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JOSEPH T. SPRINGER, Department of Biology, University of Nebraska at Kearney, Kearney,. Nebraska 68849-1140 USA. Using radio telemetry data to estimate.
HOME RANGE RELOCATIONS

SIZE

ESTIMATES

BASED

ON

NUMBER

OF

JOSEPH T. SPRINGER, Department of Biology, University of Nebraska at Kearney, Kearney, Nebraska 68849-1140 USA Abstract: Regardless of how animal location data are obtained, using such data to delineate and measure home range sizes has posed some problems: the kind of locations that should be included, how the home range should be delineated, and the number of relocations needed to make useful estimates. Randomly generated points were plotted within a known area to provide a table of correction factors to be used for home range size estimates. Over 50% of the entire home range is included after plotting only 12 locations, yet 100 locations account for a little less than 90% of the home range. Using the correction factors with as few as 3 independent locations (with the minimum area method) a useful estimate of home range size and shape can be found. Key words: area estimates, delineation, home range, minimum area method, point method. Springer, J. T. 2003. Home range size estimates base on number of relocations. Occasional Wildlife Management Papers, Biology Department, University of Nebraska at Kearney 14:1-12.

Using radio telemetry data to estimate home range sizes of different wildlife species has been done since the 1960’s (Sanderson 1966). Most researchers have come to realize that the exact location of an animal’s home range and how large it is are parameters difficult to determine due to intrinsic errors in data collection (Springer 1979) and the somewhat subjective manner in which the data are analyzed (Laundré and Keller 1984). Problems associated with error in radio telemetry data collection have been addressed elsewhere (e.g. Cederlund et al. 1979; Springer 1979; Hupp and Ratti 1983; Lee et al. 1985; Saltz and Alkon 1985; White and Garrott 1986,1990; Samuel and Kenow 1992). Parameters of concern in home range data analysis were outlined by Laundré and Keller (1984). They listed 3: methods by which data were collected (many times over a period of several hours versus once or twice a day); how home range boundaries are

delineated; and determining how large a sample size is needed to adequately delineate an animal’s home range. Sample size is the parameter that this paper will address primarily, although all 3 aspects will be discussed. My own interest in the subject of home range is the result of studying coyote home ranges using radio triangulation (Springer 1977, 1979, 1982) as well as live–trap studies of small mammals in prairie habitats (Springer and Schramm 1972; Springer 1988a, 1988b). Odum and Kuenzler (1955) recognized that when plotting location data in an effort to delineate a home range, an area observation (AO) curve will result. That is, calculated sizes of home ranges tend to increase asymptotically as the number of locations increases (Springer 1982). Laundré and Keller (1984) felt that an adequate sample size was reached when the AO curve approached an asymptote. In this paper, I will show that the asymptote itself is the true home range size. I will also show x

Occasional Wildlife Management Papers

how to achieve better estimates of the home range size, even with a small data base. Burt (1943) defined home range as everywhere an animal travels in carrying out its normal activities. Movements by an animal within its home range will tend to be random. A predator cannot know where the next prey item will be beyond some general vicinity included within the predator’s home range. Herbivores might move about in search of food more deliberately, but much research has shown that movement itself has been selected for so that resources do not get overly depleted. Furthermore, herbivores need to remain aware of predators and cannot stay long in a single place. METHODS My investigation into home range size estimation began with the graphing of areas of known size and with different shapes as simulated home ranges. The shapes used were squares, triangles, and ellipses. Ten of the squares measured 25 in2, and 15 squares measured 100 in2. All other shapes measured 100 in2. All computer work was done on a Macintosh™ LC with System7.01 (® Apple™ Computer Corporation). This system was needed so that several applications could be run simultaneously, allowing me to change among them rapidly and effortlessly. Under System6.07 it would have been possible using the Multifinder (® Apple™ Computer Corporation), but there were frequent system crashes. A total of 100 randomly generated binomial coordinates was produced for each simulated home range. Three different methods were used to generate coordinates: random numbers from a Casio™ pocket calculator, random numbers generated by

