Water Balance in the Aquatic Bugs Notonecta Glauca L

Total Page:16

File Type:pdf, Size:1020Kb

Water Balance in the Aquatic Bugs Notonecta Glauca L J. Exp. Biol. (1963), 40, 563-571 563 Jtjth 4 text-figures ^^mted m Great Britain WATER BALANCE IN THE AQUATIC BUGS NOTONECTA GLAUCA L. AND NOTONECTA MARMOREA FABR. (HEMIPTERA; HETEROPTERA) BY B. W. STADDON Department of Zoology, University College of South Wales and Monmouthshire, Cardiff (Received 29 April 1963) INTRODUCTION Several workers have investigated mechanisms of water balance in aquatic insect larvae. An account of the mechanism of water balance in the mosquito larva Aedes aegypti L. will be found in papers by Wigglesworth (1933) and Ramsay (1950, 1951, 1953). Beadle (1939) and Ramsay (1950) give an account of the situation in the larva of Aedes detritus Edw. The alderfly larva Sialis lutaria L. has been studied by Shaw (1955a, b); Limnephilus affinis Curt, and other trichopterous larvae by Sutcliffe (1961a, b, 1962). Aquatic imagines have attracted little attention and the work to be described in this paper goes some way towards remedying this situation. MATERIAL AND METHODS The investigation was carried out on two closely related species of aquatic bug, Notonecta glauca L. and N. marmorea Fabr. The bugs were collected from ponds and ditches in Monmouthshire and Glamorgan. Both species occurred together in ponds lying very close to the sea; elsewhere N. marmorea appeared to be absent. N. marmorea is reported to occur mainly in brackish waters in coastal areas (Southwood & Leston, 1959), unlike N. glauca which appears to be confined to fresh waters, and it was hoped that a comparison of the two species would throw some light on these differences in distribution. Adult specimens varied a great deal in weight, but no attempt was made to obtain uniformity in this respect. Adults of N. glauca ranged in weight from about no to 150 mg. and adults of the somewhat smaller N. marmorea ranged from about 100 to 120 mg. To facilitate comparison uptake and output measurements have been calculated in terms of a standard body weight of 100 mg. In the laboratory the bugs were kept without food in separate containers until required, and the experiments were carried out at a temperature of about 180 C. Collection and analysis of rectal fluid. Measurements were made on the clear fluid voided from the anus of the intact bug. In order to obtain this fluid a bug was carefully dried on filter-paper and placed in a wax-lined dish. The specimen was gently secured in order to induce the ejection of fluid which was collected in a capillary pipette and analysed without delay. For the purpose of routine ammonia measurements bugs were narcotized with CO2 in order to induce the ejection of fluid from the rectum and this had the advantage that handling was reduced to a minimum. 36 Exp. Biol. 40, 3 564 B. W. STADDON Ammonium, bicarbonate and conductivity measurements were made in dupli^B or triplicate and 0-2 /xl. of fluid was used for each determination. Ammonium was measured by the diffusion method described by Shaw & Beadle (1949) and o-oi N-HC1 was used for the titration. In order to facilitate the mixing of the sample and alkali in the diffusion chamber a clear lid was employed and the absorbing acid was placed on the floor of the chamber. Bicarbonate was measured by direct titration of the sample with o-oi N-HC1 which contained 5 ml. of B.D.H. '4-5' indicator per 100 ml. A measure of the total ionic concentration was obtained by comparing the conductivity of samples diluted in about 44 (A. of de-ionized water in a Perepex conductivity cell (Shaw & Staddon, 1958) with the conductivity of standard solutions of ammonium bicarbonate prepared in the same way. Ammonium was measured with an average error of ± 2 mM./l., bicarbonate with an error of ± 4 mM./l. and conductivity measure- ments with an average error of ± 2 mM./l. Output of water in the rectal fluid. This was deduced from measurements of the rate of ammonia output and of the concentration of ammonia in the rectal fluid. Given the rate of ammonia output (in /*M./day) and the concentration of ammonia in the rectal fluid (in pM.