1Universidade Federal do Rio de Janeiro,
Instituto de Biologia, Departamento de Ecologia. Av. Brigadeiro Trompowski,
s/n. CCS, IB, Laboratório de Ecologia de Insetos, Bloco A, Sala
A0111, Ilha do Fundão 21941-590 - Rio de Janeiro, RJ - Brasil -
Caixa-Postal: 68020. E-mail: figueiro@ioc.fiocruz.br 2Fundação Oswaldo Cruz, Instituto
Oswaldo Cruz, Departamento de Entomologia. Av. Brasil, 4365 - Pav. Carlos
Chagas, Laboratório de Referência Nacional em Simulídeos
e Oncocercose, 4o andar, Sala 7, Manguinhos 21045-900 - Rio de Janeiro,
RJ - Brasil - Caixa-Postal: 926. E-mail: tdocile@ioc.fiocruz.br,
arion@ioc.fiocruz.br
Um Criadouro Artificial para Bioensaios com Larvicidas e Estudos
de Interação com Diptera: Simuliidae e outros Macroinvertebrados
de Sistemas Lóticos
RESUMO - Esta nota apresenta um criadouro artificial para larvas
de Diptera: Simuliidae e demais macroinvertebrados de ambientes lóticos,
composto de um aquário modificado, contendo um sistema de três
canaletas que proporcionam condições simuladas de rio, comportando
uma ampla variação controlável da vazão e da
velocidade da correnteza. Este criadouro é aplicável para
bioensaios com larvas de Diptera: Simuliidae, assim como estudos de interação
com outros macroinvertebrados e efeito de larvicidas em organismos não-alvo.
ABSTRACT - This note presents an artifical breeding site, composed
of a modified aquarium, which allows a wide range of controllable water
discharge and water velocity variation. It is applicable for bioassays
with Diptera: Simuliidae and interaction studies with other macroinvertebrates,
as well as assessing impact of larvicides on non-target organisms.
Several artificial breeding systems have been
applied in bioassays with blackfly larvae over the years. Every system
for evaluating larvicide formulations in the laboratory must generate
water current sufficient for stimulating normal feeding behaviour on the
blackfly larvae (Barton
et al. 1991).
Essentially, there are two categories of artificial systems available for
conducting laboratory bioassays with blackfly larvae. In the closed systems,
water circulation is promoted by the water bubbles from the artificial
oxygenation (Lacey & Mulla 1977) or
magnetic giratory bars (Colbo & Thompson
1978), or through rotating plastic bottles in wax cups (Hembree
et
al. 1980). In the opened systems, the larvae are held on a shallow
channel of flowing water (Hartley 1955, Jamnback
& Frempong-Boadu 1966, Muirhead-Thomson
1957 and
Gaugler
et al. 1980).
The system proposed herein stands in the later category, even though it
can also be used as a closed system. It consists of a modified aquarium
(Fig. 1), based on the model proposed by Araujo-Coutinho (oral communication),
which was applied in Figueiró
et
al. (2002). It is useful not only for larvicide bioassays, but
also for carrying out interaction studies, and therefore, it had to be
suitable for other macroinvertebrates from lotic systems.
Figure 1. Breeding site for larvicide bioassays with blackfly
larvae and other macroinvertebrates.
The aquarium itself has 0.45 m lenght, 0.24 m width and is 0.36 m high,
and features a small reservoir, located on its top, which has 0.115 m lenght,
0.07 m width and is 0.125 m high. The water is constantly pumped from the
bottom to this reservoir, and flows through a channel, which is followed
by two other ones. Each channel is placed in a greater slope than the previous
one, resulting in three different water current velocities for a given
discharge. The three channels are composed of pvc pipes, 0.03 m diameter
each, cut in the half, and fixed to the aquarium walls by using silicone.
After flowing through the channels, the water falls in the bottom of
the aquarium, where it will be pumped back to the reservoir, if the artificial
breeding site is used as a closed system.
Located on the bottom of the aquarium, it is possible to install a sewer,
if one intends to use this as an opened system, allowing a constant substitution
of the water used in the system. The angles of inclination of the channels
are not fixed, and therefore, they can be customized, as long as they form
a sequence of increasingly inclined channels. Therefore, this breeding
site can also be used as a closed system.
The pump used within the artificial breeding site was a Sarlo S180 TM,
which allows up to 180 liters per hour. This pump features a device which
allows controlling the discharge, thus consequently controlling the resulting
water currents flowing through all the three channels. This enables a large
range of water speed variation. The actual range of speed variation depends
mainly on the power of the pump, because it is directly related to the
water discharge range. The breeding site proposed by Araújo-Coutinho
allowed only one single water current speed for each discharge. However,
the architecture of that breeding site did not permit the determination
of the velocity itself, so only the discharges applied in the bioassays
could be calculated. The architecture of this new artificial breeding site,
however, was carefully designed to allow the determination of water current
velocity. The water current velocity is an important abiotic factor for
blackfly larvae (Eymann 1993). The water depth
in the channels allows the use of the float method for determining the
water velocity, which was not possible in the breeding site applied in
Figueiró
et.
al (2002), since its water layer depth was insufficient for this
method.
