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<br />. ~ r;t-?1. 0 h .;: I (\ .... (\ t ce,,' \.. <br /> <br />~ Pergamon <br /> <br />'-{'1 ~1 <br /> <br />Environrncmal Toxicology and Cherni\lrY. Vol. IJ. No.2. pp. 267-279.1994 <br />Copyright @ 1994 SETAC <br />Primed in Ihc USA <br />0730- 7268/94 S6.00 + .00 <br /> <br />EFFECTS OF BACILLUS THURINGIENSIS VAR. ISRAELENSIS ON <br />NONTARGET BENTHIC ORGANISMS IN A LENTIC HABITAT AND <br />FACTORS AFFECTING THE EFFICACY OF THE LARVICIDE <br /> <br />COLETTE S. CHARBONNEAU, *t RONALD D. DROBNEYt and CHARLES F. RABEN It <br />tThe School of Natural Resources, University of Missouri, Columbia, Missouri 65211 tU.S. Fish and Wildlife Service, <br />Missouri Cooperative Fish and Wildlife Research Unit, University of Missouri, Columbia, Missouri 65211 <br /> <br />(Received I December 1992; Accepted 2 June 1993) <br /> <br />Abstract - Field and laboratory studies were conducted to determine the effects of Bacillus thuringiensis var. israelensis (Veclobac. <br />G@) on waterfowl macroinvertebrate food resources at the Minnesota Valley National Wildlife Refuge, Bloomington, Minne- <br />sota. Laboratory toxicity tests were conducted to evaluate the influence of environmental variables (e.g., temperature and depth). <br />The EC50 was 0.20 ppm for Chironomus riparius. Fic:ld studies evaluated the effects of three applications at 5.6 kg/ha on ben- <br />thic communities during the spring and summer of 1989, and three experiments with one application of 5.6 kg/ha and 28.1 kg/ha <br />during the spring and summer of 1990. Benthic invertebrates were sampled before each application of Vectobac-G and at 48 h <br />after application. There was no reduction of the major taxa found in the ponds that could be accounted for by the treatments. <br />However, results from laboratory toxicity tests conducted with field-collecled Chironomidae indicated that these organisms were <br />...Jlffected al <; 6 and 28 I h/ha. Further toxicity tests using Ch;;imomus riparius determined that various environmental vari- <br />ables influenced the efficacy of VeclObaC-G, including temperature, larval instar, water depth, and water surface area coverage <br />by macrophytes. This study indicates that chironomids (a major waterfowl food source) are adversely affected by Vectobac-G <br />under a controlled laboratory situation; however, environmental factors reduce the efficacy of the larvicide in the field. <br /> <br />Keywords- Vectobac-Gl! <br /> <br />Toxicity tests <br /> <br />Chironomidae <br /> <br />INTRODUCTION <br />Bacillus thuringiensis var. israelensis (Bti), serotype H-14, <br />is a potent bacterial larvicide used in a variety of habitats <br />[1-10). Toxicity is limited to nematocerous dipteran families, <br />including mosquitoes (Culicidae) [1-10), and blacktlies (Sim- <br />uliidae) [4, II-IS), in which the efficacy depends on feeding <br />habits, physiology, and habitat of the insect. Besides these <br />target organisms, other dipteran families may also be im- <br />pacted. For example, 16 species of aquatic, benthic-dwelling <br />Chironomidae are known to be susceptible to the delta-endo- <br />toxin of Bti [4,16-22). Chironomidae are of special concern <br />because of their ubiquitous distribution in aquatic systems <br />and their importance as a major link in food webs contain- <br />ing fish and waterfowl. The efficacy of the larvicide and po- <br />tential impact on nontarget organisms appear to be related <br />to environmental conditions within the treated habitat. Water <br />temperature (23), water depth [24,25], aquatic vegetation <br />[26,27], and dissolved and suspended organic matter [28-30] <br />appear to be especially important, and other factors includ" <br />ing the size or age of the insect [2,31-32] also influence the <br />efficacy of Bti. <br />There is a proposal to apply Bti routinely to areas of the <br />Minnesota Valley National Wildlife Refuge ("Refuge; in the <br />metropolitan area of Minneapolis-St. Paul, by the Metro- <br />politan Mosquito Control District ("District"). Because the <br /> <br />.To whom correspondence mav be addressed. <br />The current address of C.S. Cha"rbonneau is U.S. Fish and Wild- <br />life Service, Columbia Field Office. 608 East Cherry SI., Room 200. <br />Columbia, MO 65201. <br /> <br />Mosquitoes <br /> <br />Efficacy <br /> <br />Refuge is an important breeding area for three species of <br />ducks, including mallard (Anas platyrhynchos), blue-winged <br />teal (A. discors), and wood duck (Aix sponsa), all of which <br />rely on invertebrate food during part of their life cycles, <br />the question was raised whether hens and their broods <br />would have an adequate food supply after applications of <br />Vectobac-G@ . <br />The goal of this study was to examine effects of Bti ap- <br />plications on waterfowl invertebrate food resources at the <br />Refuge. Specific objectives were to determine the effect of <br />Vectobac-G on benthic invertebrates in an aquatic wetland <br />community and to conduct laboratory toxicity tests to eval- <br />uate the conditions under which environmental factors influ- <br />enced toxicity. <br /> <br />MATERIALS AND METHODS <br /> <br />Field tests <br /> <br />Study Area. The Refuge currently encompasses about. <br />3,333 ha. A portion of its boundaries occur within the Min- <br />neapolis-SI. Paul metropolitan area. Field studies were con. <br />ducted in the Little Bass Pond (LBP) and Minnow Pond <br />(MP), both located in the Bass Ponds Environmental Study <br />Area of the Refuge. LBP is a O.4-ha, type 4 wetland (inland <br />deep fresh marsh), as classified by Cowardin et al. [33], and <br />MP is a O.I-ha, type 5 wetland (inland open fresh water). The <br />LBP contained emergent vegetation, including great bulrush <br />(Scirpus validus); narrow.leaved cattail (Typha angustifolia); <br />broadleaf cattail (T. lotifolia); and submersed or floating <br />aquatic vegetation consisting of coontail (Ceratophyllum <br />demersum), elodea (Elodea canadensis), stonewort (Chara <br /> <br />267 <br />