Appendix 3

Answers to “Analyzing Ecology” and “Graphing the Data”

A-11

Chapter 1

Analyzing Ecology

Insect abundance on uncaged trees:

  Mean = 3.0

  Variance = 1.0

Chapter 2

Analyzing Ecology

Standard deviation of the mean = 7.0

Standard error of the mean = 3.1

Graphing the Data

Based on the data, the Q10 between 5°C and 15°C is 2.0.

Chapter 3

Analyzing Ecology

Each of the three soil treatments would be considered a categorical variable because they fall into distinct categories. In contrast, if we had considered three treatments such as 100 percent sand, 70 percent sand, and 40 percent sand, then we would have a continuous variable.

Graphing the Data

Chapter 4

Analyzing Ecology

Graphing the Data

The data represent a correlation. The data also represent causation because increased time allows the birds to collect a greater number of earthworms.

Chapter 5

Analyzing Ecology

Given the following equation:

  Temperature = –1.2 × Latitude + 43

At a latitude of 10 degrees, the mean January temperature is

  Temperature = –1.2 × 10 + 43 = 31°C

At a latitude of 20 degrees, the mean January temperature is

  Temperature = –1.2 × 20 + 43 = 19°C

At a latitude of 30 degrees, the mean January temperature is

  Temperature = –1.2 × 30 + 43 = 7°C

A-12

Graphing the Data

Chapter 6

Analyzing Ecology

  Mean = 15.6

  Median = 17

  Mode = 17

The values differ because the mean measures the central tendency of the data by calculating the average value while the median ranks the data and uses the middle data point; the mode uses the commonly occurring value.

Graphing the Data

Chapter 7

Analyzing Ecology

To determine the response to selection (R), we multiply the strength of selection on a trait (S) and the heritability of the trait (h2).

S h2 R
0.5 0.7 0.35
1 0.7 0.7
1.5 0.7 1.05
2 0.9 1.8
2 0.6 1.2
2 0.3 0.6
2 0 0

Based on the above results, the responses to selection (R) are greater whenever the strength of selection increases or the heritability of the trait increases.

Graphing the Data

We can determine the mean beak size before or after selection by multiplying each beak depth by its frequency and then taking the sum of these products.

  Mean beak size before selection = 11.3 mm

  Mean beak size after selection = 12.5 mm

Because the mean beak depth has increased after selection, this set of data is an example of directional selection.

Chapter 8

Analyzing Ecology

For Population A:

For Population B:

A-13

For Population C:

Because of the higher coefficient of determination, Population A provides the strongest confidence that there is a negative relationship between seed size and seed number.

Graphing the Data

Lizards that produce a larger number of eggs do so by producing smaller eggs.

Chapter 9

Analyzing Ecology

If there are four males and five females:

  Average male fitness = 10 gene copies ÷ 4 males

   = 2.5 gene copies/male

  Average female fitness = 10 gene copies ÷ 5 females

   = 2.0 gene copies/female

If there are six males and five females:

  Average male fitness = 10 gene copies ÷ 6 males

   = 1.7 gene copies/male

  Average female fitness = 10 gene copies ÷ 5 females

   = 2.0 gene copies/female

Over the long term, if either sex becomes rare, it will have higher fitness, which will subsequently cause it to become more common. Over the long term, this process will favor an equal sex ratio.

Graphing the Data

Whenever one of the sexes becomes rare, it subsequently becomes common. Over the long term, we tend toward an equal sex ratio.

Chapter 10

Analyzing Ecology

If the fitness that primary helpers give to their parents declines to 1.0, their indirect fitness declines to 0.32 and their inclusive fitness declines to 0.73. Under this scenario, the secondary helper strategy would be the most favored by natural selection.

YEAR 1 YEAR 2
MALE ROLE B1 r1 INDIRECT FITNESS B2 r2 Psm DIRECT FITNESS INCLUSIVE FITNESS
PRIMARY HELPER 1.0 × 0.32 = 0.32 2.5 × 0.5 × 0.32 = 0.41 0.32 + 0.41 = 0.73
SECONDARY HELPER 1.3 × 0.00 = 0.00 2.5 × 0.5 × 0.67 = 0.84 0.00 + 0.84 = 0.84
DELAYER 0.0 × 0.00 = 0.00 2.5 × 0.5 × 0.23 = 0.29 0.00 + 0.29 = 0.29

Graphing the Data

SCHOOL SIZE
TRIAL 3 5 10 15 20
1 0.9 0.7 0.4 0.4 0.1
2 0.8 0.8 0.5 0.5 0.1
3 0.7 0.9 0.6 0.3 0.2
4 1.1 0.6 0.8 0.2 0.3
5 1.0 1.0 0.7 0.6 0.3
MEAN 0.90 0.80 0.60 0.40 0.20
STANDARD DEVIATION 0.16 0.16 0.16 0.16 0.10

As the size of the prey school increases, there is a decline in the number of times a predator approaches.

