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Abundance of gulls and other birds at landfills in northern Ohio.

INTRODUCTION

Gulls (Laws spp.) frequently have been reported as a hazard to aircraft (Dahl, 1984; Seubert, 1990; Sherigalin, 1990). Waste disposal sites accepting putrescible wastes (hereafter referred to as landfills) often attract birds, especially gulls (Laws spp.; Kihlman and Larsson, 1974; Burger and Gochfeld, 1983; Horton et al., 1983; Greig et al., 1986; Coulson et al., 1987; Patton, 1988). The Federal Aviation Administration issued Order 5200.5 in 1974 to prohibit landfills within 5000 ft (1.5 km) of runways used by piston-type aircraft and 10,000 ft (3 km) of runways used by turbine-powered aircraft. In 1990 this order was revised (Order 5200.51) to include landfills from 10,000 ft (3 km) to 5 miles (8 km) of runways (Federal Aviation Administration, 1990).

There has been continuing discussion and controversy regarding the minimum distance of landfills from airports. To make informed decisions on landfill sitings and operations with regard to aircraft safety, more information is needed on the extent and pattern of daily bird use (feeding, soaring, loafing) of landfills and the area around landfills (Lake, 1984; McLaren et al., 1984; Risley and Blokpoel, 1984; Southern and Southern, 1984; Forsythe and Austin, 1984). In addition, we know little about the contribution that abundant dependable food at landfills has made to the overall population increases of gulls in many areas of North America (Kadlec and Drury, 1968; Ludwig, 1974; Blokpoel and Tessier, 1986).

Although several studies in Europe have described annual use and seasonal abundance of gulls at landfills (Coulson and Butterfield, 1986; Pons, 1992), there are few quantitative data pertaining to seasonal abundance of gulls at landfills in North America. Patton (1988) provided qualitative data on annual abundance of three gull species at landfills in Florida. However, there are currently no comparative data on annual abundance of gulls at landfills in the northern United States. Therefore, our objective was to quantify annual abundance and population fluctuations of gulls and other birds at three landfills in northern Ohio, all within 30 km of Lake Erie.

STUDY AREA AND METHODS

We conducted the study at three landfills near Lake Erie in northern Ohio. The Erie County landfill, 7 km south of Lake Erie and 17-21 km southeast of herring gull (Laws argentatus) nesting colonies on Sandusky Bay (Belant et al., 1993), averaged 222 metric tons of refuse a day, five days per week. The Ottawa County landfill, 2 km from Lake Erie and 26-30 km northwest of the nesting colonies, averaged 563 metric tons of refuse per day. The Huron County landfill, 30 km from Lake Erie and 35-36 km south of the colonies, averaged 103 metric tons of refuse per day. At each landfill, refuse was spread and compacted throughout the day, then covered with soil at the end of the workday. Each landfill generally had <0.5 ha of exposed refuse on any given day. The highest rates of refuse deposition occurred from May to August (115-362 tons/day); rates were 25-39% lower from January to April.

The number of gulls at the Erie County landfill was estimated, usually twice a day five days per week, at randomly selected times in the morning and afternoon from May 1991 to July 1992. All observations were conducted by experienced personnel who were trained to estimate in similar ways the number of birds present. During each visit, one or two observers used binoculars to count a group of gulls ([less than or equal to]200 individuals). The total population of gulls at the landfill on or within 30 m of the ground was then determined by estimating the number of groups of the given size and multiplying by the group size. We generally conducted total counts when gull populations were <500 individuals. Age and species composition of gulls at the landfill was determined by sampling [greater than or equal to]10% of the estimated population with binoculars throughout the entire landfill. Each sampled bird was identified to species, and by age class based on plumage: adult, subadult (1 to 2 or 3-years-old), or hatching year (<1-year-old; Grant, 1986). All gulls hatched during 1991 were classified as subadults during 1992. The number and height of gulls soaring at three ranges of elevation (31-150 m, 151-300 m, >300 m) were also recorded; elevations were estimated using a range finder. Once the elevation(s) of one or more gulls were known, elevations of other gulls were estimated based upon the known altitude(s) at which gulls were present. When a great difference in soaring altitudes occurred, we often checked our estimates with the range finder. We generally spent 10-30 min during each observation period counting and estimating the population, depending upon the number of gulls present. After completing gull population estimates, these same techniques were used to estimate abundance of all other species, without regard to age classes.

These observation procedures also were used at the Ottawa County and Huron County landfills by the same trained personnel. However, the Ottawa County landfill was checked during the day, at a randomly selected time, once a day, usually three to five days each week from May 1991-July 1992 and the Huron County landfill was checked at a randomly selected time once a day, one to three days each week from dune 1991-July 1992.

Data were analyzed using the General Linear Models Procedure (GLM; SAS Inst., Inc. 1988). If significant (P < 0.05) differences occurred using GLM, Tukey tests were used to determine which means differed.