Another issue that was addressed in this new artificial breeding site
is the substrate used in it. Although the glass surface proved to be efficient
for blackfly larvae colonization, the same did not apply to other organisms.
In order to make the breeding site suitable to other organisms, each of
the three channels was covered by a thin layer of sand, providing a substrate
that proved to be more suitable for their colonization.
The artificial breeding site presented herein could be used for multiple
purposes, aside larvicide bioassays. Its controllable simulated stream
conditions allow interaction studies to be performed, as well as to study
the influence of abiotic factors on lotic macroinvertebrates and assessing
the impact of larvicides on non-target organisms. This feature makes it
a valuable tool for ecological studies in the laboratory.
The breeding site was submitted to 5 series of trials, consisting of
5 days each, on which the survival of blackfly larvae, in the absence of
the larvicide, was evaluated. In each of these series, a number of 20 blackfly
larvae were placed in the breeding site, and submitted to an intermediate
regime of water current velocity, what was previously determined empirically
as the optimal conditions for feeding (Lacey
& Mulla, 1977, Braimah, 1987 and Figueiró
et
al. 2002). In these trials, the mean survival observed for blackflies
after 5 days being reared in the breeding site varied from 47% to 60%,
with 4-6% of them getting to pupae.
In order to further testing the breeding site, the experiment of Figueiró
et
al. (2002), on which the optimal discharge for blackfly larvae
feeding was determined, was duplicated with the presented artificial breeding
site, achieving the same pattern observed in the forementioned study. This
proves it is appropriate for bioassays with biological larvicides, because
these kind of agents require that larvae ingest the active ingredient.
Therefore, an equipment which permits the adjustment of the water current
to a speed where the feeding of the target organism is optimal reducts
the risk of miscalculating the efficacy of these agents. The preliminary
results on bioassays conducted with blackfly larvae in the laboratory were
satisfactory, but further tests of the artificial breeding site for this
purpose were held, and interaction studies are currently being conducted.
Acknowledgements We thank Dr. Marilza Maia-Herzog, for all the support given, as well
as the rest of the staff of the Laboratório de Referência
Nacional em Simulídeos e Oncocercose.
Cited Literature
Barton, W.E., R. Noblet & D.C. Kurtak.
1991. A Simple Technique for determining relative toxicities of Bacillus
thuringiensis var. israelensis formulations against larval blackflies
(Diptera: Simuliidae). J. Am. Mosq. Control Assoc. 7(2): 313-315.
Braimah, S.A. 1987. The influence of water
velocity on particle capture by the labral fans of larvae of Simulium
malloch (Diptera: Simuliidae). Can. J. Zool. 65: 2395-2399.
Colbo, M.H. & B.H. Thompson. 1978.
An efficient technique for laboratory rearing of Simulium verecundum
S.
& J. (Diptera: Simuliidae). Can. J. Zool. 56:507-510.
Eymann, M. 1993. Some boundary layer characteristics
of microhabitats occupied by larval black flies (Diptera: Simuliidae).
Hydrobiol. 259: 57-67.
Figueiró, R., E.S. Nascimento
&
C.J.P.C. Araújo-Coutinho. 2002. Avaliação da influência
da vazão da coluna d'água do criadouro artificial sobre a
captação de partículas por larvas de Simulium pertinax
(Diptera: Simuliidae). Entomologia y Vectores. 9(2): 251-261.
Gaugler, R., D. Molloy, T. Haskins &
G. Rider. 1980. A bioassay system for the evaluation of blackfly (Diptera:
Simuliidae) control agents under simulated stream conditions. Can. Entomol.
112: 1271-1276.
Hartley, C.F. 1955. Rearing simuliids in the
laboratory from eggs to adults. Proc. Helminthol. Soc. Wash. 22: 93-95.
Hembree, S.C., R.L. Frommer & M.P.
Remington. 1980. A bioassay apparatus for evaluating larvicides against
blackflies. Mosq. News 40: 647-650.
Jamnback, H. & J. Frempong-Boadu.
1966. Testing black fly larvicides in the laboratory and in streams.Bull.
Wld Hlth Org. 34: 405-421.
Lacey, L.A. & M.S. Mulla. 1977. A
new bioassay unit for evaluating larvicides against blackflies. J. Econ.
Entomol. 70: 453-456.
Muirhead-Thomson, R.C. 1957. Laboratory
studies on the reactions of Simulium larvae to insecticides. Am.
J. Trop. Med. Hyg. 6: 920-925.