Sampling Riparian Arthropods With Flight-interception Bottle Traps

Creating or restoring habitat for insectivo rous birds requires producing an adequate food supply of arthropods (Williams 1993). Employ ing traps to estimate arthropod abundances may be easier and less disturbing to wildlife than sampling (e.g., sweeping) vegetation. My objec tive is to develop an easy and repeatable method for sampling arthropods in habitat created for ri parian wildlife, in particular the southwestern willow flycatcher Empidonax traillii (Audubon) ssp. extimus Phillips. This endangered bird eats a variety of insects and spiders (Wiesenborn & Heydon 2007). I compared relative numbers of arthropods in taxa captured by flight-intercep tion bottle traps and collected from branches on narrow-leaved willows (Salix exigua Nutt.) and Fremont cottonwoods (Populus fremontii S. Wat son) planted for wildlife. The study site (33?41'N, 114?32,W; elevation 81 m) is a 21.4-ha farm field, planted with shrubs and trees during Mar 2007, near the Colorado River in Riverside County, California, 12 km northeast of Blythe. I sampled arthropods within two 1.0-ha plots of S. exigua shrubs, 2-3 m tall, and two 0.6-ha plots of P. fremontii trees, 4-5 m tall. Willows, but not cottonwoods, were flowering or seeding. Alfalfa (Medicago sativa L.) grows as an understory throughout the site. The site is sur rounded by agriculture. I trapped arthropods in each plot with an aerial-interception trap made of four 2-liter, clear-plastic, carbonated-beverage bottles (Car rel 2002). Bottles were placed together and hung by their caps from a plywood board held 1.5 m aboveground by 2 steel rods. Spiders and insects flew or walked through outward-facing, rectangular openings cut into the bottles and fell into soapy water. Traps were placed near the centers of plots and did not contact branches. Arthropods were trapped during 15 19 May, 4-9 Jun, 8-12 Jul, and 10-13 Aug 2008. Air temperatures measured at the start and end of each trapping period averaged 29?C dur ing 0740-0845 PDT and 35?C during 1510-1821 PDT. Insects and spiders were collected from plants concurrent with trapping. Sampled plants were randomly selected along rows ex tending 40 m north and south from each trap. I collected arthropods by sweeping a 1.4-m long, fine-mesh net (field insect-cage cover, Bioquip, Gardena, CA), held open with a 0.8-m diameter metal hoop, over a 1-m long, arbitrarily-se lected branch. I constricted the net around the base of the branch and fumigated the enclosed arthropods with 43 g of aerosol insecticide (0.2% tetramethrin + 0.4% permethrin, Hot Shot Fogger?, United Industries, St. Louis, MO). I shook the arthropods into a 40-dram plastic container, attached by a rubber band to a cut corner of the net, and cut and weighed (?2 g) the sampled branch with a 300-g capacity spring scale. Arthropods were collected from 1 branch each on a different shrub or tree in each plot on 8 dates (16 & 27 May, 9 & 10 Jun, 7 & 8 Jul, and 11 & 12 Aug 2008). Spiders and insects were identified to order. Insects in Hemiptera and Diptera were identi fied to suborder, and bees (Apoidea) were distin guished from other Hymenoptera. Numbers of arthropods in traps were divided by numbers of days (n = 3-5) during each trapping period. Numbers of arthropods on branches in each plot were summed across dates in each month and divided by total masses of sampled branches. Adjusted numbers of arthropods from traps and branches were paired by month, producing 8 pairs (2 plots x 4 months) in each plant species. Associations between adjusted numbers of ar thropods from traps and branches across taxa on each plant species and within taxa on both plant species were measured with Spearman rank correlation coefficients. I calculated coeffi cients with SYSTAT (version 10.2, Richmond, CA) and their test statistics (Neter et al. 1996). Coefficients within taxa were calculated only if arthropods were taken from traps and branches. Flight-interception traps within willows cap tured 176 arthropods, and those within cotton woods captured 221 arthropods. An average of 6.2 insects or spiders was captured per trap per day. Trapped arthropods (Fig. 1) were mostly Araneae (spiders) followed by Thysanoptera. I collected 155 arthropods from 16 willow branches totaling 4.7 kg and 205 arthropods from 16 cottonwood branches totaling 4.5 kg. Most arthropods col lected from branches (Fig. 1) were Araneae fol lowed by Homoptera and Heteroptera. Most ho mopterans on branches were Cicadellidae fol lowed by Aphididae. Relative numbers of arthropods in taxa cap tured by traps were similar to those collected on branches. Arthropod abundances across taxa (n = 15) from traps and branches were positively asso ciated within plots of S. exigua (rs = 0.42, t* = 5.07, P < 0.001, n = 120) and P. fremontii (rs = 0.33, t* = 3.82, P < 0.001, n = 120). Within taxa, numbers of