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Habitat use and population dynamics of the Azure-Winged Magpie ...

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eeding species have high survival rates, <strong>and</strong> longevity seems to be a contributing factor to<br />

cooperative breeding in <strong>the</strong> Splendid fairy-wrens (Rowley & Russell, 1990).<br />

The Khonin Nuga C. cyanus colony is small –an average <strong>of</strong> 37 individuals present per year<br />

(starting <strong>population</strong> in May) [cf. 40-60 breeding birds in Spain (de la Cruz, pers. comm.) <strong>and</strong> up<br />

to 287 individuals in Japan (Imanishi, 2002)]. Perhaps with recent colonisation, small numbers<br />

are normal (although <strong>the</strong>re was no increase or decrease in colony size over <strong>the</strong> four years), <strong>and</strong><br />

data from this study has shown that this is most likely an open <strong>population</strong>. It would be interesting<br />

to see in <strong>the</strong> near future if numbers <strong>and</strong> geographic range do increase in <strong>the</strong> Nor<strong>the</strong>rn Mongolian<br />

C. cyanus <strong>population</strong>s.<br />

4.5 The Fire Situation in Mongolia <strong>and</strong> <strong>the</strong> West Khentii Region<br />

As in o<strong>the</strong>r developing countries, Mongolia’s management <strong>of</strong> natural resources suffers from<br />

unregulated <strong>use</strong>, over<strong>use</strong>, <strong>and</strong> inadequate protection. There was a revolution in <strong>the</strong> political,<br />

social <strong>and</strong> economic situation in <strong>the</strong> 1990s. The cessation <strong>of</strong> <strong>the</strong> Soviet era <strong>and</strong> state-subsidised<br />

social services in Mongolia, combined with access to formerly restricted markets, has exposed<br />

forests <strong>and</strong> steppes to threats such as fire, overgrazing, mining activities, improper commercial<br />

logging, illegal collection <strong>of</strong> wood for construction <strong>and</strong> fuel, hay making in forest steppes,<br />

complacency in enforcement <strong>of</strong> forest rules <strong>and</strong> regulations, <strong>and</strong> damage by pests <strong>and</strong> diseases.<br />

Fires, by far, have had <strong>the</strong> most serious impact on <strong>the</strong> forests <strong>of</strong> Mongolia (Bayartaa et al., 2007).<br />

Fires generally occur in spring (March to mid June) <strong>and</strong> in autumn (September to October)<br />

(Bayartaa et al., 2007). The spring fires account for 80 percent <strong>of</strong> all fires, while <strong>the</strong> fires in<br />

autumn account for five to eight percent. Fires occur during <strong>the</strong>se periods beca<strong>use</strong> dry fuel loads<br />

are at <strong>the</strong>ir highest. In summer, fires are uncommon beca<strong>use</strong> this is <strong>the</strong> time <strong>of</strong> highest<br />

precipitation.<br />

Between 1981 <strong>and</strong> 1999 <strong>the</strong>re were on average 160 wildfires per year in Mongolia. However <strong>the</strong><br />

average area burnt in <strong>the</strong> 1990s was around 4,771,297 hectares per year, compared to one-fifth <strong>of</strong><br />

that in <strong>the</strong> 1980s (Goldammer, 2002). From <strong>the</strong> years 2000 to 2008 <strong>the</strong> average number <strong>of</strong> fires<br />

per year was 188, <strong>and</strong> <strong>the</strong> area burnt was an average <strong>of</strong> 3,253,000 ha/ year (Johnson et al., 2009).<br />

The increase in <strong>the</strong> number <strong>of</strong> fires in <strong>the</strong> last two decades is related to anthropogenic ca<strong>use</strong>s.<br />

They are mostly accidents, ca<strong>use</strong>d by herders, loggers <strong>and</strong> hunters. Fires can start by carelessness<br />

from a campfire, tracer bullets <strong>use</strong>d by hunters to hunt deer, or sparks from vehicle exhaust pipes<br />

72

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