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Aquatic Coleoptera From Lake Xochimilco, Mexico PDF

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302 ENTOMOLOGICALNEWS AQUATIC COLEOPTERA FROM LAKE XOCHIMILCO, MEXICO1 Silvia Santiago-Fragoso, Elizabeth Mejorada-Gomez^ ABSTRACT: Aquatic Coleoptera were collected in Lake Xochimilco, Mexico, from April 1988 through May 1989, plus one collection in 1990. The collection consisted of 3 families with 22 species. The most diverse family was Hydrophilidae with 11 species. The family Dytiscidae was represented by 10 species. Only one species belonging to the family Halip- lidae,Peltodytesmexicanuswascollected. Linedrawingsofthe malegenitaliaareincludedfor the species identified, except for those whose identifications were to genus. Mexico's basin is located at the south border of the Mexican plateau, between 98 15' - 99 30' and 19 00' - 20 15'. This basin is formed by a group of lakes named Texcoco, Chalco, Zumpango, Xaltocan and Xochi- milco. The marshy region with wide and shallow lakes was obliterated by natural aging processes; those processes were accelerated by human actions (Novelo, 1988). Actually, most of these lakes are reduced or have disap- peared. Lake Xochimilco is endangered, therefore this is the main reason to study part ofits fauna. Lake Xochimilco is located SE Mexico city (Fig. 1) (Tamayo de Ham, 1981), at 2270 msnm and its inflow basin is mainly the Ajusco Sierra. At present the lake is reduced to a series of primary, secondary and tertiary channels with the water surrounding the cultivated parcels ("chinampas") and an urban area. METROPOLITAN AREA XOCHIMILCO 19 15' J_< Figure I Locotion of ttuditd area Fig. 1. Lake Xochimilco location. Due to the demographic growth of Mexico city, in 1913 the aqueduct Mexico-Xochimilco was built to provide potable water to the population. 1 ReceivedOctober28, 1998. Accepted Apri 27, 1999. 2 InstitutedeBiologfa, UNAM. Apdo. postal 70-153, Mexico, D.F. C.P. 04510. ENT.NEWS 110(5):302-310,November&December, 1999 Vol. 110, No. 5, November& December, 1999 303 However, in 1953, it was necessary to reduce the water flow to the city because the water resource diminished considerably. That is why in 1959 the Departamento del Distrito Federal decided to reconstitute part of the water & extracted, using treated sewage water (Baez Belmont, 1972). Studies to determine the water quality in the lake have shown a high degree of salinity, and the physicochemical analysis indicate the polisaprobic nature of the water due to the presence ofcoliform bacteria. Also, the high values for the phosphates (up to 28 mg/1) cause eutrophication in the channels (Baez, Bel- mont & Gonzalez,1975). Later, Ramos Espinosa et al. (1993), showed in the Primer Seminario Internacional de Investigadores de Xochimilco results very similar to those mentioned above. In 1988, Lake Xochimilco was declared by UNESCO as patrimony of the world. However, the biodiversity is still threatened (Bojorquez y Olguin, 1993). The dominant vegetation in the channnels are the free-floating hydro- phytes Eichhornia crassipes and Hydromystria laevigata and two species of Lemnaceae, Lemna gibba and Wolffia columbiana. Another important ele- ment characteristic of the typical "chinampera " region SE of the Mexican plateau, is the tree called ahuejote (Salix bonplandiana) (Novelo y Gallegos, 1988). The only studies dealing with aquatic insects from the area are as fol- lows: Salcedo (1978), recorded the following species in the family Dytis- cidae: Cybister explanatus LeConte, Thermonectus basillaris Harris and in the family Hydrophilidae: Tropisternus tinctus Sharp and Paracymus Thom- son. Young (1985) reported a single species in the family Noteridae, Hydro- canthus pallisteri Young from Xochimilco. Also Campos & Fernandez (1993) recorded the