Appendix C. A table of model parameters and additional model results.
Next: List of Figures Previous: Altering All Clam Factors
TABLE C1. Names, units, descriptions, values and references for the list of variables used in the crab model.
| Symbol |
Units |
Description |
Value |
References |
|---|---|---|---|---|
|
||||
3D Random Fields |
||||
# of Mesh Levels |
|
Total number of refinements done of the coarse grid |
4 |
Appendix A.3. |
|
|
Number of discretization points used for generating field in the |
64 |
Appendix A.3.1 |
|
|
Number of discretization points used for generating field in the |
32 |
Appendix A.3.1 |
|
|
Number of discretization points used for generating field in the |
256 |
Appendix A.3.1 |
|
|
Filter used on the Gaussian Random Field |
|
Eq. (A.1) |
|
m |
SD of filter in |
1000 |
Appendix A.3.3 |
|
m |
SD of filter in |
800 |
Appendix A.3.3 |
|
hr |
SD of filter in |
48 |
Appendix A.3.3 |
|
m |
SD of filter in |
1000 |
Appendix A.3.2 |
|
m |
SD of filter in |
800 |
Appendix A.3.2 |
|
hr |
SD of filter in |
48 |
Appendix A.3.2 |
|
|
Component of the filter |
|
Eq. (A.2) |
|
||||
|
||||
Variables Associated with Habitat |
||||
|
m |
Distance from the western most point of the estuary |
|
Appendix A.3.2 |
|
m |
Maximum distance from the western most point of the estuary |
|
Appendix A.3.2 |
|
|
Proportion of distance from the western most point of the estuary |
|
Appendix A.3.2 |
|
m |
Depth of estuary at location |
|
Appendix A.3 |
|
mg/L |
Concentration of oxygen in bottom water of estuary |
Eq. (A.9) |
|
|
mg/L |
Concentration of oxygen in upper water column at saturation |
Eq. (A.11) |
|
|
1/hr |
Rate constant for oxygen demand by sediment Eq. (A.15) |
5.75E-3 |
Based on Borsuk et al. (2001b); Borsuk et al. (2001a) |
|
|
Constant representing level of temperature dependency. Eq. (A.15) |
1.13 |
|
|
m/hr |
Constant for vertical oxygen exchange from surface, Eq. (A.12) |
0.003 |
|
|
1/hr |
|
||
|
|
Constant representing level of temperature dependence. Eq. (A.12) |
1.0 |
|
|
psu |
Bottom salinity |
Eq. (A.6) |
Appendix A.3.3 |
|
psu |
Maximum salinity |
Eq. (A.7) |
Appendix A.3.3 |
|
|
Temperature |
Eq. (A.3) |
Appendix A.3.2 |
|
|
Temperature |
Eq. (A.5) |
Appendix A.3.2 |
|
|
Temperature |
Eq. (A.4) |
Appendix A.3.2 |
|
m/hr |
Mean tidal velocity Eq. (A.12) |
100 |
|
|
||||
|
||||
Clam Variables |
||||
|
g/cm |
Scaling parameter relating clam length,
|
0.1 |
|
|
|
Power relating clam length
|
3.0 |
|
|
|
Coeff. of temperature growth. Eq. (A.17) |
0.2 |
|
|
|
Coeff. of temperature respiration. Eq. (A.17) |
0.17 |
|
|
hr |
Time between updates of clams |
24 |
|
|
|
Temperature dependence of clam growth |
Eq. (A.18) |
|
|
|
Temperature dependence of clam respiration |
Eqs. (A.17) |
|
|
g |
Maximum growth rate for clam on a wet weight basis Eq. (A.17). |
4.3E-4 |
Based on Solidoro et al. (2000, Table 2) |
|
|
Proportion decrease in metabolism due to DO |
Eq. (A.19) |
|
|
|
Clam biomass factor influencing recruitment |
Eq. (A.23) |
|
|
|
Triangle depth factor influencing recruitment |
App A.4.3 |
|
Initial mass |
g |
Initial mass of recruited clam |
0.001 |
|
|
cm |
Length of clam shell |
|
Eq. (A.16) |
|
hr |
Parameter Eq. (A.20), CDF of times till death at fixed DO |
32.16 |
|
|
L hr/mg |
Parameter Eq. (A.20), CDF of times till death at fixed DO |
27.36 |
|
|
hr |
Parameter Eq. (A.20), CDF of times till death at fixed DO |
9.6 |
|
|
hr |
Mortality rate without predation Eq. (A.20) |
1.2E-5 |
|
|
hr |
Mortality rate for clams in water less than -5
|
0.2 |
|
|
hr |
Mortality rate for clams in water greater than
|
1.04E-2 |
|
|
1/hr |
Maximum respiration rate for clam on a wet weight basis Eq. (A.17) |
3.5E-4 |
|
|