//tl.) then division of one term by the other gives directly the output of water in the rectal fluid (in /xl./day). In order to measure the rate of ammonia output a bug was placed in 25 ml. of de-ionized water in a covered beaker. At the end of 24 hr. the ammonia content of the water was measured colorimetrically and for this purpose Nessler's reagent was used. This method of collecting ammonia appeared to be reliable as shown by the fact that on removing a bug at the end of the 24 hr. period the concentration of ammonia in the water underwent little or no change during a further period of 24 hr. Now the concentration of ammonia in the rectal fluid was measured by diffusion analysis and the output of ammonia was measured colorimetrically. Dissimilar methods of analysis may yield dissimilar results, and it was clearly necessary to check this possibility. To make this check several samples of rectal fluid were pooled and ana- lysed by both methods. The results which were obtained by the two methods did not differ significantly. Ingestion of water. The uptake of water into the gut was measured with the aid of amaranth. A specimen was placed in an o-oi M solution of the dye for a period of 8 hr. It was then removed, washed with water and narcotized with COj. The dye was extracted from the gut and for this purpose the method devised by Treherne (1957) was closely followed. The gut was dissected out in isotonic saline and then transferred to 5 ml. of phosphate buffer at pH 10. It was finely ground up with the aid of glass powder. The extract was centrifuged and the concentration of amaranth in the clear supernatant was measured with a Unicam absorptiometer at an absorption maximum of 525 m/i. A slight correction had to be made to each measurement to allow for the effect of soluble gut material on absorption. Given the quantity of dye in the gut (in m/xM.) and the concentration in the external medium (in m^.M.//il.) then division of one term by the other gives the volume of water (in /J.) ingested in the 8 hr. period. The procedure was tested by feeding individual bugs on a measured quantity of dye. To do this each bug was narcotized by means of CO2 and the proboscis was sealed into a small wax-lined tube with a warm mixture of beeswax and rosin. A quantity of Water balance in aquatic bugs 565 ^Raranth, 10 /A. of an o-oi M solution, was introduced into the tube which was then covered in order to reduce evaporation. The bug was left in air to consume the fluid overnight. The small traces of amaranth which remained on the sides of the tube were washed out and measured in order to obtain an accurate measure of the quantity actually ingested. The quantity of amaranth recovered from the gut was always over 97 % of that ingested which shows that there can be little, if any, absorption from the gut lumen. The reason for selecting an experimental period of 8 hr. was to avoid the loss of amaranth from the gut by evacuation in the rectal fluid. In 8 hr. the dye may have reached but not travelled beyond the pyloric valve; in 12 hr. the rectal fluid is frequently coloured with the dye. A more direct method was also used to measure the ingestion of water. This entailed sealing the proboscis into a capillary tube of about 1 mm. external diameter with the beeswax-rosin mixture. The tube was filled with water to a mark and then secured vertically so as to suspend the bug in water in its normal resting position just beneath the surface. The decreased volume of water in the tube was recorded 24 hr. later. This method had the advantage that simultaneous measurements of water output could be made. RESULTS (a) Excretion of ammonia. Ammonia is quantitatively the most important nitro- genous excretory product of adult bugs kept without food. Measurements of total-N and ammonia-N showed that approximately 75 % of the total-N in the rectal fluid of N. glauca is in this form. The rectal fluid is not a dilute one for the mean conductivity (92 mM./l.) of the measurements which are recorded in Table 1 is as much as 56 % of that of the haemolymph (165 mM./l. as equiv. NaCl) and the greater part of the ionic material is in the form of ammonium bicarbonate. A fluid of similar composition is produced by the larval SiaUs hitaria L. (Shaw, 19556). Table 1. The composition of the rectal fluid of Notonecta glauca Sample 1 a 3 Mean Conductivity as equiv. 107 90 78 9a ammonium bicarbonate soln. (mM./l.) Ammonium (mM./l.) 97 75 54 75 Bicarbonate (mM./l.) 84 78 62 75 The output of ammonia fluctuates a little from day to day as shown by the results of measurements which are recorded in Table 2. It is not known what causes these fluctuations in ammonia output but small fluctuations in the output of rectal fluid may be partly responsible. (b) Relationship between water output and ammonia output. In view of the fact that ammonia is the major end product of protein catabolism in Notonecta adults it is of interest to know whether the output of water in the rectal fluid is closely related to the output of ammonia.
