Optimal habitat (% spp present) (1)
Coastal risk assessment (2)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (3)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (5)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (6)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (7)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (8)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (10)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (11)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (12)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (13)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (15)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (16)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (17)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (18)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (20)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (21)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (22)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (23)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (25)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (26)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (27)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (28)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (30)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (31)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (32)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (33)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (35)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (36)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (37)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (38)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (40)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (41)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (42)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (43)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (45)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (46)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (47)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (48)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (50)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (51)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (52)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (53)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (55)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (56)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (57)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (58)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (60)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (61)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (62)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (63)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (65)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (66)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (67)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (68)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (70)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (71)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (72)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (73)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (75)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (76)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (77)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (78)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (80)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (81)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (82)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (83)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (85)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (86)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (87)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (88)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (90)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (91)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (92)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (93)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (95)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (96)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (97)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (98)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (100)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (101)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (102)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (103)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (105)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (106)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (107)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (108)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (110)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (111)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (112)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (113)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (115)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (116)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (117)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (118)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (120)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (121)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (122)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (123)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (125)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (126)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (127)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (128)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (130)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (131)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (132)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (133)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (135)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (136)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (137)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (138)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (140)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (141)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (142)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (143)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (145)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (146)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (147)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (148)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (150)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (151)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (152)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (153)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (155)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (156)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (157)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (158)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (160)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (161)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (162)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (163)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (165)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (166)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (167)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (168)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (170)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (171)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (172)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (173)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (175)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (176)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (177)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (178)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (180)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (181)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (182)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (183)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (185)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (186)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (187)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (188)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (190)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (191)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (192)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (193)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (195)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (196)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (197)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (198)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (200)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (201)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (202)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (203)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (205)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (206)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (207)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (208)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (210)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (211)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (212)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (213)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (215)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (216)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (217)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (218)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (220)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (221)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (222)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (223)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (225)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (226)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (227)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (228)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (230)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (231)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (232)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (233)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (235)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (236)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (237)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (238)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (240)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (241)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (242)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (243)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (245)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (246)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (247)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (248)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (250)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (251)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (252)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (253)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (255)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (256)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (257)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (258)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (260)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (261)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (262)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (263)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Abundance (265)
| Not modeled |
| <0.3 |
| 1 |
| 2 to 10 |
| 11 to 100 |
| 101 to 1,000 |
| 1,001 to 10,000 |
Optimal nearshore habitat (266)
| Optimal nearshore habitat |
| Nearshore extent |
Coastal risk assessment (267)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
Tributary risk assessment (268)
| Very low |
| Low |
| Moderate |
| High |
| Very high |
| Nearshore extent |
|