g/m |
Grams of clam biomass on a given fine-level triangle |
|
Eq. (A.23) |
|
g/m |
Upper bound on clam biomass on a given fine-level triangle Eq. (A.23) |
850 |
|
|
#/m |
Potential recruitment egg density |
|
Appendix A.4.3 |
|
#/m |
Clam density on a fine-level triangle |
|
Eq. (A.24) |
|
#/m |
Upper bound on clam density on a given triangle Eq. (A.24) |
1300 |
|
|
|
Temperature of clam. |
|
|
|
|
Max temperature for growth. Eq. (A.17) |
31 |
|
|
|
Max. temperature for respiration. Eq. (A.17) |
33 |
|
|
|
Min. temperature for respiration. Eq. (A.17) |
-5 |
|
|
|
Optimal temperature for growth. Eq. (A.17) |
22 |
|
|
|
Optimal temperature for respiration. Eq. (A.17) |
20 |
|
|
g |
Clam's wet weight. |
|
|
|
||||
|
||||
Background Food |
||||
|
m |
Area of fine-level triangle |
Eq. (A.25) |
|
|
1/hr |
Base mortality rate of background |
2E-4 |
|
|
|
Coeff. of temperature growth. Eq. (A.25) |
0.2 |
|
|
|
Temperature dependence of growth of background food Eq. (A.25) |
|
Eq. (A.18) |
|
g |
Number of grams of background food on a fine-level triangle |
|
Eq. (A.25) |
|
g |
Average density of background food just on triangle and neighbors |
|
Eq. (A.25) |
|
g/m |
Carrying capacity of background |
400 |
Eq. (A.25) |
|
g/m |
Density of background food on triangle |
|
|
|
1/hr |
Max growth rate of background |
8E-4 |
Eq. (A.25) |
|
hr |
Time between updates of background |
24 |
Eq. (A.25) |
|
|
Max temperature for growth. Eq. (A.25) |
35 |
|
|
|
Optimal temperature for growth. Eq. (A.25) |
26 |
|
|
||||
|
||||
Crab Variables |
||||
|
|
Parameter in Eq. (A.40). |
0.004 |
|
|
|
Parameter relating size of crab to ingestion rate. Eq. (A.38) |
30.0 |
|
|
g/cm
|
Scale parameter in Eq. (A.36) relating CW to wet weight |
0.14 |
Pullen and Trent (1970); Olmi III and Bishop (1983); Cadman and Weinstein (1985); Newcombe et al. (1949) |
|
g
|
Scalar governing maximum rate of movement Eq. (A.28) |
|
|
|
|
Maximum base respiration parameter. Eq. (A.44) |
0.00678 |
Booth and McMahon (1992, Table 1) and Houlihan et al. (1985, Fig. 1). |
|
|
Minimum base respiration rate. Eq. (A.44) |
0.00166 |
Booth and McMahon (1992, Table 1)and Houlihan et al. (1985, Fig. 1). |
|
g/cm
|
Scalar relating CW to total grams to molt. Eq. (A.46) |
2E-2 |
|
|
|
Scalar relating mass and movement rate to energy expenditure. Eq. (A.45) |
4E-5 |
|
|
cm |
Scaling parameter for stomach volume in Eq. (A.37) |
0.0255 |
Based on McGaw and Reiber (2000) |
|
|
Parameter in Eq. (A.40). |
2.0 |
|
|
|
Parameter relating size of crab to ingestion rate. Eq. (A.38) |
0.25 |
|
|
|
Power relating CW to wet weight in Eq. (A.36) |
2.7 |
Pullen and Trent (1970); Olmi III and Bishop (1983); Cadman and Weinstein (1985); Newcombe et al. (1949) |
|
|
How metabolic demand increases with weight. Eq. (A.44) |
2/3 |
|
|
|
Power relating CW to total grams crab must expend to molt. Eq. (A.46) |
2 |
|
|
|
Power relating mass to rate of energy usage for movement. Eq. (A.45) |
0.33 |
|
|
|
Power of CW for computing stomach volume Eq. (A.37) |
2.0 |
See Appendix A.5.6 |
|
|
First parameter of movement distribution. App. A.5.4 |
1 |
|
|
|
Second parameter of movement distribution. App. A.5.4 |
40 |
|
CW |
cm |
Carapace width |
|
|
|
cm |
Lower range of CW at 7th instar. Appendix A.5.13 |
1.05 |
|
|
cm |
Width of CW instantiation range at. Appendix A.5.13 |
0.6 |
|
|
m |
Maximum distance between crabs when they may interact |
12 |
Appendix A.5.3 |
|
hr |
Random time interval between a crab's updates |
|
Appendix A.5.2 |
Energy |
cal |
Energy content of a single crab egg. |
0.0454 |
|
|
# |
Number of clams in age class |
Eq. (A.33) |
|
|
|
Function governing metabolism on temperature |
Eq. (A.39) |
|
|
|
Particular parameterization of