Recommended publications
  • Folk Taxonomy, Nomenclature, Medicinal and Other Uses, Folklore, and Nature Conservation Viktor Ulicsni1* , Ingvar Svanberg2 and Zsolt Molnár3
    Ulicsni et al. Journal of Ethnobiology and Ethnomedicine (2016) 12:47 DOI 10.1186/s13002-016-0118-7 RESEARCH Open Access Folk knowledge of invertebrates in Central Europe - folk taxonomy, nomenclature, medicinal and other uses, folklore, and nature conservation Viktor Ulicsni1* , Ingvar Svanberg2 and Zsolt Molnár3 Abstract Background: There is scarce information about European folk knowledge of wild invertebrate fauna. We have documented such folk knowledge in three regions, in Romania, Slovakia and Croatia. We provide a list of folk taxa, and discuss folk biological classification and nomenclature, salient features, uses, related proverbs and sayings, and conservation. Methods: We collected data among Hungarian-speaking people practising small-scale, traditional agriculture. We studied “all” invertebrate species (species groups) potentially occurring in the vicinity of the settlements. We used photos, held semi-structured interviews, and conducted picture sorting. Results: We documented 208 invertebrate folk taxa. Many species were known which have, to our knowledge, no economic significance. 36 % of the species were known to at least half of the informants. Knowledge reliability was high, although informants were sometimes prone to exaggeration. 93 % of folk taxa had their own individual names, and 90 % of the taxa were embedded in the folk taxonomy. Twenty four species were of direct use to humans (4 medicinal, 5 consumed, 11 as bait, 2 as playthings). Completely new was the discovery that the honey stomachs of black-coloured carpenter bees (Xylocopa violacea, X. valga)were consumed. 30 taxa were associated with a proverb or used for weather forecasting, or predicting harvests. Conscious ideas about conserving invertebrates only occurred with a few taxa, but informants would generally refrain from harming firebugs (Pyrrhocoris apterus), field crickets (Gryllus campestris) and most butterflies.
    [Show full text]
  • Common Backswimmer Notonecta Glauca (Linnaeus 1758) (Hemiptera: Notonectidae)1 Taryn B
    EENY-738 Common Backswimmer Notonecta glauca (Linnaeus 1758) (Hemiptera: Notonectidae)1 Taryn B. Griffith and Jennifer L. Gillett-Kaufman2 Introduction Notonecta glauca, the common backswimmer (Figure 1), is an aquatic insect in the family Notonectidae. Insects in this family are commonly referred to as backswimmers or greater water boatman. Notonectids propel themselves through the water with their ventral side (belly) facing upwards, hence their common name of backswimmers (Figure 2). Notonectids can inflict wounds to humans with Figure 2. Notonecta sp. adult resting upside down underwater, which their proboscis (mouthpart), but this is very rare and often is typical of all Notonectids. is a result of rough handling. Credits: JRxpo. Flickr.com Distribution Although commonly collected in Europe (Soós et al. 2009), the common backswimmer can range from parts of northern Africa to western Siberia and northwestern China (Berchi 2013). Notonecta glauca is typically found in inland freshwater ponds, although they can be found in eutrophic (water excessively enriched in nutrients) freshwater bodies near the sea (Kjærstad et al. 2009). Many other Notonecta species occur in North America north of Mexico (Torre Bueno 1905). It is unclear if this species could become established if introduced to Florida, but its current distribu- tion includes several locations with similar climates and habitats. Figure 1. An adult Notonecta glauca (Linnaeus). Credits: David Nicholls 1. This document is EENY-738, one of a series of the Entomology and Nematology Department, UF/IFAS Extension. Original publication date August 2019. Visit the EDIS website at https://edis.ifas.ufl.edu for the currently supported version of this publication.
