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20

DECEMBER 2014

WORLD AQUACULTURE

WWW.WA S.ORG

We believe that rainbow trout aquaculture in earthen raceways

along the Assi River is not sustainable. Earthen raceways are

more difficult to clean and sediments accumulate, leading to

anaerobic conditions. Earthen raceways are subject to resuspension

and accumulation of solids, which could harbor pathogens.

Furthermore, earthen raceways are prone to erosion and caving in of

embankments, resulting in irregular widths and depths that disrupt

water flow patterns (Piper

et al

. 1982). Finally, earthen ponds are

difficult to sterilize between harvests.

Feeds and Feeding

All rainbow trout farmers along the Assi River use

manufactured fish feed, purchasing any brand available. Most

farmers knew some of the major ingredients in the pelleted feed but

do not know their proportions. Only 11 percent were willing to state

the composition of the feed used.

Nearly all farmers (96 percent) offer fish only aquafeeds. The

price of aquafeed and fishmeal is a very important factor in deciding

whether to feed fish a manufactured diet or chicken processing

wastes. Trout farmers occasionally replace fish feed with poultry

byproducts because they cannot always afford to purchase fish

feed and because they do not fear legal penalties, inasmuch as the

government does not control their practices.

If chicken processing wastes are used as substitutes for

aquafeed, the water quality of the Assi River may be at risk. Even if

poultry byproduct is added to aquafeeds as a substitute for fishmeal,

it performs worse in terms of pollution loadings (Wu 1995). Also,

poultry byproducts do not always contain the necessary nutrients

required for healthy growth (Riche and Brown 1996).

Very few farmers are aware that fingerlings need feed with a

greater protein level than larger rainbow trout. However, because

the majority of farmers purchase their feed at the correct pellet

size for their fish and the feed manufacturers know the required

feed composition at various sizes, the fish receive the correct feed

composition and size for each development stage. This is not a

problem because most farms along the Assi River stock fish at the

same time and have similar-size animals.

Healthy fish growth depends on appropriate feeding rates.

When asked stocking densities, farmers gave such different answers

that it almost was impossible to sort responses into categories. For

most trout farms along the Assi River, the biomass of fish per tank

is not known with certainty and, without this estimate, the proper

quantity of feed as a function of body weight cannot be determined.

Most farmers offer feed to apparent satiation as instructed by feed

salesmen but do not weigh the feed given. Some farmers do not feed

fish for days if they do not have the money to purchase feed.

We are uncertain that actual feeding practices match responses

to the survey. Trout farmers do not keep records of water quality,

mortalities and fish growth, despite this information being essential

to determining feeding quantities. Repercussions of feeding in

excess of what fish are able to metabolize include increases in

production costs, deterioration of water quality and outbreaks of

diseases (Cain and Garling 1993, Dunning and Sloan 2001). Very

few farmers realize uneaten food is a pollutant.

TABLE 1. Water quality requirements for rainbow trout culture.

PAR AME TER

R ANGE

REFERENCE

Optimal temperature

13 – 18

Dunning and Sloan 2001

7 – 18

Cain and Garling 1993

12 – 21

FAO 2011c

10 – 15

IDEQ 1998

Optimal pH range

6.5 – 7

Hinshaw 2000

6.5 – 8

Cain and Garling 1993

6.7 – 8.5

Klontz 1991

6.5 – 8.5

FAO 2011b

Alkalinity (mg/L as CaCO3)

10 – 400

Cain and Garlin 1993; IDEQ 1998, FAO 2011b

30 – 200

Klontz 1991

Hardness (mg/L as CaCO3)

10 – 400

IDEQ 1998

Minimum dissolved oxygen (mg/L)

6

Hinshaw 2000

5

Piper

et al

. 1982;

7

IDEQ 1998

Phosphorus (mg/L)

0.01 – 3

IDEQ 1998

Ammonia-N (mg/L)

< 0.03

Klontz 1991

0.0125 – 0.025

IDEQ 1998

Nitrate (mg/L)

< 0.55

Klontz 1991

< 0.1 in soft water

< 0.2 in hard water

IDEQ 1998