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Pseudorasbora parva (Temminck & Schlegel, 1846)

Stone moroko
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Pseudorasbora parva
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Italy country information

Common names: Pseudorasbora
Occurrence: introduced
Salinity: freshwater
Abundance: | Ref:
Importance: | Ref:
Aquaculture: | Ref:
Regulations: | Ref:
Uses: no uses
Comments: Naturalized in 1988. Established in Northern Italy, expanding in central Italy (Ref. 45688). Found in the River Po in 1990 as reported from FISH Magazine of the Institute of Fisheries Management, Nottingham UK. Introduced accidentally into the Po and Tevere basins (Ref. 27118), Tuscany (Ref. 97736). Recorded for the 1st time in the Grosseto Province, now established in the middle and lower courses of the Ombrone, Albegna and Fiora. Found at a wide size range. Is also locally abundant (Ref. 45688). Invasive in north, central, and southern Italy (Ref. 119201). Interferes with native cyprinids (Ref. 94493). Has been reported in the shallow marine waters of the Tyrrhenian Sea (Ref. 97736).
National Checklist:
Country Information: https://www.cia.gov/library/publications/resources/the-world-factbook/geos/it.html
National Fisheries Authority:
Occurrences: Occurrences Point map
Main Ref: Bianco, P.G. and V. Ketmaier, 2001
National Database: ICTIMED

Common names from other countries

分類 / Names 俗名 | 同種異名 | Catalog of Fishes(, ) | ITIS | CoL | WoRMS | Cloffa

Teleostei > Cypriniformes (Carps) > Gobionidae (Gudgeons)
Etymology: Pseudorasbora: Greek, pseudes = false + Rasbora, an Indian word for a fish, also used in Malay peninsula.
  More on authors: Temminck & Schlegel.

Environment: milieu / climate zone / depth range / distribution range 生態學

; 淡水; 半鹹淡水 底中水層性; pH range: ? - 7.0; dH range: ? - 15.   溫帶; 5°C - 22°C (Ref. 2060); 54°N - 22°N, 110°E - 141°E

分布 國家 | FAO區域 | 生態系 | 發現紀錄 | Point map | 簡介 | Faunafri

Asia: Amur to Zhujiang [Pearl River] drainages in Siberia, Korea and China (Ref. 59043). Introduced to various areas in Europe and Asia. Several countries report adverse ecological impact after introduction (Ref. 1739).
亞洲: 日本南部與中部,台灣,韓國,中國,阿穆爾河流域。 引進了歐洲各地與亞洲 (參考文獻 1739) 而且現在出現於聶伯河,第聶伯河,多瑙河流域,斯庫台利湖與普雷帕斯湖與希臘的 Aliakmon 河中。 (參考文獻 26334) 引入後的一些國家報告不利的生態衝擊。 也在伊朗與土庫曼引入。 (參考文獻 39702)

Length at first maturity / 大小 / 重量 / 年齡

Maturity: Lm 3.0  range ? - ? cm
Max length : 12.5 cm TL 雄魚/尚未辨別雌雄; (Ref. 88166); common length : 8.0 cm TL 雄魚/尚未辨別雌雄; (Ref. 1441); 最大年齡: 5 年 (Ref. 56557)

簡短描述 檢索表 | 型態特徵 | 形態測量圖

背棘 (總數) : 3; 背的軟條 (總數) : 7; 臀棘: 3; 臀鰭軟條: 6. Mouth superior and transverse; 6 branched anal rays; barbels absent; distal margin of dorsal convex; large adults with sexually dimorphic coloration (Ref. 43281).
嘴上位且橫向; 6個分枝的臀鰭鰭條; 觸鬚不存在; 背部凸狀的末梢部邊緣; 大的成魚有性別雙型性顏色。 (參考文獻 43281)

生物學特性     字彙 (例如 epibenthic)

Found in a wide variety of habitats, most abundantly in well vegetated small channels, ponds and small lakes (Ref. 59043). Adults occur in cool running water. Feed on small insects, fish and fish eggs (Ref. 30578), and plant material (Ref. 59043). Usually breed in habitats with still or very slow-flowing water (Ref. 59043). Females spawn 3-4 times in a season (Ref. 59043). Males clear the surface of the spawning site and guard the eggs until they hatch (Ref. 59043). Regarded as pest which competes with the fry of other species due to its high reproductive rate (Ref. 1739).

成魚出現在冷的流動水。 捕食小的昆蟲,魚與魚卵。 (參考文獻 30578) 被認為與其他種的魚苗競爭的有害之物.由於它的生殖率高.(參考文獻 1739)

Life cycle and mating behavior Maturities | 繁殖 | Spawnings | Egg(s) | Fecundities | 仔魚

Nests under stones and the male cleans the cavity with its pearl organs. Eggs adhere to the ceiling of the cavity. The male leaves the nest before the eggs hatch. Females spawn 3-4 times during a season (Ref. 59043).亞洲: 日本南部與中部,台灣,韓國,中國,阿穆爾河流域。 引進了歐洲各地與亞洲 (參考文獻 1739) 而且現在出現於聶伯河,第聶伯河,多瑙河流域,斯庫台利湖與普雷帕斯湖與希臘的 Aliakmon 河中。 (參考文獻 26334) 引入後的一些國家報告不利的生態衝擊。 也在伊朗與土庫曼引入。 (參考文獻 39702)

主要參考資料 Upload your references | 參考文獻 | 合作者 | 合作者

Kottelat, M. and J. Freyhof, 2007. Handbook of European freshwater fishes. Publications Kottelat, Cornol and Freyhof, Berlin. 646 pp. (Ref. 59043)

IUCN 瀕危狀態 (Ref. 130435)

  無危 (LC) ; Date assessed: 14 April 2020

CITES (Ref. 128078)

Not Evaluated

CMS (Ref. 116361)

Not Evaluated

對人類具威脅

  潛能有害之物




人類使用

漁業: 沒有興趣; 水族館: 商業性
FAO(Publication : search) | FishSource |

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Estimates based on models

Phylogenetic diversity index (Ref. 82804):  PD50 = 0.5312   [Uniqueness, from 0.5 = low to 2.0 = high].
Bayesian length-weight: a=0.00776 (0.00665 - 0.00906), b=3.13 (3.09 - 3.17), in cm Total Length, based on LWR estimates for this species (Ref. 93245).
營養階層 (Ref. 69278):  3.1   ±0.1 se; based on diet studies.
回復力 (Ref. 120179):  中等的, 族群倍增時間最少 1.4 - 4.4年 (tm=1; tmax=5; K=0.24; Fec=1,000).
Fishing Vulnerability (Ref. 59153):  Low to moderate vulnerability (29 of 100).