    [Show full text]
  • Predator-Induced Defences in Daphnia Longicephala: Location of Kairomone Receptors and Timeline of Sensitive Phases to Trait Formation Linda C
    © 2015. Published by The Company of Biologists Ltd | Journal of Experimental Biology (2015) 218, 2918-2926 doi:10.1242/jeb.124552 RESEARCH ARTICLE Predator-induced defences in Daphnia longicephala: location of kairomone receptors and timeline of sensitive phases to trait formation Linda C. Weiss1,2,*, Julian Leimann2 and Ralph Tollrian2 ABSTRACT defences that oppose the current predatory threat and increase The freshwater crustacean Daphnia adapts to changing predation survival chances of the individual. These, so-called inducible risks by forming inducible defences. These are only formed when defences can manifest as behavioural, morphological or shifts in they are advantageous, saving associated costs when the defence is life-history parameters and are elicited upon the perception of ‘ ’ superfluous. However, in order to be effective, the time lag between predator-specific chemical cues called kairomones . All of these the onset of predation and the defence formation has to be short. inducible defensive strategies incur costs that are saved when the Daphnia longicephala develop huge protective crests upon exposure defence is not essential (Auld et al., 2010; Barry, 2002; DeWitt, to chemical cues (kairomones) from its predator the heteropteran 1998; Tollrian and Dodson, 1999; Walls et al., 1991). In addition, backswimmer Notonecta glauca. To analyse time lags, we costs are kept at a minimum, as many species scale their defences to determined kairomone-sensitive stages and the developmental time the predation risk and the magnitude of defence formation is directly frames of inducible defences. Moreover, we looked at additive correlated with the concentration of predator kairomones (Tollrian, effects that could result from the summation of prolonged kairomone 1993).
    [Show full text]
  • The Backswimmer Notonecta Glauca L. (Hemiptera, Notonectidae) in Central Norway
    © Norwegian Journal of Entomology. 5 June 2009 The backswimmer Notonecta glauca L. (Hemiptera, Notonectidae) in Central Norway GAUTE KJÆRSTAD, DAG DOLMEN, HANS A. OLSVIK & EVA TILSETH Kjærstad, G., Dolmen, D., Olsvik, H.A. & Tilseth, E. 2009. The backswimmer Notonecta glauca L. (Hemiptera, Notonectidae) in Central Norway. Norw. J. Entomol. 56, 44–49. In Central Norway, the backswimmer Notonecta glauca L., 1758 occurs on the northern margin of its distribution area. The species has recently dispersed northwards, both naturally along the west coast and inland from an introduced population in Trondheim. The history of N. glauca records in the Trondheim district is presented in detail, and new records from Central Norway and some habitat characteristics are given. In the next few decades, we expect the species to become more widely distributed and abundant in Central Norway and northwards. Key words: Hemiptera, Notonecta glauca, distribution, Central Norway Gaute Kjærstad, Norwegian University of Science and Technology, Museum of Natural History and Archaeology, NO-7491 Trondheim, Norway. E-mail: [email protected] Dag Dolmen, Norwegian University of Science and Technology, Museum of Natural History and Archaeology, NO-7491 Trondheim, Norway. E-mail: [email protected] Hans A. Olsvik, Olsvika, NO-6694 Foldfjorden, Norway. E-mail: [email protected] Eva Tilseth, Håkon Herdebreis vei 4, NO-7046, Trondheim, Norway. E-mail: [email protected] Introduction bog ponds or lakelets with little vegetation, apart from Sphagnum mosses, in the southeastern part Three species of backswimmer, Notonecta glauca of the country (Dolmen 1989a). N. lutea and N. L., 1758, N. lutea Müller, 1776 and N.