|
Eq. (A.38) |
|
|
g |
Wet weight of crab. |
Eq. (A.30) |
|
|
g/hr |
Grams egested from the crab |
Eq. (A.41) |
|
|
g/hr |
Grams egested from the stomach |
Eq. (A.40) |
|
|
g/hr |
Grams ingested into the crab's stomach. |
Eq. (A.38) |
|
|
g |
Mass when next molting will be triggered. Eq. (A.36) |
|
|
|
g/hr |
Grams expended molting over |
Eq. (A.47) |
|
|
g/hr |
Grams used solely by crab moving |
Eq. (A.45) |
|
|
g/hr |
Grams put into reproduction |
Appendix A.5.12 |
|
|
g/hr |
Respiration and excretion costs |
Eq. (A.44) |
|
|
g |
Grams of food in stomach |
Eq. (A.42) |
|
|
g |
Total grams crab expends to molt |
Eq. (A.47) |
|
|
g |
Grams expended molting. |
Eq. (A.47) |
|
|
|
Absorption coefficient. Eq. (A.41) |
0.6 |
|
|
|
Change in weighting factor caused by DO |
|
Appendix A.5.6 |
|
|
Default weighting factor for clam depth refuge Eq. (A.34) |
1.0 |
|
|
m |
Constant in Eq. (A.31) |
1/75 |
|
|
m |
Governs probability of finding background food |
Eq. (A.35) |
|
|
|
Excretion as a proportion of respiration costs |
0.05 |
|
|
|
Constant governing rate crab development in maturation pot. See App. A.5.13 |
0.55 |
|
|
|
Gives dependence of rate of movement on temperature. |
Eq. (A.27) |
|
|
1/hr |
Mortality rate for crabs in maturation pot. App. A.5.13 |
5E-3 |
|
|
hr |
Parameter governing crab's update times |
1.0 |
|
|
|
First parameter for crab's lifetime distribution. App. A.5.14 |
3.0 |
|
|
|
Second parameter for crab's lifetime distribution. App. A.5.14 |
1.5 |
|
Max Age |
hr |
App. A.5.14 |
70080 |
|
|
|
Weighting factor governing crab's foraging ability on clams |
Eq. (A.33) |
|
|
|
Lower bound for proportion increase in CW. Eq. (A.49) |
0.24 |
|
|
|
Upper bound for proportion increase in CW. Eq. (A.49) |
0.32 |
|
|
|
Slope for temperature dependence of egestion in Eq. (A.40) |
5 |
|
|
|
Slope for temperature dependence of intake in Eq. (A.38) |
5 |
|
|
|
Slope for temperature dependence of metabolism |
2.5 |
|
|
|
Quality of food feeding on |
|
|
|
|
Quality of food in stomach |
Eq. (A.43) |
|
|
#/m |
Density of clams within crab's forageable size range |
|
Eq. (A.31) |
|
cal/g wet wt |
Energy density of crab |
1000 |
|
|
g/cm |
Density of food in stomach |
1.5 |
|
|
#/m |
Density clams on triangle |
|
|
|
g/m |
Density of background food on triangle |
Eq. (A.35) |
|
|
#/m |
Upper bound on the density of crabs in the estuary |
0.4 |
Appendix A.5.13 |
Scale factor |
|
Factor by which the estuary is scaled Appendix A.6 |
100 |
|
Sex Ratio |
|
Proportion of male crab's instantiated into the estuary. |
0.5 |
|
|
g |
Parameter governing rate of energy expenditure as molting progresses. Eq. (A.47) |
0.15 |
|
|
rad |
Direction of crab movement, kept between |
|
|
|
|
Maximum temperature for crab egestion. Eq. (A.40) |
33 |
|
|
|
Maximum temperature for crab ingestion. Eq. (A.38) |
33 |
|
|
|
Maximum temperature for metabolic processes |
35 |
|
|
|
Maximum temperature for crab spawning |
29 |
|
|
|
Minimum temperature for crab spawning |
19 |
|
|
|
Minimum temperature for metabolic processes |
2 |
|
|
|
Optimal temperature for crab egestion. Eq. (A.40) |
25 |
|
|
|
Optimal temperature for crab ingestion. Eq. (A.38) |
25 |
|
|
|
Optimal temperature for metabolic processes |
26 |
|
|
m/hr |
Maximum rate of crab movement. Eq. (A.28) |
720 |
|
|
m/hr |
Actual rate of crab movement. |
Eq. (A.28) |
|
|
cm |
Volume of Crab's Stomach. |
Eq. (A.37) |
|
|
cm |
Volume of food in crab's stomach. |
|
|
|
|
Gaussian Random Field |
|
|
|
|
Random mixing term for DO |
|
|
