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Emergence Traps (emergence + trap)

Distribution by Scientific Domains

Life Sciences	71%
Earth and Environmental Science	28%

Selected Abstracts

Adaptations of an Emergence Trap for Use in Tropical Streams

INTERNATIONAL REVIEW OF HYDROBIOLOGY, Issue 4 2004
Hendrik Freitag
Abstract An emergence trap based on the MPI Schlitz model was designed for use in the tropics and it was tested over one year in Palawan, the Philippines. Instructions for construction and use are given here. Only commonly available materials were used, except for the collection assembly made of UV-light permeable acrylic glass. Heavy and bulky assemblies were avoided to enable easy transportation in the field. A special modification allows a fast and easy replacement of the screen when damaged by flooding, as is often required when traps are used downstream of headwaters. This type of trap also allows sampling of a wide littoral strip. Problems concerning the use of emergence traps in the humid tropics are discussed based on experience at different longitudinal stream sections in Palawan. The results presented here suggest that this trap should be used especially for qualitative or semi-quantitative approaches. (© 2004 WILEY-VCH Verlag GmbH & Co. KGaA, Weinheim) [source]

Benthic secondary production and biomass of insects emerging from a northern German temperate stream

FRESHWATER BIOLOGY, Issue 2 2000
Rainer Poepperl
Summary 1Secondary production and emergence of aquatic insects were examined in the outlet of Lake Belau, Northern Germany, by means of benthic samples and emergence traps. 2At three stream sections annual larval secondary production varied between 4.9 and 10.8 gDM (dry mass) m -2 year -1. Insects contributed with 3.4, 8.9, and 8.7% to the total macroinvertebrate production that varied between 56.5 and 215.1 gDM m -2 year -1. Emerged biomass was between 1.0 and 2.0 gDM m -2 year -1. At all three stream sections Diptera dominated with a larval production of 3.0,l6.1 gDM m -2 year -1, followed by Trichoptera with 1.0,2.1 and Ephemeroptera with up to 0.9 gDM m -2 year -1. 3Average larval production amounted to 9.0 gDM m -2 year -1 and emerged biomass to 1.7 gDM m -2 year -1. Larvae of insects amounted to 7.0% of total macroinvertebrate production. 4The ratio of annual emerged biomass to secondary production (E/P) varied among individual taxa. At the stream sections the ratio ranged from 15.9% to 20.1% with an average of 18.3% for the stream. 5Relative constancy of the E/P ratio suggests that the determination of emerged biomass can be used as a method for estimating the secondary production of aquatic insects. The composition of functional feeding groups clearly differs between emerged biomass and total macroinvertebrate production. Therefore, the method does not allow conclusions on the level of production of the whole benthic community. However, composition of functional feeding groups at emergence roughly reflects composition of these groups in the benthic insect community. [source]

Adaptations of an Emergence Trap for Use in Tropical Streams

Effect of time of year on the development of immature stages of the Large Pine Weevil (Hylobius abietis L.) in stumps of Sitka spruce (Picea sitchensis Carr.) and influence of felling date on their growth, density and distribution

JOURNAL OF APPLIED ENTOMOLOGY, Issue 3 2004
R. Moore
Abstract:, The time of year and time of felling of a commercial stand of Sitka spruce (Picea sitchensis Carr.) were both shown to influence the spatial distribution and development of the large pine weevil, Hylobius abietis (L). Stump and root systems were excavated over a 5-month period in 1997, between 18 and 27 months after felling, and all immature H. abietis removed. On a site with a 6-month spread of felling dates in 1995, mean larval weights in 1997 were higher in stumps from earlier fellings, but H. abietis numbers were higher in stumps from later fellings. This appeared to be due to the continued presence of older, heavier larvae, laid as eggs in 1995, in stumps from earlier fellings, combined with a greater concentration of oviposition having occurred in 1996 in the fresher stumps of later fellings. Pupae were first found in excavated stumps on 12 June 1997 and adults on 29 July 1997. Emergence of the ,new generation' of adult weevils commenced on 7 August 1997. On average, 25% of H. abietis adults emerged in autumn 1997, 41% in 1998 and 34% in 1999. First emergence (1997) was proportionally higher in the areas felled earlier in 1995 than those felled later that year. However, the opposite was found for third emergence (1999) where emergence was greater for stumps created later in 1995. Larger stumps contained greater densities of H. abietis. Total ,potential' emergence was estimated to be between 46400 and 170825 H. abietis/ha. However, emergence traps indicated that only 40,80% managed to complete their development and emerge successfully. It is suggested that within-season felling date may be one of the most important factors affecting larval development, distribution and abundance; as well as subsequent damage levels associated with adult feeding. Consequently, knowledge of felling date could be crucial to developing methods of integrated forest management for this major forest pest. [source]

