm and the light 

yellow eggs number up to 5500 (Caspian Sea 

Biodiversity Database, www.caspianenvironment.o- 

rg) presumably total seasonal fecundity. Only one 

gonad develops. Larvae are pelagic but may school 

close to shore. Patimar et al. (2009) for their 

Gomishan study found the reproductive season was 

March-July, peaking in March. Average absolute 

and relative fecundities were 2976 eggs and 784 eggs 

g-1 of body weight respectively (874 in the abstract). 

Maximum fecundity was 10,188 eggs for a 4+ fish. 

Mean oocyte diameter was 0.68 mm. 

Parasites and predators: The Caspian seal, Pusa 
caspica, is a predator on this species (Krylov, 1984) 
as are the larger fishes such as Stenodus leucichthys 
and Alosa saposchnikowii (Lönnberg, 1900) and the 
sturgeons Acipenser persicus and A. stellatus 
(Haddadi Moghadam et al., 2009). 

Economic importance: This species is food for a 
number of other fishes including such economic 

species as sturgeons, Sander and the predacious 

shads. It has been caught as a by-catch in kilka seine 

nets and used in fishmeal production. In Europe, the 

related A. boyeri has been sold fresh or canned, and 
in Turkey has been investigated as a food in the form 

of fish chips (Izci et al., 2011).  

Conservation: Kiabi et al. (1999) consider this 
species to be of least concern in the south Caspian 

Sea basin according to IUCN criteria. Criteria 

include abundance in numbers, widespread range 

(75% of water bodies), absent in other water bodies 

in Iran, and present outside the Caspian Sea basin. 

The IUCN (2014) has not assessed this species. 

Sources: Further details on collections examined can 
be found in the museum catalogues. 

Iranian material: CMNFI 1970-0507, 11, 22.2-56.3 
mm standard length, Gilan, Caspian Sea at Hasan 

Kiadeh (37º24'N, 49º58'E); CMNFI 1970-0509, 5, 

49.5-101.7 mm standard length, Gilan, pond at 

Hasan Kiadeh (37º24'N, 49º58'E); CMNFI 1970-

0543A, 7, 52.9-83.1 mm standard length, Gilan, 

Caspian Sea at Hasan Kiadeh (37º24'N, 49º58'E); 

CMNFI 1970-0563, 18, 39.8-112.5 mm standard 

length, Gilan, Kazian Beach (ca. 37º29'N, ca. 

49º29'E); CMNFI 1970-0581, 5, 47.6-54.8 mm 

standard length, Caspian Sea near Hasan Kiadeh 



287 
 

Coad/Silversides of Iran 

(37º24'N, 49º58'E); CMNFI 1970-0586, 7, 33.4-84.9 

mm standard length, Mazandaran, Gorgan Mordab at 

Ashuradeh-ye Kuchak (36º50’N, 53º56’E); CMNFI 

1971-0343, 2, 65.9-72.5 mm standard length, Gilan, 

Langarud at Chamkhaleh (37º13'N, 50º16'E); 

CMNFI 1979-0081, 3, 74.1-77.3 mm standard 

length, Mazandaran, Caspian Sea, 3 km west of 

Chalus (36º41'N, 51º24'E); CMNFI 1980-0127, 6, 

39.7-44.4 mm standard length, Gilan, Caspian Sea 

near Hasan Kiadeh (37º24’N, 49º58’E); CMNFI 

1980-0146, 4, 92.1-103.6 mm standard length, 

Mazandaran, Gorgan Mordab at Ashuradeh-ye 

Kuchak (36º50'N, 53º56'E); and CMNFI 1980-0160, 

2, 49.2-73.8 mm standard length, Iran, Caspian Sea 

basin (no other locality data); CMNFI 1993-0144, 1, 

75.3 mm standard length, Mazandaran, Neka Power 

Plant (36º51’48”N, 53º23’24”E); CMNFI 2008-

0105, 1, 87.6 mm standard length, Gilan, Bandar 

Anzali breakwater (37º26’N, 49º29’E). 
 

Acknowledgements 

I am indebted to the Department of Biology, Shiraz 

University and the Canadian Museum of Nature, 

Ottawa for funding of research. Numerous 

colleagues and co-authors assisted in developing the 

website on Iranian fishes, providing specimens, data 

and photographs and are listed at 

www.briancoad.com. 

 

References 
Abbasi K., Valipour A., Talebi Haghighi D., Sarpanah A., 

Nezami S. (1999). Atlas of Iranian Fishes. Gilan 

Inland Waters. Gilan Fisheries Research Centre, 

Rasht. 113 p. (In Farsi).  

Abdoli A., Naderi M. (2009). Biodiversity of fishes of the 

southern basin of the Caspian Sea. Abzian Scientific 

Publications, Tehran. 243 p. (In Farsi).  

Afraei M., Lalooie F. (2000). Fishes distribution assay in 

Tonekabon River. Iranian Journal of Fisheries 

Sciences, 9(1): 1-14. (In Farsi).  

