Common use of Minimization and Avoidance Measures for Predator Control Clause in Contracts

Minimization and Avoidance Measures for Predator Control. Pūlama Lānaʻi will implement the following minimization and avoidance measures for its predator control activities: (1) Cat trap lines may be situated on the inside or outside of the perimeter fence, located to minimize interactions with waterbirds, while maintaining trapping efficacy. (2) Rat traps may be situated on the inside or outside of the perimeter fence. Traps which pose a potential source of Take (e.g. snap traps) will be enclosed in a box or other suitable structure that excludes water birds entirely, or in the case of A24 automatic rat traps, with an excluder that prevents them from accessing the inside of the trap. (3) Rodenticide may be used inside or outside the perimeter fence. All rodenticide use will follow United States Environmental Protection Agency (“EPA”) labeling for that rodenticide. Any rodenticide used will be deployed in containers that exclude waterbirds per EPA labeling instructions. Loose and/or hand broadcast rodenticides will not be used. (4) Fine mesh screen barrier will be installed on the perimeter fence at ground level to prevent entry of bullfrogs and cane toads. TMK 2-4-9-002-102 TMK 2-4-9-002-103 TMK 2-4-9-002-104 TMK 2-4-9-002-105 TMK 2-4-9-002-106 TMK 2-4-9-002-107 TMK 2-4-9-002-108 TMK 2-4-9-002-109 TMK 2-4-9-002-110 TMK 2-4-9-002-111 TMK 2-4-9-002-112 TMK 2-4-9-002-113 TMK 2-4-9-002-114 TMK 2-4-9-002-115 TMK 2-4-9-002-116 TMK 2-4-9-002117 TMK 2-4-9-002-119 TMK 2-4-9-003-010 TMK 2-4-9-003-023 TMK 2-4-9-003-027 TMK 2-4-9-004014 TMK 2-4-9-004-037 TMK 2-4-9-004-039 TMK 2-4-9-004-048 TMK 2-4-9-004-050 TMK 2-4-9-004-051 TMK 2-4-9-004-056 TMK 2-4-9-004-077 TMK 2-4-9-017-001 TMK 2-4-9-017-002 TMK 2-4-9-017-003 TMK 2-4-9-017-004 TMK 2-4-9-017-005 TMK 2-4-9-017-006-600 TMK 2-4-9-017-008 TMK 2-4-9-017-009 TMK 2-4-9-017-010 TMK 2-4-9-017-011 TMK 2-4-9-017-022 TMK 2-4-9-017-023 TMK 2-4-9-017-024 TMK 2-4-9-017-025 TMK 2-4-9-017-026 TMK 2-4-9-017-028 TMK 2-4-9-017-029 TMK 2-4-9-017-030 TMK 2-4-9-017-031 TMK 2-4-9-017-032 TMK 2-4-9-017-034 TMK 2-4-9-018-001 TMK 2-4-9-018-002 TMK 2-4-9-018-003 TMK 2-4-9-018-004 TMK 2-4-9-018-005 TMK 2-4-9-019-005 TMK 2-4-9-019-010 TMK 2-4-9-019-028 TMK 2-4-9-019-031 TMK 2-4-9-019-035 TMK 2-4-9-019-036 TMK 2-4-9-019-041 TMK 2-4-9-019-042 TMK 2-4-9-019-046 TMK 2-4-9-019-054 TMK 2-4-9-019-055 TMK 2-4-9-019-066 TMK 2-4-9-019-068 TMK 2-4-9-019-071 TMK 2-4-9-019-073 TMK 2-4-9-019-087 TMK 2-4-9-019-095 TMK 2-4-9-019-102 TMK 2-4-9-019-104 TMK 2-4-9-020-020 TMK 2-4-9-021-002-0001 TMK 2-4-9-021-002-0007 TMK 2-4-9-021-003 TMK 2-4-9-021-004-0003 TMK 2-4-9-021-004-0005 TMK 2-4-9-021-004-0011 TMK 2-4-9-021-004-0013 TMK 2-4-9-021-004-0016 TMK 2-4-9-021-004-0018 TMK 2-4-9-021-004-0019 TMK 2-4-9-021-004-0020 TMK 2-4-9-021-005 TMK 2-4-9-021-006 TMK 2-4-9-021-008 TMK 2-4-9-021-009 TMK 2-4-9-021-011 TMK 2-4-9-022-001 TMK 2-4-9-022-002-0004 The U.S. Fish and Wildlife Service (USFWS) recommends the following measures to be incorporated into project planning to avoid or minimize impacts to fish and wildlife resources. Best Management Practices (BMPs) include the incorporation of procedures or materials that may be used to reduce either direct or indirect negative impacts to aquatic habitats that result from project construction-related activities. These BMPs are recommended in addition to, and do not over-ride any terms, conditions, or other recommendations prepared by the USFWS, other federal, state or local agencies. If you have questions concerning these BMPs, please contact the USFWS Aquatic Ecosystems Conservation Program at ▇▇▇-▇▇▇-▇▇▇▇. 1. Authorized dredging and filling-related activities that may result in the temporary or permanent loss of aquatic habitats should be designed to avoid indirect, negative impacts to aquatic habitats beyond the planned project area. 2. Dredging/filling in the marine environment should be scheduled to avoid coral spawning and recruitment periods, and sea turtle nesting and hatching periods. Because these periods are variable throughout the Pacific islands, we recommend contacting the relevant local, state, or federal fish and wildlife resource agency for site specific guidance. 