Chapter 11

Analyzing Ecology

Given the equation:

  N = M × C ÷ R

  N = 20 × 48 ÷ 24

  N = 40

Because these 40 crayfish were found in a 300 m2 stretch of a stream, the density of the crayfish can be calculated as:

  40 crayfish ÷ 300 m2 = 0.13 crayfish/m2

A-14

Graphing the Data

Once four individuals have arrived at the high-quality patch, the next individual to arrive would receive a larger per capita benefit by moving to the low-quality patch.

If there are 12 individuals, all individuals would gain the highest per capita benefit if 8 individuals remained in the high-quality patch and 4 individuals moved to the low-quality patch.


Chapter 12

Analyzing Ecology

AGE SURVIVAL RATE SURVIVORSHIP FECUNDITY    
(x) (nx) (lx) (bx) (lx)×(bx) (x)×(lx)×(bx)
0 530 1.000 0.05 0.05 0.00
1 134 0.253 1.28 0.32 0.32
2 56 0.116 2.28 0.26 0.53
3 39 0.089 2.28 0.20 0.61
4 23 0.058 2.28 0.13 0.53
5 12 0.039 2.28 0.09 0.44
6 5 0.025 2.28 0.06 0.34
7 2 0.022 2.28 0.05 0.35

Graphing the Data



Chapter 13

Analyzing Ecology

The population sizes from year 1 through 15 are as follows:

YEAR CHANGE IN POPULATION SIZE TOTAL POPULATION SIZE
1   10.0
2   10.0   20.0
3   19.8   39.8
4   35.0   74.8
5   49.5 124.4
6   34.4 158.8
7 –42.6 116.2
8 –75.2   41.0
9  –7.3   33.7
10   21.9   55.6
11   40.5   96.1
12   47.0 143.1
13    6.2 149.2
14 –70.7   78.5
15 –42.5   36.0

Given that the product rT = 1.1 × 1 = 1.1, we would expect the population will experience damped oscillations, which you can confirm from the graphed data.

Graphing the Data

PROPORTION OF OCCUPIED PATCHES PROBABILITY OF EXTINCTION RATE OF EXTINCTION PROBABILITY OF COLONIZATION RATE OF COLONIZATION
p e e × p c (c × p) × 1 − p
0.1 0.25 0.025 0.5 0.045
0.2 0.25 0.050 0.5 0.080
0.3 0.25 0.075 0.5 0.105
0.4 0.25 0.100 0.5 0.120
0.5 0.25 0.125 0.5 0.125
0.6 0.25 0.150 0.5 0.120
0.7 0.25 0.175 0.5 0.105
0.8 0.25 0.200 0.5 0.080
0.9 0.25 0.225 0.5 0.045
1 0.25 0.250 0.5 0

A-15

For these data, the rates of extinction and colonization come to equilibrium where the two lines meet when the proportion of occupied patches is 0.5. This can also be calculated using the equilibrium equation:

Chapter 14

Analyzing Ecology

When we repeatedly sample the two distributions, we can conclude that they are significantly different if the two means do not overlap 95 percent of the time. This would happen when the two distributions are approximately two standard deviations apart from each other.

Graphing the Data

Because the number of caribou killed per wolf gradually slows as caribou density increases, the wolves most closely follow a type II functional response.

Chapter 15

Analyzing Ecology

To calculate the t-value:

To calculate the degrees of freedom:

  degrees of freedom = 8 + 8 − 2 = 14

Based on the statistical table for a t-test (see the Statistical Tables appendix), the critical value of t for 14 degrees of freedom and an alpha value of 0.05 is 2.1. Since our t-value exceeds the critical value from the table, we conclude that the two means are significantly different.

Graphing the Data

Based on the graph, one can see that the peak density of acorns is followed 1 year later by the peak density of chipmunks and 2 years later by the peak density of ticks.

Chapter 16

Analyzing Ecology

Use the following equation for a Chi-square test:

Degrees of freedom = (number of observed categories − 1) = (2 − 1) = 1

Using the Chi-square table in the Statistical Tables appendix, we can compare our calculated value (0.8) to the critical Chi-square value when we have 1 degree of freedom and an alpha value of 0.05. The critical Chi-square value is 3.841, which exceeds our Chi-square value. Thus, we conclude that our observed distribution of mice in the bare zone and in the grass is not significantly different from an equal distribution.

A-16

Graphing the Data

Based on this graph, the predicted outcome of this competition is that either of the two species can win, but it depends on the initial number of each species.

Chapter 17

Analyzing Ecology

  U = R1 − (n1 (n1 + 1) ÷ 2)

  U = 40.5 − (8 (8 + 1) ÷ 2)

  U = 40.5 − (72 ÷ 2)

  U = 4.5

Using this value for R1, we can now calculate z:

When we look up the critical value of z in the Statistical Tables appendix, we use the absolute value of z. As a result, both R1 and R2 provide us with values of z that have the same absolute value.