TABLE C2. Estuary wide summaries of hypoxic extent crossed with duration. Additional variables are given in Table 1. For all variables except Recruit 7, 12 and 18, the mean and (SD) were calculated for the daily model exports for years 30 through 39 between June 1 and September 30 (n=1220). Recruit 7, 12 and 18 were calculated over the entire 10 year period. The variable Max % Hypoxic is the maximum percentage of the estuary hypoxic per year averaged over the 10 years.
|
Max Extent Hypoxia |
|||||||||||
|
|
|
|
|
||||||||
Hypoxic Dur |
Short |
Long |
Fixed |
Short |
Long |
Fixed |
Short |
Long |
Fixed |
Short |
Long |
Fixed |
Max % Hypoxic |
17.7 |
18 |
15.6 |
28.1 |
27 |
32.8 |
44.9 |
41.7 |
45.1 |
61.9 |
58.3 |
58.8 |
|
(6.5) |
(6.5) |
(0.1) |
(7.2) |
(7.4) |
(0.1) |
(7.2) |
(7.7) |
(0.1) |
(6.2) |
(6.4) |
(0) |
% Hypoxic |
5.7 |
6.9 |
7.3 |
10.7 |
12.5 |
18.9 |
20.9 |
22.9 |
31.1 |
36.9 |
37.8 |
45.2 |
|
(5.3) |
(5.9) |
(5.7) |
(7.7) |
(8.4) |
(9.8) |
(11.3) |
(11.4) |
(12.7) |
(13) |
(12.6) |
(12.7) |
DO (mg/L) |
5.5 |
5.4 |
3.5 |
5.2 |
5.1 |
3.1 |
4.8 |
4.8 |
2.9 |
4.1 |
4.1 |
2.6 |
|
(0.7) |
(0.7) |
(0.2) |
(0.8) |
(0.8) |
(0.3) |
(0.8) |
(0.8) |
(0.3) |
(0.9) |
(0.9) |
(0.3) |
Hypoxic Edge (10 |
1.12 |
1.33 |
1.59 |
1.82 |
2.06 |
2.7 |
3.04 |
3.25 |
3.71 |
4.13 |
4.24 |
4.84 |
|
(0.85) |
(0.91) |
(1.08) |
(1.07) |
(1.11) |
(0.97) |
(1.28) |
(1.27) |
(1.04) |
(0.94) |
(0.91) |
(1.02) |
Clam Density (#/m |
915 |
913 |
882 |
914 |
902 |
821 |
893 |
852 |
802 |
774 |
722 |
696 |
|
(73) |
(92) |
(134) |
(89) |
(115) |
(184) |
(128) |
(159) |
(236) |
(230) |
(244) |
(248) |
Crab Biomass (g/m |
7.84 |
7.52 |
4.7 |
6.84 |
6.3 |
3.33 |
5.29 |
4.86 |
2.69 |
2.83 |
2.75 |
2.01 |
|
(0.8) |
(0.77) |
(0.58) |
(0.87) |
(0.68) |
(0.52) |
(0.77) |
(0.57) |
(0.4) |
(0.42) |
(0.39) |
(0.31) |
Mat Female Mass (g) |
239.2 |
245.2 |
221.8 |
242.2 |
241.7 |
217.6 |
234.1 |
231.7 |
220.3 |
223.4 |
220.2 |
222.4 |
|
(5.9) |
(6.5) |
(8.6) |
(8.3) |
(8.2) |
(9.4) |
(6.3) |
(9.1) |
(9.4) |
(8) |
(13) |
(11.1) |
Mat Female CW (cm) |
17.4 |
17.6 |
17.1 |
17.5 |
17.5 |
17 |
17.5 |
17.4 |
17.1 |
17.4 |
17.4 |
17.3 |
|
(0.1) |
(0.1) |
(0.2) |
(0.1) |
(0.1) |
(0.2) |
(0.1) |
(0.2) |
(0.2) |
(0.2) |
(0.4) |
(0.3) |
Egg (#/m |
19.04 |
16.22 |
6.46 |
16.67 |
12 |
4.41 |
10.83 |
6.42 |
3.83 |
3.28 |
2.08 |
2.26 |
|
(13.38) |
(12.75) |
(7.98) |
(12.55) |
(10.74) |
(6.66) |
(9.94) |
(7.9) |
(5.88) |
(5.8) |
(4.48) |
(4.57) |
Egg per Mat Fe (#/# hr) |
1794 |
1750 |
1261 |
1893 |
1653 |
1252 |
1828 |
1397 |
1280 |
1283. |
1007 |
1195 |
|
(1250) |
(1362) |
(1501) |
(1418) |
(1472) |
(1839) |
(1655) |
(1718) |
(1962) |
(2289) |
(2214) |
(2418) |
Recruit 7 (10 |
133.85 |
119.82 |
74.95 |
131.47 |
99.6 |
57.65 |
95.45 |
64.61 |
51.51 |
38.79 |
27.2 |
33.41 |
|
(456.73) |
(388.57) |
(275.73) |
(468.41) |
(343.84) |
(215.23) |
(325.31) |
(240.68) |
(188.49) |
(162.63) |
(121.68) |
(139.27) |
Recruit 12 (10 |
14.28 |
11.94 |
12.55 |
15.92 |
11.52 |
10.94 |
15.33 |
10.34 |
9.56 |
8.51 |
6 |
7.67 |
|
(25.53) |
(19.91) |
(25.75) |
(29.51) |
(20.15) |
(22.62) |
(28.66) |
(19.22) |
(19.84) |
(15.94) |
(11.53) |
(15.87) |
Recruit 18 (10 |
2.36 |
2.13 |
1.69 |
2.12 |
1.91 |
1.25 |
1.73 |
1.55 |
0.99 |
1.06 |
0.93 |
0.79 |
|
(3.7) |
(3.33) |
(2.96) |
(3.51) |
(3.17) |
(2.31) |
(3.06) |
(2.78) |
(1.97) |
(2.08) |
(1.88) |
(1.6) |
Gut Fullness 7-12 |
0.366 |
0.352 |
0.382 |
0.4 |
0.351 |
0.379 |
0.438 |
0.363 |
0.365 |
0.394 |
0.339 |
0.36 |
|
(0.07) |
(0.063) |
(0.092) |
(0.069) |
(0.064) |
(0.091) |
(0.077) |
(0.068) |
(0.085) |
(0.078) |
(0.081) |
(0.094) |
Gut Fullness 13-17 |
0.445 |
0.447 |
0.463 |
0.459 |
0.456 |
0.457 |
0.478 |
0.459 |
0.464 |
0.464 |
0.438 |
0.457 |
|
(0.032) |
(0.031) |
(0.039) |
(0.033) |
(0.034) |
(0.045) |
(0.03) |
(0.039) |
(0.046) |
(0.039) |
(0.058) |
(0.051) |
Gut Fullness 18+ |
0.43 |
0.412 |
0.434 |
0.455 |
0.427 |