Springer • Estimating home range size

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Microsoft® Works version 2.00 e spreadsheet (® Microsoft Corporation), and random numbers generated by ClarisWorks™ version 1.0v2 spreadsheet (®Claris™ Corporation). All coordinates fell within the graphed area. Coordinates were plotted using MacDraw II version1.1 (®Claris™ Corporation). This program allows precise 2-dimensional measurement of length and angles. The first 3 coordinate pairs were connected by lines to form a triangle, and the area of the triangle was measured. The result was recorded on a Microsoft® Works spreadsheet. As each new pair of coordinates was plotted, a new area was calculated if the new point fell outside the current delineation. If not, the same area was recorded for the new point as was recorded for the previous point. Where the total area of the home range was 100 in2, each measured area represented the percentage of the total area. Where the total area of the home range was 25 in2, measured areas were recorded in true size, but also as a percentage of the total area. Areas versus location numbers were averaged, standard deviations and standard errors were calculated for all data on the Microsoft Works spreadsheet. Although Microsoft Works spreadsheets will produce graphs automatically from data such as these, the graphs are too coarse. The data were therefore plotted manually using the MacDraw II program. To show the adjusted home range size based on a given number of plotted locations, a convex polygon was plotted around the outermost points. This polygon was copied and inserted into a SuperPaint 2.0a (®Silicon Beach Software Inc.). MacDraw allows for resizing by dragging object handles, but one cannot simply type in a resizing factor. SuperPaint does allow

Occasional Wildlife Management Papers

Springer • Estimating home range size

Table 1. Percentage of home range delineated by a convex polygon, depending on the number (N) of locations used so far. Standard Error (SE) based on 45 polygons. N

Area

SE

N

Area

SE

N

Area

SE

1

XXX

XXX

35

77.37

0.956

69

85.70

0.708

2

XXX

XXX

36

77.71

0.972

70

85.83

0.705

3

8.510

1.029

37

78.13

0.970

71

85.99

0.692

4

14.59

1.218

38

78.66

0.912

72

86.16

0.687

5

21.56

1.424

39

78.97

0.901

73

86.36

0.670

6

27.06

1.386

40

79.49

0.824

74

86.47

0.664

7

32.42

1.427

41

79.82

0.800

75

86.63

0.649

8

37.93

1.576

42

80.11

0.792

76

86.84

0.646

9

41.67

1.614

43

80.41

0.779

77

87.02

0.645

10

45.13

1.416

44

80.62

0.787

78

87.12

0.652

11

48.06

1.404

45

80.81

0.775

79

87.36

0.615

12

50.85

1.377

46

81.15

0.785

80

87.49

0.612

13

53.77

1.387

47

81.41

0.795

81

87.61

0.604

14

56.40

1.438

48

81.82

0.760

82

87.74

0.602

15

58.55

1.461

49

82.12

0.774

83

87.82

0.609

16

60.18

1.380

50

82.40

0.781

84

87.95

0.601

17

61.88

1.416

51

82.57

0.773

85

88.08

0.593

18

63.06

1.360

52

82.72

0.785

86

88.17

0.573

19

64.35

1.234

53

82.83

0.776

87

88.23

0.561

20

65.52

1.223

54

82.96

0.788

88

88.32

0.553

21

66.82

1.215

55

83.10

0.784

89

88.36

0.550

22

67.70

1.241

56

83.19

0.793

90

88.43

0.553

23

68.62

1.214

57

83.40

0.782

91

88.55

0.552

24

69.41

1.233

58

83.58

0.793

92

88.66

0.535

25

70.31

1.290

59

83.92

0.802

93

88.75

0.527

26

71.15

1.248

60

84.11

0.791

94

88.87

0.526

27

72.00

1.172

61

84.37

0.799

95

88.93

0.521

28

72.73

1.167

62

84.49

0.802

96

89.03

0.524

29

73.49

1.179

63

84.66

0.796

97

89.13

0.496

30

74.14

1.119

64

84.90

0.772

98

89.22

0.494

31

74.91

1.045

65

85.04

0.761

99

89.29

0.496

32

75.76

0.998

66

85.24

0.749

100

89.42

0.474

33

76.48

1.004

67

85.37

0.721

34

77.14

0.975

68

85.51

0.719

3

Occasional Wildlife Management Papers

Springer • Estimating home range size

100%

90%

80%

70%

Average

60%

Percentage 50%

of Total Area

40%

30%

20%

10%

0% 0

10

20

30

40

50

60

70

80

90

100

Number of Relocations

Fig. 1. Percentage of the total home range delineated as a function of the number of relocations. The horizontal marks indicate the percentages. Vertical marks indicate + SE.