Graphing the Data

NUMBER OF FUNGAL SPECIES MEANPHOSPHORUS REMAINING INTHE SOI (mg p/kg soil) STANDARD ERROR
0 16.0 0.6
2 11.0 0.6
4 9.0 0.6
8 5.0 0.6
14 4.0 0.6

Chapter 18

Analyzing Ecology

Simpson’s index

Community A:

Community B:

Community C:

Shannon’s index

Community A:

−[(0.24) (ln 0.24)+(0.16) (ln 0.16)+(0.8)(ln 0.08)+(0.34) (ln 0.34)+(0.18) (ln 0.18)] = 1.51

Community B:

−[(0.20) (ln 0.20)+(0.20) (ln 0.20)+(0.20) (ln 0.20)+(0.20) (ln 0.20)+(0.20) (ln 0.20)] = 1.61

Community C:

−[(0.25) (ln 0.25)+(0.25) (ln 0.25)+(0.25)(ln 0.25)+(0.25) (ln 0.25)] = 1.39

For both indexes, greater evenness with the same richness provides a higher index value. When evenness is identical, the community with the higher richness has a higher index value.

Graphing the Data

A-17

Chapter 19

Analyzing Ecology

Comparing Communities A and B:

Comparing Communities A and C:

Comparing Communities B and C:

Based on these calculations, Communities A and B are the most similar to each other.

Graphing the Data

Over time, the composition of the seral stages changes, but total species richness continually increases.

Chapter 20

Analyzing Ecology

Lake ecosystem

  Consumption efficiency = 65%

  Assimilation efficiency = 70%

  Net production efficiency = 42%

  Ecological efficiency = 19%

Stream ecosystem

  Consumption efficiency = 65%

  Assimilation efficiency = 38%

  Net production efficiency = 40%

  Ecological efficiency = 10%

The two aquatic ecosystems have higher ecological efficiencies than the terrestrial ecosystem primarily due to higher consumption efficiencies.

In this example, the lower ecological efficiency in the stream ecosystem compared to the lake ecosystem is caused by a lower assimilation efficiency in the stream ecosystem.

Graphing the Data

TERRESTRIAL ECOSYSTEMS NPP (g/m2/yr) AREA (106km2) TOTAL PR0DUCTION (1012kg/yr)
Tropical rainforest 2,000 17.0 34.00
Tropical seasonal forest 1,500 7.5 11.25
Temperate rainforest 1,300 5.0 0.01
Temperate seasonal forest 1,200 7.0 8.40
Boreal forest 800 12.0 9.60
Savanna 700 15.0 10.50
Cultivated land 650 14.0 9.10
Woodland/shrubland 600 8.0 4.80
Temperate grassland 500 9.0 4.50
Tundra 140 8.0 1.12
Desert shrub 70 18.0 1.26
AQUATIC ECOSYSTEMS
Swamp and marsh 2,500 2.0 5.00
Coral reef 2,000 0.6 1.20
Salt marsh 1,800 1.4 2.52
Upwelling zones 500 0.4 0.20
Lake and stream 500 2.5 1.25
Continental shelf 360 26.6 9.58
Open ocean 125 332.0 41.50

Some areas, such as the open ocean, do not have a high productivity per unit area, but the total area is so large that it contributes a relatively large amount to total production. In contrast, some highly productive ecosystems, such as swamps and marshes, do not cover a large area so they contribute a relatively small amount of total production.

A-18

Chapter 21

Analyzing Ecology

We can calculate these answers using the following equation: mt = mo ekt

  For k = 0.05

  After 10 days: mt = mo ekt = 100 e–(0.05)(10) = 61 grams

  After 50 days: mt = mo ekt = 100 e–(0.05)(50) = 8.2 grams

  After 100 days: mt = mo ekt = 100 e–(0.05)(100) = 0.7 grams

  For k = 0.10

  After 10 days: mt = mo ekt = 100 e–(0.10)(10) = 37 grams

  After 50 days: mt = mo ekt = 100 e–(0.10)(50) = 0.7 grams

  After 100 days: mt = mo ekt = 100 e–(0.10)(100) = 0.0 grams

Graphing the Data

Based on this graph, maple leaves have the highest value of k.

Chapter 22

Analyzing Ecology

For this problem, we will use the following equation:

For Community B:

For Community C:

The greater the number of species represented by a single individual, the greater the estimated number of species in the community.

Graphing the Data

Community A has been sampled sufficiently enough to provide a good estimate of species richness, as evidenced by the fact that the species accumulation curve reaches a plateau. In contrast, the curve for Community B suggests that more sampling needs to be conducted before a plateau is achieved.

Chapter 23

Analyzing Ecology

We can make use of the equation that calculates half-lives:

   t1/2 = t ln(2) ÷ ln(N0 ÷ Nt)

   t1/2 = (1) ln(2) ÷ ln(50 ppb ÷ 10 ppb)

   t1/2 = 0.69 ÷ 1.61

   t1/2 = 0.43 days

Graphing the Data

When we look at the absolute numbers in each category, we are able not only to have a sense of the proportion of species that fall within each category, but also to know the absolute number in each category. For example the percentage of threatened mammals is about twice that of birds, but the total number of threatened birds and mammals is about the same. In addition, the percentage of threatened mammals and conifers is similar, but the actual number of threatened mammals is more than six times higher.