Amri Sahebi A., Taghavi H., Fazli H. (2015). The diet of 

big-scale sand smelt Atherina boyeri  caspia (Risso, 
1810) in the southeastern coast of the Caspian Sea. 

Iranian Scientific Fisheries Journal, 24(1): 121-133. 

(In Farsi). 

Bamber R.N., Henderson P.A. (1985). Morphological 

variation in British atherinids, and the status of 

Atherina presbyter Cuvier (Pisces: Atherinidae). 
Biological Journal of the Linnaean Society, 25: 61-76.  

Berg L.S. (1948-1949). Freshwater fishes of the USSR 

and adjacent countries. Israel Program for Scientific 

Translations, Jerusalem (1962-1965). 3 volumes.  

Coad B.W. (1987). Zoogeography of the Freshwater 

Fishes of Iran. In: F. Krupp, W. Schneider, R. 

Kinzelbach (Eds.). Proceedings of the Symposium on 

the Fauna and Zoogeography of the Middle East, 

Mainz, 1985. Beihefte zum Tübinger Atlas des 

Vorderen Orients, Reihe A (Naturwissenschaften), 28, 

Dr. Ludwig Reichert Verlag,  Wiesbaden. Pp: 213-

228. 

Coad B.W. (1998). Systematic biodiversity in the 

freshwater fishes of Iran. Italian Journal of Zoology, 

65 (Supplement): 101-108. (Proceedings of the Ninth 

Congress of European Ichthyologists (CEI-9) "Fish 

Biodiversity" organised in Naples at the University 

Federico II and held in Trieste - Italy, 24-30 August 

1997).  

Coad B.W., Abdoli A. (1996). Biodiversity of Iranian 

freshwater fishes. Abzeeyan, 7(1): 4-10. (In Farsi).  

Dobrovolov I.S., Ivanaova P.P. (1999). Biochemical 

comparison of the Atherina boyeri and Atherina 
mochon pontica (Pisces, Atherinidae). Folia 
Zoologica, 48(1): 55-60.  

Eschmeyer W.N., Fong J.D. (2011). Pisces. In: Z-Q. 

Zhang (Ed.). Animal biodiversity: An outline of 

higher level classification and survey of taxonomic 

richness. Zootaxa, 3148: 26-38.  

Esmaeili H.R., Coad B.W., Mehraban H.R., Masoudi M., 

Khaefi R., Abbasi K., Mostafavi H., Vatandsoust S. 

(2014). An updated checklist of fishes of the Caspian 

Sea basin of  Iran with a note on their zoogeography. 

Iranian Journal of Ichthyology, 1(3): 152-184.  

Ghoorbanalidoost G., Kayvan A., Ramin M. (2003). 

Morphology and population structure of Atherina 
boyeri in the southern Caspian Sea. Iranian Journal of 
Fisheries Sciences, 12(2): 63-78. (In Farsi).  

Haddadi Moghadam K., Tavakoli M., Pazhand Z.A., 

Roufchahi R., Choubian F., Parand Avar H. (2009). 

Summer and winter feeding behaviour in Acipenser 
persicus and  Acipenser stellatus in the south Caspian 
Sea. Iranian Scientific Fisheries Journal, 18(2): 13-26. 

(In Farsi).  

Henderson P.A., Bamber R.N. (1987). On the 



288 
 

Int. J. Aquat. Biol. (2015) 3(5): 282-289 

reproductive biology of the sand smelt Atherina boyeri 
Risso (Pisces: Atherinidae) and its evolutionary 

potential. Biological  Journal of the Linnaean Society, 

32: 395-415.  

Heydarnejad M.S. (2009). Length-weight relationships 

for six freshwater fish species in Iran. Chinese Journal 

of Oceanology and Limnology, 27(1): 61-62.  

Holčík J. Oláh J. (1992). Fish, fisheries and water quality 

in Anzali Lagoon and its watershed. Report prepared 

for the project-Anzali Lagoon productivity and fish 

stock investigations. Food and Agriculture 

Organization, Rome, FI:UNDP/IRA/88/001 Field 

 Document 2:  109 p.  

IUCN. (2014). The IUCN red list of threatened species. 

International Union for the Conservation of Nature, 

Gland, Switzerland (http://www.iucnredlist.org/).  

Izci L., Günlü A., Bilgin Ş. (2011). Production of fish 

chips from sand smelt (Atherina boyeri, Risso 1810) 
and determination of some quality changes. Iranian 

Journal of Fisheries Sciences, 10(2): 230-241. 

Karimpour M. (1998). The ichthyofauna of Anzali 

Lagoon. Iranian Journal of Fisheries Sciences, 7(2): 

83-94 (In Farsi).  

Kiabi B.H., Abdoli A., Naderi M. (1999). Status of the 

fish fauna in the South Caspian Basin of Iran. Zoology 

in the Middle East, 18: 57-65.  

Kiener A., Spillmann C.J. (1972). Note complémentaire 

à l'étude systématique et écologique d'Atherina boyeri 
Risso (Poissons, Cyprinidae) dans sa zone de 

dispersion actuelle.  Bulletin du Muséum national 

d'Histoire naturelle, Zoologie, Paris, 3(5541): 563-

580.  