0.453 |
0.492 |
0.431 |
0.443 |
0.452 |
0.419 |
0.442 |
|
(0.037) |
(0.034) |
(0.029) |
(0.035) |
(0.035) |
(0.031) |
(0.031) |
(0.042) |
(0.038) |
(0.044) |
(0.046) |
(0.042) |
Food Qual 7-12 |
0.347 |
0.346 |
0.346 |
0.347 |
0.346 |
0.345 |
0.347 |
0.347 |
0.346 |
0.35 |
0.35 |
0.343 |
|
(0.015) |
(0.016) |
(0.016) |
(0.014) |
(0.015) |
(0.016) |
(0.014) |
(0.017) |
(0.017) |
(0.019) |
(0.027) |
(0.02) |
Food Qual 13-17 |
0.415 |
0.42 |
0.405 |
0.409 |
0.418 |
0.405 |
0.402 |
0.417 |
0.407 |
0.405 |
0.412 |
0.4 |
|
(0.007) |
(0.009) |
(0.007) |
(0.007) |
(0.008) |
(0.008) |
(0.006) |
(0.008) |
(0.01) |
(0.01) |
(0.011) |
(0.009) |
Food Qual 18+ |
0.402 |
0.407 |
0.391 |
0.396 |
0.403 |
0.389 |
0.385 |
0.398 |
0.392 |
0.386 |
0.392 |
0.39 |
|
(0.008) |
(0.008) |
(0.006) |
(0.008) |
(0.007) |
(0.007) |
(0.006) |
(0.01) |
(0.008) |
(0.009) |
(0.01) |
(0.009) |
Death Aggr 7-12 (10 |
6.63 |
6.1 |
6.04 |
7.31 |
5.78 |
5.76 |
7.79 |
5.57 |
5.63 |
5.74 |
4.01 |
5.08 |
|
(4.83) |
(4.38) |
(4.82) |
(5.08) |
(4.25) |
(5.06) |
(5.82) |
(4.19) |
(4.82) |
(5.33) |
(4.49) |
(5.01) |
Death Aggr 13-17 (10 |
7.31 |
7.11 |
8.05 |
8.24 |
7.65 |
8.9 |
8.89 |
8.21 |
9.67 |
8.31 |
7.48 |
9.14 |
|
(3.16) |
(3.38) |
(3.54) |
(3.78) |
(3.96) |
(4.85) |
(4.47) |
(4.94) |
(5.51) |
(5.11) |
(5.59) |
(5.77) |
Death Aggr 18+ (10 |
2.4 |
2.12 |
3.07 |
2.61 |
2.4 |
3.36 |
2.93 |
2.55 |
3.19 |
3.26 |
2.8 |
3.5 |
|
(1.82) |
(1.67) |
(2.24) |
(2.05) |
(1.97) |
(2.74) |
(2.61) |
(2.39) |
(2.99) |
(3.31) |
(3.22) |
(3.7) |
TABLE C3. Effect of altering the levels of clam and background prey. Additional variables are given in Table 2. The food Limited case corresponds to decreasing the upper bound on clam biomass recruitment to
=425 (g/m
) (Default value is
g/m
, Table C1) and background carrying capacity to 200 (g/m
) (Default value is
g/m
, Table C1). The Default is the same as Short hypoxic duration in Table C2. The food Unlimited case corresponds to turning off all clam and background mortality due to hypoxia. A Short hypoxic duration was used in all scenarios.
|
Short Duration, Max Extent Hypoxia |
|||||||||||
|
|
|
|
|
||||||||
Food Level |
Limit |
Def |
Unlim |
Limit |
Def |
Unlim |
Limit |
Def |
Unlim |
Limit |
Def |
Unlim |
Max % Hypoxic |
18.6 |
17.7 |
19.4 |
33.9 |
28.1 |
30.9 |
49.9 |
44.9 |
46.8 |
61.8 |
61.9 |
62.9 |
|
(6.7) |
(6.5) |
(6.2) |
(7.4) |
(7.2) |
(7) |
(6.8) |
(7.2) |
(6.8) |
(6.5) |
(6.2) |
(6) |
% Hypoxic |
|
|
|
|
|
|
|
|
|
|
|
|
|
6 |
5.7 |
6.8 |
13.5 |
10.7 |
12.6 |
24.9 |
20.9 |
23.3 |
36.8 |
36.9 |
38.3 |
|
(5.6) |
(5.3) |
(5.7) |
(9.1) |
(7.7) |
(8.2) |
(12) |
(11.3) |
(11.1) |
(12.9) |
(13) |
(12.7) |
DO (mg/L) |
5.5 |
5.5 |
5.4 |
5.1 |
5.2 |
5.2 |
4.7 |
4.8 |
4.8 |
4.1 |
4.1 |
4 |
|
(0.7) |
(0.7) |
(0.7) |
(0.8) |
(0.8) |
(0.8) |
(0.9) |
(0.8) |
(0.9) |
(0.9) |
(0.9) |
(0.9) |
Hypoxic Edge (10 |
1.14 |
1.12 |
1.26 |
2.16 |
1.82 |
2.05 |
3.34 |
3.04 |
3.29 |
4.13 |
4.13 |
4.18 |
|
(0.87) |
(0.85) |
(0.86) |
(1.2) |
(1.07) |
(1.06) |
(1.21) |
(1.28) |
(1.18) |
(0.95) |
(0.94) |
(0.89) |
Clam Density (#/m |
448 |
915 |
915 |
441 |
914 |
928 |
436 |
893 |
947 |
384 |
774 |
983 |
|
(39) |
(73) |
(58) |
(51) |
(89) |
(55) |
(83) |
(128) |
(53) |
(111) |
(230) |
(52) |
Crab Biomass (g/m |
4.63 |
7.84 |
7.99 |
3.62 |
6.84 |
6.92 |
2.69 |
5.29 |
5.53 |
1.8 |
2.83 |
3.78 |
|
(0.36) |
(0.8) |
(0.86) |
(0.47) |
(0.87) |
(0.83) |
(0.42) |
(0.77) |
(0.71) |
(0.3) |
(0.42) |
(0.55) |
Mat Female Mass (g) |
254.4 |
239.2 |
239.4 |
244.5 |
242.2 |
239 |
240 |
234.1 |
238.5 |
225.5 |
223.4 |
240.3 |
|
(10.1) |
(5.9) |
(6.4) |
(8.6) |
(8.3) |
(6.5) |
(12.4) |
(6.3) |
(6.8) |
(13.6) |
(8) |
(8.9) |
Mat Female CW (cm) |
17.7 |
17.4 |
17.5 |
17.6 |
17.5 |
