Dealing with salinity in Wheatbelt Valleys - Department of Water
Dealing with salinity in Wheatbelt Valleys - Department of Water
Dealing with salinity in Wheatbelt Valleys - Department of Water
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George and Coleman<br />
SPECIES<br />
Table 5: Temperature and <strong>sal<strong>in</strong>ity</strong> parameters for a number <strong>of</strong> species <strong>of</strong><br />
fish crustaceans and molluscs (modified from Lawrence 1996).<br />
SALINITY<br />
(mg/L x 1000)<br />
TEMPERATURE REFERENCE<br />
BRINE SHRIMP 31–340 6–35 Persoone et al. (1980)<br />
Artemia sal<strong>in</strong>a/Parartemia sp.<br />
BARRAMUNDI 0–70 16–35 Shelley (1993);.<br />
Lates calcarifer Coleman (pers.com)<br />
RED SNAPPER 16–60 13–28 Anon. (1995)<br />
Pagrus auratus<br />
BLACK BREAM 3–60 8–33 Lenanton (1976);<br />
Acanthopagrux butcheri Sudmeyer et al. (1999)<br />
GROUPER 23–45 18–31 Akatsu et al. (1983)<br />
Ep<strong>in</strong>ephelus tauv<strong>in</strong>a<br />
MARRON 0–6 0–30 Morrissy et al. (1990);<br />
Cherax tenuimanus Morrissy (1992)<br />
MILK FISH 0.5–158 25–36 Schuster (1960)<br />
Chanos chanos<br />
MULLET 0–75 3–35 Murashige et al. (1991);<br />
Mugil cephalux Walsh et al. (1991)<br />
GIANT TIGER PRAWN 13–33 10–25 Tseng (1987)<br />
Penaeux monodon<br />
RAINBOW TROUT 0–35 10–22 Sedgwick (1985);<br />
Oncorhynchus mykiss Bromage & Shepherd (1990)<br />
TILAPIA 0–60 8–42 Kueltz & Onke (1993)<br />
Oreochromis mossambicus<br />
YABBIES 0–8 0–36 Morrissy & Cassells (1992);<br />
Cherax albidus Mills & Geddes (1980)<br />
specialised and experienced people. As for most<br />
micro algae ventures the difficulty is not grow<strong>in</strong>g the<br />
small plant but harvest<strong>in</strong>g it and process<strong>in</strong>g the f<strong>in</strong>e<br />
chemicals that make them so valuable. The follow<strong>in</strong>g<br />
(Table 6) is a list <strong>of</strong> potential algae species that could<br />
be cultured <strong>in</strong> sal<strong>in</strong>e water.<br />
Most algae species require an extensive area for<br />
cultur<strong>in</strong>g <strong>with</strong> a high level <strong>of</strong> solar radiation. An<br />
extensive area also means that evaporation is high, so<br />
a large supply <strong>of</strong> relatively low <strong>sal<strong>in</strong>ity</strong> 'make up'<br />
water is needed to ma<strong>in</strong>ta<strong>in</strong> the <strong>sal<strong>in</strong>ity</strong> <strong>of</strong> grow out<br />
ponds dur<strong>in</strong>g high evaporation. This is not normally a<br />
problem for Dunaliella sal<strong>in</strong>a that is cultured <strong>in</strong> water<br />
up to 300,000 mg/L and where seawater<br />
concentration makeup water is <strong>of</strong>ten effective <strong>in</strong><br />
– 12 –<br />
ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g a constant <strong>sal<strong>in</strong>ity</strong> <strong>in</strong> the grow out ponds.<br />
It is more <strong>of</strong> an issue <strong>with</strong> species cultured at lower<br />
sal<strong>in</strong>ities where an effective make up water needs to<br />
be approach<strong>in</strong>g potable water standards to be useful.<br />
It is not practical to grow a species that can only<br />
tolerate a <strong>sal<strong>in</strong>ity</strong> <strong>of</strong> 50,000 mg/L when the only<br />
water available <strong>in</strong> large quantities is at 35,000 mg/L.<br />
Algae culture uses a large amount <strong>of</strong> water as the<br />
culture areas need to be <strong>in</strong> the hectare range or<br />
greater to be commercial. The commercial<br />
Dunaliella sal<strong>in</strong>a farms are several hundred hectares<br />
<strong>in</strong> size. The water used for algae culture needs a<br />
high concentration <strong>of</strong> nutrients and can tolerate a<br />
high concentration <strong>of</strong> metals, although some metals<br />
will tie up valuable nutrients.