We recorded 699,350 individuals of 42 species of birds at the three landfills in 958 observation periods (38 species at Erie, 17 at Ottawa, and 21 at Huron; Table 1). Gulls comprised 94.5% of the birds recorded with European starlings [Sturnus vulgaris (5.0%)] and turkey vultures [Cathartes aura (0.3%)] the next most abundant birds. The gulls were primarily of two species, ring-billed [L. delawarensis (74.5%)] and herring (25.5%); great black-backed (L. marinus), glaucous (L. hyperboreus) and laughing (L. atricilla) gulls combined comprised <0.01%.

[TABULAR DATA OMITTED]

The total numbers of gulls varied considerably among landfills and among days and seasons at a landfill. Overall mean numbers of gulls at the Erie County and Ottawa County landfills were six and five times greater, respectively, than the mean number observed at Huron County Landfill (Table 2). There were also differences (P < 0.01) in the monthly mean number of gulls observed at the Erie Count,v (F = 24.01; 14 and 1110 df), Huron County (F = 6.14; 13 and 260 df), and Ottawa County (F = 45.27; 14 and 458 df) landfills. The mean number of gulls per observation during July through January was at least five times the mean number observed during other months (Fig. 1). The number of gulls peaked at all of the landfills in August (>4000 birds), with gulls virtually absent in February.

[TABULAR DATA 2 OMITTED]

Overall, ring-billed gulls were more abundant (P < 0.01) than herring gulls at each of the landfills (F= 35.25-148.74 and 1260-1110 df). However, species composition differed (P < 0.01) at all three landfills among months (F = 4.10-27.45; 1 and 13 or 1 and 14 df). Herring gulls were more abundant than ring-billed gulls from February through June and ring-billed gulls were more abundant than herring gulls from July through January (Fig. 1).

Herring gulls at the landfills from April through December were predominantly adults (Fig. 2). The proportion of subadult herring gulls generally increased during fall and peaked between February and April. Hatching-year herring gulls were first observed during July of both years and generally increased in numbers through December of 1991.

Age composition of ring-billed gulls among landfills was more variable than that of herring gulls. At Erie County, adults were most abundant from August through April whereas subadults were more abundant from May through July in both years (Fig. 3). At Huron County, adults were most abundant from November through January. Except during July 1992, subadults were most abundant between March and August. At Ottawa County landfill, adult ring-billed gulls were more abundant than subadults during all months except May 1991, and April and June 1992. Hatching-year ring-billed gulls were first observed at the landfills curing duly of both years. Their numbers increased through October or November, then declined by December. At Huron County, hatching-year ring-billed gulls were the most prevalent age class during September and October.

Over 98% of the gulls observed at the three landfills were on or within 30 m of the ground during observations. Gulls were observed infrequently (x = one [+ or -] 17 [SD]) soaring at elevations >300 m over the landfills (Table 3). The number of gulls soaring >30 m over a landfill did not differ (F = 0.58; 3 and 954 df; P = 0.63) for the four 2-h periods from 0800-1600 h. However, there was a greater total mean number of gulls <30 m of the ground at the landfills from 1200-1400 h than from 0800-1000 h (F = 4.17; 3 and 954 df; P < 0.01). The number of gulls present during other times of day was similar (Tukey test, P > 0.05; Table 3).
TABLE 3.--Mean number of herring and ring-billed gulls per
observation
period at three landfills by elevation and time of day

                                        Mean number of gulls(a)

Time (h)   No. of obs.  <30 m(b)  31-150 m  151-300 m  >300 m
Total

0800-0959     204         1350      44        <1        0      1394
1000-1159     225         1841      11         8       <1      1862
1200 1359     189         1985       7         2       <1      1994
1400-1600     340         1474      11        14        2      1502
Total         958         1635      18         7        1      1661
(a) Sum of means for the 3 landfills
(b) Includes gulls on the ground




DISCUSSION

Although 42 bird species were observed at the three landfills, four species (ring-billed and herring gulls, European starling, and turkey vulture) comprised 99.8% of the birds recorded. The remaining 38 species were present in low numbers and generally were seen flying over the sites. Gulls, European starlings and turkey vultures have frequently been reported to forage at landfills (Forsythe, 1980; Southern and Southern, 1984; Patton, 1988).

Seasonal variations recorded in numbers, species composition and age composition of gulls appear to be related to nesting activities and migration patterns. The presence of herring gulls at the landfills between April and June was low relative to the large nesting population (3250 pairs in 1992) near Lake Erie and within 36 km of the landfills during that same time of year (Belant et al., 1993). The low mean numbers of herring gulls observed from April to June can be attributed in part to their diet of primarily fish during this time (Belant et al., 1993). The increase in adults and the presence of hatching-year herring gulls at the landfills in July coincided with the onset of fledging at these nesting colonies (Belant et al., 1993).