Interactions between gnathiid isopods, cleaner fish and other fishes on Lizard Island, Great Barrier Reef

JOURNAL OF FISH BIOLOGY, Issue 9 2008
A. S. Grutter
The rate of emergence of micropredatory gnathiid isopods from the benthos, the proportion of emerging gnathiids potentially eaten by Labroides dimidiatus, and the volume of blood that gnathiids potentially remove from fishes (using gnathiid gut volume) were determined. The abundance (mean ±s.e.) of emerging gnathiids was 41·7 ± 6·9 m,2 day,1 and 4552 ± 2632 reef,1 day,1 (reefs 91,125 m2). The abundance of emerging gnathiids per fish on the reef was 4·9 ± 0·8 day,1; but excluding the rarely infested pomacentrid fishes, it was 20·9 ± 3·8 day,1. The abundance of emerging gnathiids per patch reef was 66 ± 17% of the number of gnathiids that all adult L. dimidiatus per reef eat daily while engaged in cleaning behaviour. If all infesting gnathiids subsequently fed on fish blood, their total gut volume per reef area would be 17·4 ± 5·6 mm3 m,2 day,1; and per fish on the reefs, it would be 2·3 ± 0·5 mm,3 fish,1 day,1 and 10·3 ± 3·1 mm3 fish,1 day,1 (excluding pomacentrids). The total gut volume of gnathiids infesting caged (137 mm standard length, LS) and removed from wild (100,150 mm LS) Hemigymnus melapterus by L. dimidiatus was 26·4 ± 24·6 mm3 day,1 and 53·0 ± 9·6 mm3 day,1, respectively. Using H. melapterus (137 mm LS, 83 g) as a model, gnathiids had the potential to remove, 0·07, 0·32, 0·82 and 1·63% of the total blood volume per day of each fish, excluding pomacentrids, caged H. melapterus and wild H. melapterus, respectively. In contrast, emerging gnathiids had the potential of removing 155% of the total blood volume of Acanthochromis polyacanthus (10·7 mm LS, 0·038 g) juveniles. That L. dimidiatus eat more gnathiids per reef daily than were sampled with emergence traps suggests that cleaner fishes are an important source of mortality for gnathiids. Although the proportion of the total blood volume of fishes potentially removed by blood-feeding gnathiids on a daily basis appeared to be low for fishes weighing 83 g, the cumulative effects of repeated infections on the health of such fish remains unknown; attacks on small juvenile fishes, may result in possibly lethal levels of blood loss. [source]

Patterns of saproxylic beetle succession in loblolly pine

AGRICULTURAL AND FOREST ENTOMOLOGY, Issue 2 2010
Michael D. Ulyshen
1Patterns of insect succession in dead wood remain unclear, particularly beyond the first several years of decay. In the present study, saproxylic beetles were sampled from loblolly pine (Pinus taeda L.) logs aged between 1 month and 9 years old using both emergence traps attached to logs in the field and rearing bags in the laboratory. 2Species richness peaked within the first year as a result of a diverse assemblage of bark beetles, wood-borers and predators associated with young logs. After the phloem phase, there were no significant differences in species richness among decay classes. 3Beetle communities differed significantly among decay classes, with 25 and seven species being significantly associated with young and old logs, respectively. [source]