    [Show full text]
  • First Record of the Backswimmer Notonecta Meridionalis (Hemiptera: Heteroptera: Notonectidae) in Romania
    Travaux du Muséum National d’Histoire Naturelle © 28 décembre «Grigore Antipa» Vol. LV (2) pp. 217–220 2012 DOI: 10.2478/v10191-012-0013-y FIRST RECORD OF THE BACKSWIMMER NOTONECTA MERIDIONALIS (HEMIPTERA: HETEROPTERA: NOTONECTIDAE) IN ROMANIA GAVRIL MARIUS BERCHI, PETR KMENT, MILCA PETROVICI Abstract. Notonecta meridionalis Poisson, 1926 is present in almost all circum-Mediteranean countries and shouthern parts of Central Europe. First record of this species from Romania is given. Résumé. Notonecta meridionalis Poisson, 1926 est présente dans les pays circum-méditerrannéens et dans la region sudique de l’Europe Centrale. C’est la première mention de cette éspèce en Roumanie. Key words: true bugs, new record, hemelytron variability, Palaearctic Region. The backswimmers (family Notonectidae) are represented worldwide with 11 genera and nearly 400 species (Polhemus, 2009), but in Europe only 3 genera and 13 species occur (Notonecta Linnaeus, 1758 – 9 species, Anisops Spinola, 1837 – 3 species, Nychia Stål, 1860 – 1 species) (Polhemus, 1995; Aukema, 2011). Among others, Paina (1975) listed for Romania 2 species of Notonectidae, subfamily Notonectinae: Notonecta glauca glauca Linnaeus, 1758 and N. viridis Delcourt, 1909. Besides the two previous species, Kis & Davidescu (1994) recorded one female specimen of N. lutea Müller, 1776 from the Danube Delta. The list of this family was complemented recently by Anisops sardeus sardeus Herrich-Schaeffer, 1849 belonging to subfamily Anisopinae (Berchi, 2011). There are no records of N. meridionalis in Romania so far. Notonecta (Notonecta) meridionalis Poisson, 1926 (syn: Notonecta obliqua meridionalis Poisson, 1926) (syn: Notonecta glauca hybrida Poisson, 1933) Material examined. South-western Romania: Mehedinţi county: Sviniţa – Porţile de Fier Nature Park, 44°33′15″ N; 22°02′35″ E, 147 m alt., puddle formed on the course of a spring, 6.XI.2011, 4 ♂♂ 7 ♀♀, G.
    [Show full text]
  • AI 2010 5 4 Copp Etal Suppl
    Aquatic Invasions (2010) Volume 5, Issue 4: 413–422 doi: 10.3391/ai.2010.5.4.11 Open Access © 2010 The Author(s). Journal compilation © 2010 REABIC Research article Preliminary assessment of feral goldfish impacts on ponds, with particular reference to native crucian carp Gordon H. Copp, A. Serhan Tarkan, Michael J. Godard, Nathan J. Edmonds and Keith J. Wesley Supplementary material Appendix 1. List of aquatic invertebrates (summarized in Table III) observed in ponds of Epping Forest (Essex, England) during the week of 23 April 2007, with their status, rarity score, description. (FM = Fairmeads; EP = Earl's Path; HC = Hawcock; CP = Carroll's; PP = Pizzole Pit; JP = Johnson's). Non-native species are indicated with an asterisks, and nationally notable species are indicated as ‘Nat. Notable B’. Species Status Rarity Description FM EP HC CP PP JP Polycelis tenuis Common 1 A flatworm 4 1 3 Erpobdella octoculata Common 1 A leech 1 5 2 Erpobdella testacea Common 1 A leech 1 8 Glossiphonia complanata Common 1 A leech 1 4 10 1 Helobdella stagnalis Common 1 A leech 2 2 12 7 2 Theromyzon tessulatum Common 1 A leech 1 2 Trocheta bykowski Local 2 A leech 8 Acroloxus lacustris Common 1 Lake limpet 2 4 1 Gyraulus albus Common 1 White ram's-horn 3 5 3 Gyraulus crista Common 1 Nautilus ram's-horn 2 1 Hippeutis complanatus Common 1 Flat ram's-horn 1 96 1 1 1 Radix balthica Common 1 Wandering snail 1 1 Lymnaea stagnalis Common 1 Great pond snail 3 Physella (acuta)* Common 1 Tadpole snail 178 3 2 Planorbarius corneus Common 1 Great ram's-horn 3 2 34 Planorbis