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Occasional Wildlife Management Papers

precise resizing of shapes, and each home range polygon was increased by the appropriate factor. The resized polygon was copied and centered on the original MacDraw home range file. RESULTS The home range areas versus number of locations plotted were averaged and are shown in Table 1. Since ≤3 points are required to form a polygon, no area or standard error are shown for N = 1 or 2. These results are also shown graphically in Fig. 1, clearly illustrating the asymptotic nature of the curve. The asymptote at the upper limit is 100%. DISCUSSION Methods of Data Collection Laundré and Keller (1984) compared several studies of coyote home ranges, identifying different methods that have been used to collect radio telemetry data. The “Sequential Method” involved finding a location at regular time intervals over a period of 6 to 24 straight hours. The “Point Method” involved finding a location only once or twice a day. Anderson (1982) pointed out that the degree of statistical independence of these 2 methods differs substantially. Dunn and Gipson (1977) had already shown that the sequential method would produce locations that were clearly not independent. Swihart and Slade (1985) showed how to test for independence using the Schoener (1981) ratio of t2/r2, where t = mean distance between successive locations and r = mean distance from the center of activity. The amount of time needed between successive locations would be found using a nonsignificant one-tailed test of the t2/r2 ratio (P >.25), where the null hypothesis is t2/r2 = 2.0. This was about 4.5 h for their

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work on cotton rats (Sigmodon hispidus). Swihart and Slade (1986) justified their choice of P >.25. In general, then, it would be safe to assume that locations obtained by the point method are independent. Exceptions would be when animals repeated are found at the same place: den site, nest site, roost site, water hole, salt lick, etc. When plotting such locations in order to delineate a home range, each should be counted as a single relocation instance regardless of how many times the animal was found there. Since it is a basic assumption in home range analysis that successive locations of an animal must be independent (Hayne 1949), the points plotted in this study are not comparable to those obtained by the sequential method. These randomly selected points are independent of each other, and are therefore comparable to a properly conducted point method. Delineation of Boundaries Another problem with data analysis is the matter of delineating home range boundaries. Laundré and Keller (1984) pointed out (with regard to coyotes) that the array of location data can be assessed several ways. One method has been Hayne’s (1949) ellipse method. This establishes a long and a short diameter, and creates an ellipse that encompasses most location points. Since it does not include all points, and since it has a fixed shape (the ellipse) that may or may not include important habitats that the animal uses, its primary value is in estimating home range size. Another failing in this method would be not showing territorial boundaries that could be shown if other methods were used. This method yields size estimates that may be larger than or smaller than estimates based on the other methods (Laundré and Keller 1984). That does not necessarily

Occasional Wildlife Management Papers

make it less accurate than other methods, but it does make comparison to results from other methods difficult. The most widely used method to delineate home ranges has been called the minimum area method or convex-polygon method, originally described by Mohr (1947), who did not name it. In this method, the outermost locations are connected by a convex polygon, and everything within the polygon is considered to be the animal’s home range. Burt (1943:351) excluded “occasional sallies outside the area, perhaps exploratory in nature.” This is why some researchers have described animals’ home ranges using a modified minimum area method: a certain percentage of location points are excluded. Either all locations are excluded that exceed some specified distance from the next nearest location (Barbaur and Harvey 1965), or the 5% of all locations lying the greatest distance from the center of activity (Bowen 1985, Holzman et al. 1992). In an earlier paper (Springer 1982), I argued that such sallies should not necessarily be excluded, particularly when a home range is comprised of 2 or more core areas separated by some distance. Burt’s (1943) idea was to eliminate the occasional sally outside of the home range from being considered part of the home range. Fig. 2 shows that with randomly distributed locations some locations seem remote such as #57. As the 57th location plotted, it was 2.40 units from the next nearest location, and definitely 1 of the 5% farthest from the center of activity. The modified minimum area method would have eliminated this point from consideration, yet it was within the home range. Other points tend to be clustered indicating an area of significance that might be truly important or might simply be the result of a random distribution of points.

