Chemicals used in fish farms
Chemicals used in marine fish farms can be broadly
divided into two categories:
- hygiene products for disinfection or for environmental
control, e.g. antifouling agents for fish cages,
and
- medicinal products, divided into chemotherapeutic
agents for therapy or prophylaxis of disease which
act on the invading organisms, and pharmacological
drugs which act on the target animal.
Inevitably when such therapeutants are applied
to farmed stocks, a significant proportion will
not reach the target species but will enter the
environment. Route of entry and potential concentrations
will depend on the volumes used and method of application.
For example chemicals could enter the marine environment
through faeces, uneaten food, or from bath treatments.
Greater volumes can be expected for chemicals used
in bath treatments, compared to chemicals applied
through food.
Sea lice treatments are necessarily toxic medicines
which are applied, either as bath treatments or
as in-feed treatments. The fate and effects of these
chemicals in the environment depend upon their physical
and chemicals properties. They may persist in the
water column and affect plankton and/or affect the
seabed and its benthic fauna.
A Nature Conservancy Council report in 1989 (NCC
1989) identified impacts in the environment from
mariculture. This included a consideration of chemical
pollution from aquaculture; feed additives, pharmaceuticals
and other treatments, e.g. antibiotics, immersion
and antifoulant treatments to equipment. The reader
is referred to this review for background information.
SEPA has recently published a document entitled
Regulation and monitoring of marine cage fish
farming in Scotland - A procedures manual (SEPA
Fish Farming Manual) which details the procedures
SEPA will follow in the control of fish farm chemicals
and includes EQSs in the water column and the sediments.
This document is freely available and should be
used as a companion to this manual when considering
the impact of fish farm chemicals on European marine
sites.
The table below lists the main chemicals used in
marine cage fish farming and indicates where standards
exist and where further information can be found.
Hydrogen peroxide is administered as a bath treatment
for the removal of sea lice by enclosing the cage
in a tarpaulin. It is the recommended treatment
for the removal of sea lice by SEPA. The Environment
Agency is investigating its effects on aquatic organisms.
Dichlorvos is also administered as a bath treatment
and EQSs have been proposed for the water column
in the form of annual averages and maximum allowable
concentrations.
Main chemicals used in cage fish farming
Use/chemical
|
Water quality standards
|
Sediment quality standards
|
Reference
|
Sea
lice treatment |
|
|
|
Hydrogen
peroxide |
No
|
No
|
Jones
and Stewart (1991) (see Section B28) |
Dichlorvos |
Yes
|
No
|
Lewis
et al (1998) |
Azamethiphos |
Yes
|
No
|
SEPA
Policy No. 17 |
Cypermethrin |
Yes
|
No
|
SEPA
Policy No. 30 |
Teflubenzuron |
Yes
|
Yes
|
SEPA
Policy No. 29 |
Ivermectin |
Yes
|
No
|
Codling
et al (1998)
SEPA Policy No. 2
|
Antimicrobials/
disinfectants |
|
|
|
Oxolinic
acid |
Yes
|
No
|
Murgatroyd
et al (1994) |
Oxytetracycline |
Yes
|
No
|
Gendebien
et al 1994 |
Malachite
green |
Yes
|
No
|
Burchmore
and Wilkinson (1993) |
Formaldehyde |
Yes
|
No
|
Jerman
and Wilkinson (1993) |
Azamethiphos is an organophosphate that has recently
been granted market authorisation by SEPA for use
as a bath treatment for the removal of sea lice.
EQSs have been proposed by Lewis et al (1998)
for the protection of saltwater life in the form
of annual averages and maximum allowable concentrations
(these are non-statutory). SEPA Policy No. 17 contains
short term (3 to 72 hours) EQSs in the form of maximum
allowable concentrations. The SEPA Fish Farming
Manual explains the application of these EQSs.
Cypermethrin is a synthetic pyrethroid (see Section
B20 for general information on synthetic pyrethroid
pesticides) that has recently been granted market
authorisation by SEPA as a bath treatment for the
removal of sea lice. The Environment Agency is currently
investigating the effects of cypermethrin on aquatic
organisms with a view to deriving EQSs. SEPA Policy
No. 30 contains EQSs in the form of short-term maximum
allowable concentrations and an annual average.
The SEPA Fish Farming Manual explains the application
of these EQSs.
Teflubenzuron is the active ingredient of
Calcide which is a new in-feed sea lice treatment
which has recently been granted limited market authorisation
by SEPA. SEPA Policy No. 29 contains EQSs for this
chemical in the water column in the form of a short-term
(3 hour) maximum allowable concentration and in
the sediment in the form of a maximum allowable
concentration in surface sediment outside an allowable
impact zone and as an average for surface sediment
within the zone of impact. The SEPA Fish Farming
Manual explains the application of these EQSs.
Ivermectin is an in-feed sea lice treatment and
EQSs have been proposed in the water column in the
form of annual averages and maximum allowable concentrations
(these are non-statutory). SEPA Policy No. 2 deals
with the application of ivermectin in fish farming
and the SEPA Fish Farm Manual explains the application
of the existing standards.
Antimicrobials are used as treatments for diseases.
These chemicals can be persistent in seabed sediments
and reduce metabolic processes of micro-organisms.
Problems caused by a bacterial infection, furunculosis,
in the 1980s required the use of substantial quantities
of antibiotics which had the potential of causing
environmental harm. Reviews, and (where possible)
EQSs (although these are not statutory) have been
proposed for the protection of saltwater organisms
for a number of chemicals used as antimicrobials
or disinfectants, namely oxolinic acid, oxytetracycline,
malachite green and formaldehyde (Murgatroyd et
al 1994; Gendebien et al 1994; Burchmore
and Wilkinson 1993; Jerman and Wilkinson 1993).
The reader is referred to these studies for further
information on the effects of saltwater organisms.
However, SEPA has suggested that the industry is
no longer dependent on chemical treatments following
the introduction of vaccination.
Antifoulant paints which contain toxic chemicals
for preventing growth of marine plants and animals
are used on fish cage structures and nets. These
chemicals will gradually be released to the marine
environment. The move to deploy bigger net enclosures
is viewed with concern as this involves the use
of increased chemical antifoulant coating as the
nets are larger and it becomes uneconomical to change
them regularly. The washing of antifoulant coated
nets also causes concern as the spent washings have
been found to contain unacceptably high concentrations
of copper and zinc.
Micro-nutrients (e.g. zinc) are added to fish feeds.
There are indications of elevated levels in sediments
below cages which require further investigation.
Anaesthetics and disinfectants are also used, but,
according to SEPA, these are not currently perceived
to pose a significant environmental risk.
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References
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