    [Show full text]
  • 423 – Aquatic Hemiptera of Northeastern
    AQUATIC HEMIPTERA OF NORTHEASTERN ALGERIA: DISTRIBUTION, PHENOLOGY AND CONSERVATION Fouzi ANNANI 1,2, Ahmed H. AL F ARHAN 3 & Boudjéma SA M RAOUI 1,3* RÉSUMÉ.— Hémiptères aquatiques du nord-est de l’Algérie : distribution, phénologie et conserva- tion.— L’échantillonnage de 83 sites à travers le complexe de zones humides du nord-est Algérien, un point chaud de la biodiversité aquatique, a permis d’identifier 35 espèces d’hémiptères aquatiques. La répartition et la phénologie des espèces sont présentées et les histoires de vie de Notonecta glauca et Notonecta obli- qua déduites. Ces deux espèces estivent dans des milieux refuges à hautes altitudes avant de redescendre se reproduire en plaine à l’automne. Diverses manifestations de changements globaux (pompage de l’eau, construction de barrages, introduction d’espèces exotiques et fragmentation des milieux) influencent néga- tivement l’intégrité écologique des milieux de la région étudiée. SUMMARY.— A survey, involving the sampling of 83 sites, investigated the aquatic hemiptera of north- eastern Algeria, a well known hotspot of aquatic biodiversity. The study recorded 35 species with data on distribution and phenology presented and discussed. Aspects of the life history of some species (Notonecta glauca and Notonecta obliqua) were inferred from their distribution and phenology and they were found to aestivate at high altitude refuges. Insect conservation in North Africa is still embryonic, relying mainly on protected areas to provide surrogate conservation to a rich and diverse group. This is inadequate in view of the current distribution of aquatic insects, often located in unprotected habitats (intermittent streams, temporary pools, dunary ponds) and the fact that diverse manifestations of global changes (loss of habitats due to water extraction and dam construction, invasive species, habitat fragmentation) are fast eroding the biodiversity of protected areas.
    [Show full text]
  • Download PDF File
    M. Bazzanti et al.: Ann. Limnol. - Int. J. Lim. 45 (2009) 29–39 1 Online material Appendix 1. Functional traits assigned to taxa collected at the study ponds. FFG=Functional feeding groups: CG=Collector- gatherers, CF=Collector-filterers, PR=Predators, SH=Shredders, SC=Scrapers. HAB=Habits: BU=Burrowers, SP=Sprawlers, CL=Climbers, SW=Swimmers, DI=Divers, SK=Skaters. WIG=Groups of Wiggins et al. (1980): 1–4, ?=unknown. TAXA FFG HAB WIG TAXA FFG HAB WIG HYDROZOA S. striolatum PR CL, SP 3 Hydra sp. PR SP 1 S. meridionale PR CL, SP 3 TURBELLARIA undet. PR CL, SP 1 HEMIPTERA OLIGOCHAETA undet. CG BU 1 Corixa affinis SH SW 4 C. punctata SH SW 4 HIRUDINEA Hesperocorixa moesta SH CL, SW 4 Helobdella stagnalis PR CL, SP 1 Sigara lateralis CG, SH CL, SW 4 Placobdella costata PR CL, SP 1 Sigara nigrolineata CG, SH CL, SW 4 Erpobdellidae undet. PR CL, SP 1 S. basalis CG, SH CL, SW 4 Hirudinidae undet. PR CL, SP 1 Sigara sp. CG, SH CL, SW 4 ANOSTRACA Micronecta scholtzi PR CL, SW 4 Chirocephalus diaphanus CF SW 1 Ilyocoris cimicoides PR CL, SW 4 C. kerkyrensis CF SW 1 Ranatra linearis PR CL 4 NOTOSTRACA Anisops sardeus PR CL, SW 4 Lepidurus apus lubbocki SH, PR CL, SP 1 Notonecta glauca PR CL, SW 4 ISOPODA N. maculata PR CL, SW 4 Proasellus gr. coxalis SH CL, SP 1 N. viridis PR CL, SW 4 Plea minutissima PR CL, SW 4 AMPHIPODA Gerris argentatus PR SK 4 Echinogammarus veneris SH CL, SP 1 G.