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Fig. 2 also shows what might be considered core areas within a home range: several locations that fall within a short distance of each other. Only 10 of the locations fall outside a “core area” in this example. Locations that are truly independent of all others will tend to form clusters and voids. Simple proximity of points should not be the only measure of a core area or a home range. Burt’s (1943) definition of home range included everywhere an animal travels in carrying out its normal activities. His concept of the occasional sally should apply only to rare travels that are excessively long in distance but short in duration. Otherwise, it seems possible (if not likely) that such travels are in fact within the home range and the area encompassed should be so designated. Sample Size The third aspect of data analysis that has caused concern in respect to home ranges is determining how many relocations are needed to adequately delineate an animal’s home range. Researchers have simply used all the locations they had available within a year or a designated season. Laundré and Keller (1984) tentatively established 100 relocations as the number needed to adequately delineate a home range. As Fig. 1 shows, however, even when 100 locations have been plotted, less than 90% of the true home range has been delineated. Laundré and Keller (1984) discussed the AO curve, and looked for the data to approach an asymptote. They concluded that when the increase in area from one sample to the next was less than 5%, they had reached an adequate sample size. They used the sequential method, so that a single sample included 24 to 48 locations over a 24–hr period. This point was reached with 4 or 5 such samples.

Occasional Wildlife Management Papers

Springer • Estimating home range size

61 79 42 19 76

20

92

4 13

89

80

33

2

81 50 67 21

30 49

72 84

46

69

43

48 98 73

12

36

25

55

39

75

44 62

53

65

9

78

52

22

95 47 15 37

97

90

96 99

8 32

66

18

87

60

63

100

41

74

23

82 94 34 35 (56)

58

16 86

24 27 54 29 59

71

40

70

17 51

88

14

45

5

6

7

1 31

77

10

64

91

3

93

28 26 85

68

38 11

57

Fig. 2. Ellipse #8, after 100 relocations. Points that lie within 1.0 unit (total area is 100 square units) of at least 1 other point have been connected with a convex polygon. Center of true home range =  . Center of estimated home range = 

.

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Occasional Wildlife Management Papers

Springer • Estimating home range size

Table 2. Correction factor for home range size calculation based on number (N) of locations used so far. Data based on 45 polygons. N

Correction

N

Correction

N

Correction

1

XXX

35

1.1369

69

1.0802

2

XXX

36

1.1344

70

1.0794

3

3.4282

37

1.1313

71

1.0784

4

2.6184

38

1.1275

72

1.0773

5

2.1538

39

1.1253

73

1.0761

6

1.9224

40

1.1216

74

1.0754

7

1.7563

41

1.1193

75

1.0744

8

1.6237

42

1.1173

76

1.0731

9

1.5491

43

1.1152

77

1.0720

10

1.4886

44

1.1137

78

1.0714

11

1.4424

45

1.1124

79

1.0699

12

1.4024

46

1.1101

80

1.0691

13

1.3637

47

1.1083

81

1.0684

14

1.3316

48

1.1055

82

1.0676

15

1.3069

49

1.1035

83

1.0671

16

1.2891

50

1.1016

84

1.0663

17

1.2712

51

1.1005

85

1.0655

18

1.2593

52

1.0995

86

1.0650

19

1.2466

53

1.0988

87

1.0646

20

1.2354

54

1.0979

88

1.0641

21

1.2233

55

1.0970

89

1.0638

22

1.2154

56

1.0964

90

1.0634

23

1.2072

57

1.0950

91

1.0627

24

1.2003

58

1.0938

92

1.0620

25

1.1926

59

1.0916

93

1.0615

26

1.1855

60

1.0904

94

1.0608

27

1.1785

61

1.0887

95

1.0604

28

1.1726

62

1.0879

96

1.0598

29

1.1665

63

1.0868

97

1.0592

30

1.1614

64

1.0853

98

1.0587

31

1.1554

65

1.0844

99

1.0583

32

1.1489

66

1.0831

100

1.0575

33

1.1435

67

1.0823

34

1.1386

68

1.0814

8

Occasional Wildlife Management Papers

A

C

Springer • Estimating home range size

B

D

Fig. 3. Triangle #09 showing delineated polygons and adjusted polygons after different numbers of relocations. A = After 10 relocations. B = After 20 relocations. C = After 40 relocations. D = After 70 relocations. Center of true home range =  . Center of estimated home range =  .

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Occasional Wildlife Management Papers

From Table 1, using the point method, the rate of increase drops to less than 5% at the 14th location (an increase from 53.77 square units to 56.40 square units is a 4.9% increase). Yet, only 56.4% of the home range has been delineated. Thus the 5% increase in area is not an adequate point at which to say the home range has been delineated. On the other hand, would 100 locations be enough to fully delineate the home range? Table 1 shows that even after 100 locations have been plotted, the average area delineated is still

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