17.5 |
17.6 |
17.5 |
17.5 |
17.5 |
17.4 |
17.5 |
|
(0.1) |
(0.1) |
(0.1) |
(0.1) |
(0.1) |
(0.1) |
(0.2) |
(0.1) |
(0.1) |
(0.3) |
(0.2) |
(0.2) |
Egg (#/m |
8.88 |
19.04 |
19.3 |
6.91 |
16.67 |
16.39 |
3.62 |
10.83 |
12.45 |
1.24 |
3.28 |
7.33 |
|
(9.4) |
(13.38) |
(14.2) |
(7.76) |
(12.55) |
(12.52) |
(5.45) |
(9.94) |
(10.92) |
(3.27) |
(5.8) |
(8.36) |
Egg per Mat Fe (#/# hr) |
1451 |
1794 |
1832 |
1442 |
1893 |
1918 |
1008 |
1828 |
1961 |
744 |
1283 |
2004 |
|
(1544) |
(1250) |
(1319) |
(1621) |
(1418) |
(1467) |
(1521) |
(1655) |
(1704) |
(2170) |
(2289) |
(2285) |
Recruit 7 (10 |
78.91 |
133.85 |
145.21 |
67.36 |
131.47 |
126.12 |
41.92 |
95.45 |
107.33 |
18.38 |
38.79 |
79.41 |
|
(282.99) |
(456.73) |
(509.53) |
(255.09) |
(468.41) |
(451.22) |
(170.24) |
(325.31) |
(363.06) |
(97.89) |
(162.63) |
(285.18) |
Recruit 12 (10 |
5.05 |
14.28 |
15.51 |
5.73 |
15.92 |
16.95 |
4.92 |
15.33 |
16.15 |
3.49 |
8.51 |
12.19 |
|
(8.43) |
(25.53) |
(27.74) |
(9.56) |
(29.51) |
(31.87) |
(8.62) |
(28.66) |
(30.72) |
(6.68) |
(15.94) |
(22.72) |
Recruit 18 (10 |
1.2 |
2.36 |
2.45 |
1.13 |
2.12 |
2.18 |
0.85 |
1.73 |
1.77 |
0.62 |
1.06 |
1.28 |
|
(1.91) |
(3.7) |
(3.89) |
(1.87) |
(3.51) |
(3.69) |
(1.61) |
(3.06) |
(3.14) |
(1.32) |
(2.08) |
(2.45) |
Gut Fullness 7-12 |
0.271 |
0.366 |
0.39 |
0.283 |
0.4 |
0.429 |
0.285 |
0.438 |
0.451 |
0.306 |
0.394 |
0.459 |
|
(0.055) |
(0.07) |
(0.069) |
(0.056) |
(0.069) |
(0.077) |
(0.049) |
(0.077) |
(0.091) |
(0.063) |
(0.078) |
(0.123) |
Gut Fullness 13-17 |
0.372 |
0.445 |
0.452 |
0.386 |
0.459 |
0.47 |
0.409 |
0.478 |
0.485 |
0.393 |
0.464 |
0.497 |
|
(0.041) |
(0.032) |
(0.031) |
(0.04) |
(0.033) |
(0.031) |
(0.043) |
(0.03) |
(0.028) |
(0.058) |
(0.039) |
(0.027) |
Gut Fullness 18+ |
0.311 |
0.43 |
0.443 |
0.336 |
0.455 |
0.478 |
0.308 |
0.492 |
0.505 |
0.319 |
0.452 |
0.518 |
|
(0.043) |
(0.037) |
(0.036) |
(0.045) |
(0.035) |
(0.031) |
(0.044) |
(0.031) |
(0.027) |
(0.048) |
(0.044) |
(0.029) |
Food Qual 7-12 |
0.344 |
0.347 |
0.347 |
0.345 |
0.347 |
0.347 |
0.345 |
0.347 |
0.345 |
0.347 |
0.35 |
0.336 |
|
(0.018) |
(0.015) |
(0.015) |
(0.018) |
(0.014) |
(0.014) |
(0.022) |
(0.014) |
(0.031) |
(0.025) |
(0.019) |
(0.063) |
Food Qual 13-17 |
0.426 |
0.415 |
0.411 |
0.42 |
0.409 |
0.404 |
0.414 |
0.402 |
0.4 |
0.419 |
0.405 |
0.4 |
|
(0.009) |
(0.007) |
(0.007) |
(0.008) |
(0.007) |
(0.006) |
(0.009) |
(0.006) |
(0.006) |
(0.011) |
(0.01) |
(0.008) |
Food Qual 18+ |
0.424 |
0.402 |
0.397 |
0.418 |
0.396 |
0.389 |
0.422 |
0.385 |
0.386 |
0.41 |
0.386 |
0.385 |
|
(0.01) |
(0.008) |
(0.008) |
(0.01) |
(0.008) |
(0.007) |
(0.012) |
(0.006) |
(0.005) |
(0.013) |
(0.009) |
(0.007) |
Death Aggr 7-12 (10 |
3.84 |
6.63 |
7.2 |
4.11 |
7.31 |
7.81 |
3.46 |
7.79 |
8.87 |
3.28 |
5.74 |
8.7 |
|
(2.96) |
(4.83) |
(5.09) |
(2.83) |
(5.08) |
(5.58) |
(2.59) |
(5.82) |
(14.06) |
(3.43) |
(5.33) |
(10.36) |
Death Aggr 13-17 (10 |
4.82 |
7.31 |
7.39 |
5.87 |
8.24 |
8.34 |
6.67 |
8.89 |
9.12 |
6.38 |
8.31 |
9.09 |
|
(3.02) |
(3.16) |
(3.22) |
(3.61) |
(3.78) |
(3.79) |
(4.43) |
(4.47) |
(4.57) |
(4.86) |
(5.11) |
(5.2) |
Death Aggr 18+ (10 |
1.85 |
2.4 |
2.44 |
2.43 |
2.61 |
2.6 |
2.53 |
2.93 |
2.75 |
2.99 |
3.26 |
3.01 |
|
(1.8) |
(1.82) |
(1.76) |
(2.36) |
(2.05) |
(2.08) |
(2.78) |
(2.61) |
(2.41) |
(3.86) |
(3.31) |
(2.91) |
TABLE C4. Estuary wide summaries for altering cannibalism potential via maximum interaction distance (Section A.5.3). Additional variables are given in Table 3. The Default interaction distance corresponds to the value used in previous simulations, Small to decreasing this distance by a factor of 4 and Large represents doubling it. All simulations done using Short hypoxic duration (Table C2).