    [Show full text]
  • Survey of Ponds at Gallows Bridge Farm Nature Reserve, Buckinghamshire
    A survey of ponds at Gallows Bridge Farm Nature Reserve, Buckinghamshire A report for the Freshwater Habitats Trust Martin Hammond Ecology [email protected] September 2016 1. Introduction Gallows Bridge Farm forms part of the Upper Ray Meadows complex owned by the Berkshire, Buckinghamshire and Oxfordshire Wildlife Trust (BBOWT). Six ponds were surveyed on 19th and 20th September 2016. A range of relict stream channels and foot drains were dry at the time of the survey, as were three small ponds in the southern meadows (Ponds 16 to 18, around SP 664 198). Tetchwick Brook, a small tributary of the River Ray, was sampled briefly at three locations to provide additional records. Each pond was surveyed as per the PSYM methodology (Environment Agency, 2002), i.e. three minutes netting time divided equally between each of the meso-habitats present plus one minute examining the water surface and submerged debris. Where it was considered that additional sampling effort was warranted, additional netting was carried out but the taxa thus found were recorded separately. As far as possible, all material was identified to species level and raw data have been provided in spreadsheet format. 2. The ponds surveyed Pond Field: Main Pond (SP 669 199) The Pond Field contains around 30 ponds created by Freshwater Habitats Trust. The Main Pond is the permanent pond nearest the car park. It is a shallow, clay-bedded pond with patchy Broad-leaved Pondweed Potamogeton natans and stoneworts Chara spp., with low emergent vegetation around its banks. Nine-spined Sticklebacks are present. A total of 45 species were recorded (40 in the PSYM sample), notably including the Nationally Scarce reed-beetle Donacia thalassina.
    [Show full text]
  • Heteroptera - Bloodsucking Mosquitoes in the Reservoirs of the Charyn State National Natural Park
    Flora and fauna N E W S OF THE NATIONAL ACADEMY OF SCIENCES OF THE REPUBLIC OF KAZAKHSTAN SERIES OF BIOLOGICAL AND MEDICAL ISSN 2224-5308 Volume 3, Number 339 (2020), 35 - 40 https://doi.org/10.32014/2020.2519-1629.21 UDC 595.754 Т.О. Altynbek1, PA. Esenbekova2, М.Б. Zhaksybayev1 1Abai Kazakh National Pedagogical University, Almaty, Kazakhstan; 2Institute oF Zoology, Almaty, Kazakhstan. E-mail: [email protected], [email protected], [email protected] NATURAL REGULATORS OF HETEROPTERA - BLOODSUCKING MOSQUITOES IN THE RESERVOIRS OF THE CHARYN STATE NATIONAL NATURAL PARK Abstract. The present article deals with the role oF bioregulation as a result oF the study oF aquatic Heteroptera in 25 stop-Flowing and slow-Flowing reservoirs on the territory oF Charyn State National Natural Park in the spring- summer period 2019. Experiments were conducted in the laboratory on determination oF the place oF Heteroptera in the bioregulation oF the number oF bloodsucking mosquitoes in reservoirs on the territory oF Charyn State National Natural Park. Laboratory and experimental work was carried out using mosquito larvae and adult specimens oF each Family species to determine their bioregulatory role. As a result oF the study, 21 varieties were identiFied that belong to 7 species oF aquatic Heteroptera. 15 experimental works in nature and 17 experimental control works in laboratories were carried out with the species Nepa cinerea (Linnaeus, 1758), Ranatra linearis (Linnaeus, 1758), Ilyocoris cimicoides (Linnaeus, 1758), Notonecta glauca (Linnaeus, 1758), For which the larvae oF relatives oF bloodsucking mosquitoes Aedes, Culex were used as Fodder. The article presents the average data oF the experiment conducted on these species.