heteropteran Belostoma sp., the hydrophilid Tropister- nus lateralis (Fabricius), and the dytiscid, Thermonectus nigrofasciatus Aube. The latterspecies was notpresent in this study. However, anotherspe- cies ofthe same genus, Thermonectus basillaris, was collected by us. METHODS From April 1988 to May 1989 we made 6 collections and one more in January, 1990. The collection sites were mainly in three types of habitats: "apancle", "acalote" and "laguna", as they are called by the local inhabitants. The "apancles" are channels betweeen the chinampas which are shal- low, with slow movement and great quantities ofaquatic plants and detritus produced by plant decay. The "acalotes" are the main channels which are deeper, wider and with greater volume ofwater; also, they are more altered. The "lagunas" are wide open areas that are connected with the channel system. 304 ENTOMOLOGICALNEWS RESULTS AND DISCUSSION During our surveys, we collected a total of 1511 adults and 43 larvae in three families as follows: Haliplidae, Dytiscidae and Hydrophilidae. Haliplidae Hydrophilidae Peltodytesmexicanus Wehncke (Figs. 2-4) Anacaenadebilis(Sharp) (Figs. 18, 19) BerosusmexicanusSharp(Figs. 20, 21) Dytiscidae B. styliferHorn (Figs. 22,23,24) CybisterexplanatusLeConte(Figs. 5,6) Cercyonpraetextatus(Say) (Figs. 25) Desmopachria nuijusculusYoung (Figs.7,8)* Enochrusmexicanus Sharp (Figs. 26,27) Hydrovatus sp. E. ochraceus(Melsheimer) (Figs. 28, 29) Hygrotus sp. Hydrochus sp. Laccophilus mexicanus mexicanus Aube ParacvmusmexicanusWooldridge (Figs. 30, 31) (Fig.9, 10, 11) TropistemuscolumbianusBrown,(Figs.32,33) Liodessusuffinis(Say)(Figs. 12, 13) T. lateralis(Fabricius)(Figs.34,35) Neobidessus sp T. tinctusSharp(Figs.36,37) Neoclypeodytes sp. RhantusanisonychusCrotch (Figs. 14, 15) ThermonectusbasillarisHarris(Figs. 16, 17) *Thisisanew recordforMexico,andthesecondrecordsinceitwasdescribedfromGuatemala. The "apancle" was the habitat with the most diversity and greater num- ber of beetles, so it was apparent that in this type of habitat the scavenging hydrophilids found enough food, and the predatory dytiscids found their prey. In the "acalotes" the aquatic beetles were found mainly along the mar- gins where the food was abundant and the water moved slowly; in general, the entomofauna found was moderately diverse and not numerous. Finally, the Coleoptera were most poorly represented in the "lagoons". The Haliplidae were represented by one species of Peltodytes, the Hydrophilidae by 1 1 species, those pertaining to the genera Tropistemus and Enochrus were in greater number; Dytiscidae with 10 species, where Lacco- philus andNeobidessus were the most numerous. The hydrophilids and dytiscids were associated in the same habitat which was characteristically with abundant aquatic vegetation. The haliplid Peltodytes mexicanus Wehncke (Figs. 2-4) was present only in the Canal del Japon, where in general the water was clear and with sparse decaying plants. The results show a list of species where those typical of polluted envi- ronments dominate, that is, the situation of the water body studied, where different types ofpollution have been detected as it is mentioned by Ramos et al (1993). The water in the channels is in hypoxic conditions with high ammonium concentrations, that make obvious the strong degradation of the organic matter. At the same time, the presence of coliform bacteria con- firm the municipal type pollution (Gama y Fernandez, 1993). Vol. 110, No. 5, November& December. 1999 305 In general the scarce diversity found can be attributed to the eco- systems physicochemical characteristics, as shown by the studies con- ducted by Baez y Belmont (1972), Ramos et al (1993), Gama and Fernandez (1993) and Olgufn, 1993). FIGS. 2-4. Male genitalia: Peltodytes mexicanus median lobe, lateral view 2; left paramere, lateral view 3;rightparamere, lateral view4. 