Kosarev A.N., Yablonskaya E.A. (1994). The Caspian 

Sea. SPB Academic Publishing, The  Hague. 259 p.  

Krylov V.I. (1984). An estimate of the effect of the 

Caspian seal (Pusa caspica) on fish populations. 
Canadian Translation of Fisheries and Aquatic 

Sciences, 5066: 15 p.  

Lönnberg E. (1900). Contributions to the ichthyology of 

the Caspian Sea. Kunglica Svenska 

Vetenskapsakademiens Handlingar, 26(IV)(8): 3-38. 

Vestnik Rybopromyshlennosti, St. Petersburg 16: 30-

39.  

Meshkov M.M. (1941). On the systematics of the fish of 

the family Atherinidae from the Black and Caspian 

seas. Izvestiya Akademii Nauk SSSR, Otdel 

Biologicheskikh Nauk, 3: 400-406.  

Miller P.J. (2003). The Freshwater fishes of Europe. 

Volume 8/I. Mugilidae, Atherinidae,  Atherinopsidae, 

Blenniidae, Odontobutidae, Gobiidae 1. AULA-

Verlag, Wiebelsheim. 404 p.  

Naseka A.M., Bogutskaya N.G. (2009). Fishes of the 

Caspian Sea: zoogeography and updated check-list. 

Zoosystematica Rossica, 18(2): 295-317. 

Nelson J.S. (2006). Fishes of the world. Fourth Edition. 

John Wiley and Sons, New York. 601 p.  

Patimar R. (1995). The biology of Boyer's sand smelt 

population Atherina boyeri Risso 1810, in Gomishan 
Lagoon. M. Sc. Thesis, Tarbiat Moddaress University, 

Tehran. (In Farsi).  

Patimar R., Yousefi M., Hosieni S.M. (2009). Age, 

growth and reproduction of the sand smelt Atherina 
boyeri Risso, 1810 in the Gomishan wetland-southeast 
Caspian Sea. Estuarine, Coastal and Shelf Science, 

81(4): 457-462  

Reshetnikov Yu.S., Bogutskaya N.G., Vasil'eva E.D., 

Dorofeeva E.A., Naseka A.M., Popova O.A., 

Savvaitova K.A., Sideleva V.G., Sokolov L I. (1997). 

An annotated check-list of the freshwater fishes of 

Russia. Journal of Ichthyology, 37(9): 687-736.  

Roshan Tabari M. (1997). Hydrological and 

hydrobiological study in the Syiah-rud River. Iranian 

Fisheries Scientific Journal, 6(2): 27-42 (In Farsi).  

Savenkova T.P., Asanov A.Yu. (1991). The Caspian 

silverside, Atherina boyeri caspia, in the lower reaches 
of the Atrek River. Journal of Ichthyology, 31(6): 134-

138.  

Vasil'eva E.D. (1994). Skull morphology of atherine 

fishes of the Black Sea, the Sea of Azov, and the 

Caspian Sea, and certain problems of the systematics 

of the genus Atherina (Atherinidae). Journal of 
Ichthyology, 34(9): 125-140.  

Vasil'eva E.D. (1996). Cranial data and some problems in 

the systematics of the genus Atherina (Atherinidae). 
Publicaciones Especiales Instituto Español de 

Oceanografía, 21: 199-204.  

Whitehead P.J.P., Bauchot M.-L., Hureau J.-C., Nielsen 

J., Tortonese E. (1984-1986). Fishes of the North-

eastern Atlantic and the Mediterranean. UNESCO, 

Paris. Volume I: 1-510; Volume II: 511-1007; Volume 

III: 1008-1473. 



  

Int. J. Aquat. Biol. (2015) 3(5): 282-289 

E-ISSN: 2322-5270; P-ISSN: 2383-0956

Journal homepage: www.ij-aquaticbiology.com 

© 2015 Iranian Society of Ichthyology 

 چکیده فارسی

 

 (Atherinidae)خانواده  ایران گل آذین ماهیانمروری بر 
 

 

  برایان کد

 نادا.، کاK1P 6P4انتاریو، ، موزه تاریخ طبیعی کانادا، اتاوا

  

 چکیده:

گونه در این خانواده  86جنس و  41شوند. حدود معتدله تا گرمسیری و آبهای شیرین یافت میدر نواحی ساحلی دریاهای ماهیان آذین گل

شناسی، یستماتیک، ریختشود. در این مقاله مروری، سدر دریای خزر یافت می Atherina caspiaوجود دارد که تنها یک گونه بومی بنام 

 هرستفشود. همچنین یک شده و به تصویر کشیده میایران توصیف گونه گل آذین خزری شناسی، اهمیت اقتصادی و حفاظت پراکنش، زیست

 گردد.در مورد این ماهی در ایران ارائه میمنابع 

 .دریای خزرشناسی، شناسی، ریختزیست ،Atherina :کلمات کلیدی