|
Short Duration, Max Extent Hypoxia |
|||||||||||
|
|
|
|
|
||||||||
Interact Dist |
Small |
Default |
Large |
Small |
Default |
Large |
Small |
Default |
Large |
Small |
Default |
Large |
Max % Hypoxic |
15.4 |
17.7 |
19 |
25.8 |
28.1 |
29.2 |
43.2 |
44.9 |
45.7 |
61.4 |
61.9 |
62.3 |
|
(6) |
(6.5) |
(6.3) |
(7.2) |
(7.2) |
(7) |
(7.3) |
(7.2) |
(7.2) |
(6.3) |
(6.2) |
(6.3) |
% Hypoxic |
4.7 |
5.7 |
6.3 |
9.5 |
10.7 |
11.4 |
19.7 |
20.9 |
21.5 |
36.4 |
36.9 |
37.1 |
|
(4.7) |
(5.3) |
(5.6) |
(7.3) |
(7.7) |
(8) |
(11) |
(11.3) |
(11.4) |
(12.9) |
(13) |
(13) |
DO (mg/L) |
5.5 |
5.5 |
5.4 |
5.3 |
5.2 |
5.2 |
4.9 |
4.8 |
4.8 |
4.1 |
4.1 |
4.1 |
|
(0.7) |
(0.7) |
(0.7) |
(0.8) |
(0.8) |
(0.8) |
(0.8) |
(0.8) |
(0.8) |
(0.9) |
(0.9) |
(0.9) |
Hypoxic Edge (10 |
0.98 |
1.12 |
1.18 |
1.66 |
1.82 |
1.91 |
2.9 |
3.04 |
3.1 |
4.11 |
4.13 |
4.14 |
|
(0.82) |
(0.85) |
(0.86) |
(1.03) |
(1.07) |
(1.1) |
(1.27) |
(1.28) |
(1.28) |
(0.95) |
(0.94) |
(0.94) |
Clam Density (#/m |
878 |
915 |
952 |
888 |
914 |
951 |
864 |
893 |
923 |
758 |
774 |
789 |
|
(85) |
(73) |
(64) |
(95) |
(89) |
(80) |
(132) |
(128) |
(122) |
(234) |
(230) |
(218) |
Crab Biomass (g/m |
12.1 |
7.84 |
4.67 |
9.93 |
6.84 |
3.62 |
8.29 |
5.29 |
2.63 |
4.43 |
2.83 |
1.65 |
|
(0.85) |
(0.8) |
(0.38) |
(1.43) |
(0.87) |
(0.32) |
(0.89) |
(0.77) |
(0.29) |
(0.78) |
(0.42) |
(0.23) |
Mat Female Mass (g) |
252 |
239.2 |
243 |
260.4 |
242.2 |
236.6 |
246.2 |
234.1 |
229.8 |
218.8 |
223.4 |
218.6 |
|
(8.7) |
(5.9) |
(8.6) |
(8.6) |
(8.3) |
(9.1) |
(8.1) |
(6.3) |
(8.5) |
(12) |
(8) |
(11.9) |
Mat Female CW (cm) |
17.8 |
17.4 |
17.3 |
17.7 |
17.5 |
17.1 |
17.7 |
17.5 |
17.2 |
17.6 |
17.4 |
17.1 |
|
(0.1) |
(0.1) |
(0.1) |
(0.1) |
(0.1) |
(0.2) |
(0.1) |
(0.1) |
(0.2) |
(0.1) |
(0.2) |
(0.3) |
Egg (#/m |
16.45 |
19.04 |
14.28 |
15.08 |
16.67 |
9.89 |
8.45 |
10.83 |
6.79 |
2.19 |
3.28 |
3.01 |
|
(12.75) |
(13.38) |
(11.18) |
(12.9) |
(12.55) |
(9.55) |
(9.46) |
(9.94) |
(7.68) |
(4.64) |
(5.8) |
(5.14) |
Egg per Mat Fe (#/# hr) |
971 |
1794 |
2203 |
1036 |
1893 |
2131 |
704 |
1828 |
2092 |
387 |
1283 |
1919 |
|
(749) |
(1250) |
(1732) |
(878) |
(1418) |
(2061) |
(784) |
(1655) |
(2365) |
(828) |
(2289) |
(3372) |
Recruit 7 (10 |
121.11 |
133.85 |
119.67 |
116.8 |
131.47 |
91.53 |
84.46 |
95.45 |
70.87 |
27.41 |
38.79 |
37.4 |
|
(472.82) |
(456.73) |
(414.75) |
(451.65) |
(468.41) |
(326.21) |
(329.71) |
(325.31) |
(257.33) |
(144.76) |
(162.63) |
(158.16) |
Recruit 12 (10 |
5.29 |
14.28 |
11.27 |
4.69 |
15.92 |
10.2 |
5.15 |
15.33 |
9.04 |
2.83 |
8.51 |
6.05 |
|
(9.98) |
(25.53) |
(22.15) |
(8.92) |
(29.51) |
(19.52) |
(9.15) |
(28.66) |
(17.51) |
(5.82) |
(15.94) |
(11.35) |
Recruit 18 (10 |
2.05 |
2.36 |
1.24 |
1.65 |
2.12 |
1.03 |
1.58 |
1.73 |
0.83 |
1 |
1.06 |
0.56 |
|
(2.79) |
(3.7) |
(2.47) |
(2.28) |
(3.51) |
(2.11) |
(2.3) |
(3.06) |
(1.85) |
(1.83) |
(2.08) |
(1.36) |
Gut Fullness 7-12 |
0.201 |
0.366 |
0.421 |
0.195 |
0.4 |
0.395 |
0.205 |
0.438 |
0.391 |
0.195 |
0.394 |
0.371 |
|
(0.038) |
(0.07) |
(0.186) |
(0.044) |
(0.069) |
(0.203) |
(0.042) |
(0.077) |
(0.199) |
(0.057) |
(0.078) |
(0.21) |