    [Show full text]
  • The Freshwater Bugs (Hemiptera: Heteroptera) of Cheshire
    The freshwater bugs (Hemiptera: Heteroptera) of Cheshire Jonathan Guest Germany. The late Dr. Alan Savage School of Life Sciences, Keele University, STS 5BG. Dr. Ian Wallace Entomology Section, Liverpool Museum, William Brown St., Liverpool, L3 8EN.* ______________________________ *address for correspondence_____________________ Introduction Cheshire is predominantly a lowland county. It has a very large number of ponds, internationally important habitats in the form of meres and mosses, intriguing inland saline waters associated with the salt industry and two major estuaries. Upland water bodies are restricted to the far east of the county. Eleven families of British Heteroptera are grouped as aquatic bugs with 64 species in 23 genera; Cheshire is both well-recorded and well-represented with 10 families, and 48 species in 21 genera. By stark contrast, the record coverage maps in Huxley (2003) show clearly that Lancashire, away from the coast, and especially south Lancashire, is very poorly recorded. Water bugs are very familiar freshwater insects, with most species being easy to catch in a pond-net; a few are best sought by pressing marginal vegetation underwater, and one lives amongst Sphagnum moss. They can be preserved in isopropyl alcohol, or a 70% ethyl alcohol solution - the traditional medium used by freshwater biologists, or pinned, or even carded - but important identification features are found on the underside in several genera. Identification is straightforward and satisfying using Savage (1989) for adults; for immatures of the large family Corixidae see Savage (1999) and for young pondskaters there is Brinkhurst (1959). Information sources Britten (1930) provided the first check-list for Cheshire water bugs, which was updated by Massee (1955) and Judd (1990).
    [Show full text]
  • Autor Benslimane Et
    Anthropogenic stressors are driving a steep decline of hemipteran diversity in dune ponds in north-eastern Algeria Nouara Benslimane, Khémissa Chakri, Dalal Haiahem, Anis Guelmami, Farrah Samraoui, Boudjéma Samraoui To cite this version: Nouara Benslimane, Khémissa Chakri, Dalal Haiahem, Anis Guelmami, Farrah Samraoui, et al.. An- thropogenic stressors are driving a steep decline of hemipteran diversity in dune ponds in north-eastern Algeria. Journal of Insect Conservation, Springer Verlag, 2019, 23 (3), pp.475-488. 10.1007/s10841- 019-00133-1. hal-02403092 HAL Id: hal-02403092 https://hal.archives-ouvertes.fr/hal-02403092 Submitted on 10 Dec 2019 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Anthropogenic stressors are driving a steep decline of hemipteran diversity in dune ponds in north-eastern Algeria Nouara Benslimane1,2 · Khémissa Chakri1,2 · Dalal Haiahem1 · Anis Guelmami3 · Farrah Samraoui1,4 ·Boudjéma Samraoui1,2 Boudjéma Samraoui : [email protected] 1 Laboratoire de Conservation des Zones Humides, Université 8 Mai 1945 Guelma, Guelma, Algeria 2 Department of Biology, University of Annaba, Annaba, Algeria 3 Tour du Valat, Research Institute for the Conservation of Mediterranean Wetlands, Tour du Valat, le Sambuc, 13200 Arles, France 4 Department of Ecology, Université 8 Mai 1945 Guelma, Guelma, Algeria How to cite : Benslimane N., Chakri K., Haiahem D., Guelmami A., Samraoui F., Samraoui B.
    [Show full text]