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Sturgeon biodiversity and conservation

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212<br />

Figure 4. Estimated numbers of sturgeons in the Northern Caspian Sea from the Volga <strong>and</strong> Ural river populations.<br />

river than they do now. These changes resulted in<br />

decreases in natural reproduction in the Volga River<br />

<strong>and</strong> in changes in the population structure of this<br />

species.<br />

In response to this decline in natural reproduction,<br />

the Soviet government began a program in the<br />

early 1960s to enhance sturgeons through artificial<br />

propagation (Barannikova 1995). Throughout the<br />

1960s, more than 3.9 million beluga juveniles were<br />

released from hatcheries annually. In the 1970s, the<br />

annual release reached more than 12.9 million<br />

young, <strong>and</strong> by the early 1980s, the average number<br />

of the young belugas released into the Volga River<br />

was 19.4 million (Figure 3). At present, practically<br />

all beluga (96.3%) in the Volga River consist of<br />

hatchery propagated fish (Khodorevskaya 1986,<br />

1992). However, artificial propagation does not<br />

completely compensate for the loss of natural reproduction<br />

of beluga in the Volga River. The population<br />

of beluga continues to decline even though<br />

the number of beluga harvested does not exceed<br />

0.1% of the number of individuals released.<br />

Spawning sites for beluga in the Ural River remain<br />

intact <strong>and</strong> the Ural River stock of beluga is<br />

replenished by natural reproduction. Until the late<br />

1970s, the number <strong>and</strong> biomass of beluga migrating<br />

into the Ural River was considerably smaller than<br />

that migrating into the Volga River (Figure 4).

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