Fall migration of hatching-year and subadult herring gulls in the Great Lakes region begins in November and peaks during December and January. Spring migration is initiated in late February and lasts until April or May (Moore, 1976). This explains the low numbers of subadult herring gulls observed at the landfills between January and March. Moore (1976) also stated that adult herring gulls within the Great Lakes breeding range are year-round residents. The paucity of adult herring gulls observed at the landfills from January to March may be partially explained by increased numbers of gulls observed near areas of greatest urbanization (e.g., Cleveland, Chicago), which provide larger amounts of putrescible waste (Moore, 1976; Dolbeer and Bernhardt, 1986). Also, the total amount of refuse deposited at the landfills in this study was lowest from January to April. Thus, there likely is a reduced amount of putrescible waste available as food.

The large numbers of ring-billed gulls at the landfills between July and January appear related to their regional breeding and wintering populations, and postbreeding dispersal (Southern, 1974; Dolbeer and Bernhardt, 1986; Blokpoel and Scharf, 1991; Blokpoel and Tessier, 1991). Premigratory movements of ring-billed gulls from the Great Lakes begin in July, with migration requiring up to five months (Southern, 1974). Many of these birds congregate along the south shore of the western basin of Lake Erie, which frequently supports the largest early-winter population of ring-billed gulls in North America (Southern, 1974). Although a few migrant ring-billed gulls return to Great Lakes breeding areas in late March, most return during May and June (Southern, 1974). This corresponds with their reoccurrence at the landfills in May.

The nearest nesting population of ring-billed gulls to the landfills is 100 km west, near Toledo (Scharf, 1978). The incubation period of ring-billed gulls in the southern Great Lakes region occurs from late April through May (Ryder, 1975; Fetterolf, 1979, 1983), with most chicks hatching between late-May and mid-June (Fetterolf, 1983). This corresponds with our first observations of hatching-year birds during July.

Changes in waste management practices can influence gull use at landfills (Patton, 1988). As landfills in this study appeared to be operated similarly, we believe the greater number of gulls observed at the Erie and Ottawa County Landfills compared to the Huron County landfill was a function of their closer proximity to Lake Erie. Because large numbers of herring and ring-billed gulls nest, stage and winter on or adjacent to the Great Lakes (Southern, 1974; Dolbeer et al., 1990; Blokpoel and Scharf, 1991), greater numbers of gulls would be expected at landfills that are closer to these bodies of water.

Because of political boundaries, coastal cities and counties may be unable to locate landfills far enough inland to reduce substantially their use by gulls. For example, herring gulls have been reported to fly 60 km daily to use landfills (Kilpi, 1984). However, at the Huron County Landfill, located more than four times farther inland (30 km) than the Erie and Ottawa County landfills (7 and 2 km, respectively), we observed 80-83% fewer gulls overall. In addition, concurrent monitoring of radio-tagged nesting herring gulls from the Sandusky Bay colonies suggest minimal use of the Huron County Landfill during incubation and chick-rearing (Belant et al., 1993). Although part of the relative scarcity of gulls observed at the Huron County landfill is likely due to smaller quantities of refuse deposited, increasing the distance of landfills from nesting and staging areas should reduce their use by gulls. Other factors such as habitat and waste management practices, and harassment/control techniques need to be considered during the planning and operating of landfills to further reduce their attractiveness to gulls.

Mixed solid waste landfills can attract large number of birds, especially gulls. However, species composition and seasonal abundance can vary considerably, even among similarly operated landfills in close proximity to each other. Therefore, to adequately assess the use of landfills by gulls and other birds, and the efficacy of management practices to keep these birds away from landfills, studies lasting 21 year are required. Furthermore, bird abundance and seasonal dynamics at one landfill cannot necessarily be applied to other landfills, even landfills in close proximity. The monthly and seasonal patterns of local and regional bird populations in relation to location and management practices of landfills must be defined.

Acknowledgments.--We thank personnel at the Erie County, Huron County, and Ottawa County landfills for access to the landfills and providing refuse deposition data; G. E. Bernhardt, S. K Ickes, R. C. Kozar, K D. Madaras, M. R. Rutger, D. A. Williams, J. A. Shieldcastle and P. P. Woronecki assisted with observations. H. Blokpoel provided helpful comments for manuscript improvement. Sponsorship and funds for this research were provided by the Federal Aviation Administration, Office of Airports Safety and Standards, Washington, D.C. and Airports Division, Airport Technology Branch, FAA Technical Center, Atlantic City International Airport, New Jersey.

[Figure 1 ILLUSTRATION OMITTED]

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Author:Belant, Jerrold L.; Seamans, Thomas W.; Gabrey, Steven W.; Dolbeer, Richard A.
Publication:The American Midland Naturalist
Date:Jul 1, 1995
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