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soil-conservation-people-religion-and-land.pdf - South West NRM

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If so, in what ways has it changed?<br />

Can the reasons for these changes be clearly<br />

identified?<br />

To what degree are the various species of plants<br />

utilized by animals?<br />

What is the relative productivity of the species<br />

present in terms of dry matter yield?<br />

What is the nutritive value of the species concerned?<br />

Are any species toxic or otherwise harmful to grazing<br />

animals?<br />

Which species are perennial <strong>and</strong> relatively stable in<br />

their annual production?<br />

Which combination of species is likely to give highest<br />

sustained animal production?<br />

Does this combination coincide with the ltclimaxflt<br />

vegetation of the area?<br />

It is useful to consider Hacker's contention that the WARMS<br />

philosophy (see this workshop) is a substantial departure from<br />

the traditional approach. The WARMS objectives to measure<br />

plant <strong>and</strong> <strong>soil</strong> changes, to underst<strong>and</strong> their causes <strong>and</strong> to<br />

convert these into management recommendations, appear similar<br />

to the original objectives. The WARMS philosophy of being<br />

strictly utilitarian <strong>and</strong> production-oriented, can be met by<br />

the practical interpretation of the above questions. The same<br />

management recommendations from both short <strong>and</strong> long tern<br />

monitoring can be obtained whether the terminology of<br />

condition or monitoring is used. In all cases we:want to know<br />

what has changed, how does that change affect grazing animals,<br />

what caused the change <strong>and</strong> what should we do about it. The<br />

WARMS technique of comparing fenced sites with adjacent grazed<br />

sites has much to recommend it in isolating the effects of<br />

stock from the effects of climate.<br />

What is required to initiate the application of the concepts<br />

of condition <strong>and</strong> trend is, firstly, the deternination of which<br />

species may be regarded as lldesirabletg in any area, <strong>and</strong><br />

secondly, the assessment of how far removed the present<br />

vegetation is from the potentially llbestw vegetation, as<br />

measured by its capabilities of sustained high animal<br />

production <strong>and</strong> maintenance of <strong>soil</strong> stability.<br />

MONITORING RESEARCH AND DROUGHT<br />

Taylor aid Whalley (1976) suggested that ~ustralian range<br />

research has been suppressed by "the seemingly unresponsive<br />

nature of native pastures to manipulation <strong>and</strong> the acceptance<br />

of the 'replacement philo~ophy~~~. The past decade has seen an<br />

improvement in this situation <strong>and</strong>, especially in the past few<br />

years, the formation of l<strong>and</strong>holder committees to tackle<br />

property planning <strong>and</strong> pasture management in the pastoral zone.<br />

Central to a sustainable pastoral production system is<br />

realistic estimation of carrying capacity. It is important to<br />

note that in the Carnarvon area-of western ~ustralia, Zahran<br />

et al. (1988) showed that at a stocking rate of 1 sheep to 2.5<br />

ha, sheep consumed 1/6 of feed available when feed was<br />

plentiful <strong>and</strong> 1/2 when in short supply. At a stocking rate of<br />

1:13 ha approximately 1/9 <strong>and</strong> 1/3 of available fodder was

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