Gut Fullness 13-17 |
0.232 |
0.445 |
0.504 |
0.248 |
0.459 |
0.503 |
0.282 |
0.478 |
0.502 |
0.294 |
0.464 |
0.503 |
|
(0.047) |
(0.032) |
(0.028) |
(0.048) |
(0.033) |
(0.032) |
(0.047) |
(0.03) |
(0.039) |
(0.062) |
(0.039) |
(0.049) |
Gut Fullness 18+ |
0.189 |
0.43 |
0.532 |
0.187 |
0.455 |
0.534 |
0.181 |
0.492 |
0.533 |
0.19 |
0.452 |
0.529 |
|
(0.038) |
(0.037) |
(0.019) |
(0.046) |
(0.035) |
(0.022) |
(0.035) |
(0.031) |
(0.026) |
(0.035) |
(0.044) |
(0.035) |
Food Qual 7-12 |
0.343 |
0.347 |
0.299 |
0.343 |
0.347 |
0.282 |
0.344 |
0.347 |
0.283 |
0.35 |
0.35 |
0.271 |
|
(0.027) |
(0.015) |
(0.119) |
(0.032) |
(0.014) |
(0.134) |
(0.033) |
(0.014) |
(0.135) |
(0.042) |
(0.019) |
(0.144) |
Food Qual 13-17 |
0.433 |
0.415 |
0.414 |
0.425 |
0.409 |
0.415 |
0.42 |
0.402 |
0.416 |
0.437 |
0.405 |
0.413 |
|
(0.02) |
(0.007) |
(0.01) |
(0.022) |
(0.007) |
(0.01) |
(0.019) |
(0.006) |
(0.011) |
(0.019) |
(0.01) |
(0.017) |
Food Qual 18+ |
0.444 |
0.402 |
0.39 |
0.452 |
0.396 |
0.391 |
0.445 |
0.385 |
0.39 |
0.437 |
0.386 |
0.382 |
|
(0.013) |
(0.008) |
(0.005) |
(0.012) |
(0.008) |
(0.006) |
(0.014) |
(0.006) |
(0.007) |
(0.018) |
(0.009) |
(0.008) |
Death Aggr 7-12 (10 |
1.42 |
6.63 |
12.11 |
1.21 |
7.31 |
11.65 |
1.24 |
7.79 |
11.24 |
0.64 |
5.74 |
8.38 |
|
(1.18) |
(4.83) |
(19.65) |
(1.17) |
(5.08) |
(22.6) |
(1.13) |
(5.82) |
(22.35) |
(1.38) |
(5.33) |
(13.92) |
Death Aggr 13-17 (10 |
1.74 |
7.31 |
9.3 |
2.2 |
8.24 |
9.9 |
2.95 |
8.89 |
10.29 |
2.91 |
8.31 |
10.49 |
|
(1.37) |
(3.16) |
(5.13) |
(1.62) |
(3.78) |
(6.55) |
(2.04) |
(4.47) |
(7.96) |
(2.88) |
(5.11) |
(15.52) |
Death Aggr 18+ (10 |
0.61 |
2.4 |
2.06 |
0.85 |
2.61 |
2.29 |
1.03 |
2.93 |
2.76 |
1.26 |
3.26 |
2.93 |
|
(0.61) |
(1.82) |
(1.83) |
(0.81) |
(2.05) |
(2.21) |
(1.04) |
(2.61) |
(3.08) |
(1.44) |
(3.31) |
(3.97) |
|
FIG. C1. Proportion of total crab biomass shallower than 3 m vs the average DO in the estuary from the beginning of year 30 to the end of year 39 under the different hypoxic extents and durations.
|
FIG. C2. Rate of mortality (#.m
.hr
) from all causes of 13 to 17 instar crabs relative to the density (#/m
) of 13 to 17 instar crabs in the estuary for the different hypoxic durations considered. Solid line generated using a Loess smoother.
|
FIG. C3. Rate of mortality (#.m
.hr
) from all causes of 18+ instar crabs relative to the density (#/m
) of 18+ instar crabs in the estuary for the different hypoxic durations considered.
|
FIG. C4. Crab survival function under three hypoxic durations and four hypoxic extents.
|
FIG. C5. Empirical cumulative distribution function for the time it takes crabs under different hypoxic extents and durations to reach the 18th instar from the 7th.
|
FIG. C6. Effect of altering the maximum interaction distance in Scenario III on crab survival. Default corresponds to the default interaction distance used, Small to decreasing this distance by a factor of 4 and Large represents doubling it. All simulations done using Short hypoxic duration. Compare to Figs. C4 and Fig. 9 in the paper.
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