306 ENTOMOLOGICALNEWS 8 FIGS.5-13. Male genitalia: Cyoisterexplamitus paramere, lateral view 5; median lobe, lateral view 6. Desmopachriamajusculusdorsal view 7; lateral view 8. Laccophilusmexicanusmexi- canus median lobe, lateral view 9; left paramere, lateral view 10; right paramere, lateral view 11. Liodessusaffinis paramere, lateral view 12; median lobe, lateral view 13. Vol. 110, No. 5, November& December, 1999 307 15 n 17 FIGS. 14-21. Malegenital\n^Rhuttr(isamsonychusparamere, lateral view 14; median lobe, lat- eral view 15. Thermonectusbasillarisparamere. lateral view 16; median lobe,dorsal view 17. Anacaena debilis lateral view 18; dorsal view 19. Berosus mexicanus lateral view 20; dorsal view21. 308 ENTOMOLOGICALNEWS 28 FIGS. 22-29. Male genitalia: Berosus stylifer paramere, lateral view 22, median lobe, dorsal view 23; lateral view 24. Cercyon praetextatus dorsal view 25. Enochrus mexicanus lateral view26;dorsal view27.: Enochrusochraceuslateral view28;dorsal view29. Vol. 110, No. 5, November& December, 1999 309 FIGS 30-37. Male genitalia: Paracymus mexicanus lateral view 30; dorsal view 31. Tropister- nuscolumbianus lateral view 32; dorsal view 33. Tropisternuslateralislateral view 34; dorsal view 35. Tropisternustinctuslateral view 36,dorsal view 37. ENTOMOLOGICALNEWS 31 ACKNOWLEDGMENTS We thank Paul J. Spongier, NMNH Smithsonian Institution, for manuscript revision and forthe identificationofsome specimens as well as data provided to include in this paper. We also thank M. en C. Maria Angela Conconi andGraciela Serrano for their support during the fieldwork. LITERATURECITED Baez, A.P. y Belmont, R. 1972. Algunos aspectos del deterioro del agua en los canales del Lago de Xochimilco. Memoria del Decenio Hidrologico Internacional. Institute de Geologia.5-13. Baez, A.P., R. Belmont. y O. Gonzalez 1975. Modificacion de la calidad de las aguas del Lago de Xochimilco por el uso de aguas negras en su recarga. I Congreso Iberoameri- cano del Medio Ambiente. 1055-1070. Bojorquez, C. L y L.M. Olguin S. 1993. Sintesis de registros sobre la biota reciente de Xochimilco. Primer Seminario Internacional de Investigadores de Xochimilco. Univer- sidad Autonoma Metropolitana, Unidad Xochimilco, Mexico. Campos,J.A.M.yM.A.FernandezA. 1993.EstudioEcologicopreliminardelaentomofau- na acuatica del Sistema Chinampero de San Luis Tlaxialtemanco, Xochimilco. Primer Seminario Internacional de Investigadores de Xochimilco Universidad Autonoma Metro- politana, Unidad Xochimilco, Mexico. GamaF.J.L.yM.A.FernandezA. 1993.Evaluaciondecoliformestotalesencanalesdedos zonas del sistema chinamperode Xochimilco duranteel veranode los anos 1986 y 1988. Primer Seminario Internacional de Investigadores de Xochimilco Universidad Autonoma Metropolitana, Unidad Xochimilco, Mexico. Novelo,R.A.yM.GallegosM. 1988. EstudiodelaFloraylaVegetacionacuaticarelacionada conel sistemadechinampasenel surestedel Vallede Mexico. Biotica. 13(1-2):121-139. Ramos Espinosa, M.G. et al. 1993. Microbiologia de aguas y lodos utilizados en las chi- nampas. Primer Seminario Internacional de Investigadores de Xochimilco. Universidad Autonoma Metropolitana, Unidad Xochimilco, Mexico. Salcedo, S. V. 1978. Fluctuacion de las poblaciones de la fauna asociada al lirio acuatico (Eichhornia crassipes Kunth) y su relacion con la contaminacion en el Lago de Xochi- milco. Tesis, Facultad de Ciencias, Universidad Nacional Autonomade Mexico. 60 pp. TamayodeHam,L.M.,C.ValverdeyA.G.Aguilar. 1981. Desigualdadsocial enlas3prin- cipales areas metropolitanas, 1980. Carta III.3.6., Atlas Nacional de Mexicojnstituto de UNAM. Geografia, Young,F. 1985. Akey totheamerican speciesdeHydrocanthusSay withdescriptionsofnew taxa (Coleoptera:Noteridae). Proc. Acad. Nat. Sci. Phila. 137: 90-98.

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