3. Turbidity and siltation from project-related work should be minimized and contained within the project area by silt containment devices and curtailing work during flooding or adverse tidal and weather conditions. BMPs should be maintained for the life of the construction period until turbidity and siltation within the project area is stabilized. All project construction-related debris and sediment containment devices should be removed and disposed of at an approved site. 4. All project construction-related materials and equipment (dredges, vessels, backhoes, silt curtains, etc.) to be placed in an aquatic environment should be inspected for pollutants including, but not limited to; marine fouling organisms, grease, oil, etc., and cleaned to remove pollutants prior to use. Project related activities should not result in any debris disposal, non-native species introductions, or attraction of non-native pests to the affected or adjacent aquatic or terrestrial habitats. Implementing both a litter-control plan and a Hazard Analysis and Critical Control Point plan (HACCP – see ▇▇▇▇▇://▇▇▇.▇▇▇.▇▇▇/policy/A1750fw1.html) can help to prevent attraction and introduction of non-native species. 5. Project construction-related materials (fill, revetment rock, pipe, etc.) should not be stockpiled in, or in close proximity to aquatic habitats and should be protected from erosion (e.g., with filter fabric, etc.), to prevent materials from being carried into waters by wind, rain, or high surf. 6. Fueling of project-related vehicles and equipment should take place away from the aquatic environment and a contingency plan to control petroleum products accidentally spilled during the project should be developed. The plan should be retained on site with the person responsible for compliance with the plan. Absorbent pads and containment booms should be stored on-site to facilitate the clean-up of accidental petroleum releases. 7. All deliberately exposed soil or under-layer materials used in the project near water should be protected from erosion and stabilized as soon as possible with geotextile, filter fabric or native or non-invasive vegetation matting, hydro-seeding, etc. ▇▇▇▇▇▇▇▇▇▇, K. 2020. Electronic mail message regarding Megalagrion xanthomelas on Maui. (August 5, 2020). 2 pp. ▇▇▇▇▇▇▇, ▇.▇. 1981. The reproductive biology of the Hawaiian subspecies of the black-necked stilt, Himantopus mexicanus knudseni. Ph.D. dissertation, Pennsylvania State University, PA. 106 pp. ▇▇▇▇, ▇.▇., and ▇.▇. ▇▇▇▇▇▇▇▇. 2003. Insects of Hawaii, Vol. 17: Hawaiian Hylaeus (Nesoprosopis) Bees (Hymenoptera: Apoidea). University of Hawaii Press, Honolulu. 234 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources, Division of Forestry and Wildlife. 2003. Title 13 Chapter 123 Rules Regulating Game Mammal Hunting. 56 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2015. Hawaiʻi State Wildlfie Action Plan. Prepared by ▇.▇. ▇▇▇▇▇▇ and Associates, Honolulu, HI 893 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2018. Commission on Water Resources Management. 06/20/18 – Decision on East Maui interim instream flow standards released. ▇▇▇▇▇://▇▇▇▇.▇▇▇▇▇▇.▇▇▇/blog/2018/06/20/nr18-116/. Last accessed September 27, 2022. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2020. Aquatic invasive species. ▇▇▇▇▇://▇▇▇▇.▇▇▇▇▇▇.▇▇▇/ais/. Last accessed July 10, 2020.

Minimization and Avoidance Measures for Predator Control. Pūlama Lānaʻi will implement the following minimization and avoidance measures for its predator control activities: (1) Cat trap lines may be situated on the inside or outside of the perimeter fence, located to minimize interactions with waterbirds, while maintaining trapping efficacy. (2) Rat traps may be situated on the inside or outside of the perimeter fence. Traps which pose a potential source of Take (e.g. snap traps) will be enclosed in a box or other suitable structure that excludes water birds entirely, or in the case of A24 automatic rat traps, with an excluder that prevents them from accessing the inside of the trap. (3) Rodenticide may be used inside or outside the perimeter fence. All rodenticide use will follow United States Environmental Protection Agency (“EPA”) labeling for that rodenticide. Any rodenticide used will be deployed in containers that exclude waterbirds per EPA labeling instructions. Loose and/or hand broadcast rodenticides will not be used. (4) Fine mesh screen barrier will be installed on the perimeter fence at ground level to prevent entry of bullfrogs and cane toads. TMK 2-4-9-002-102 TMK 2-4-9-002-103 TMK 2-4-9-002-104 TMK 2-4-9-002-105 TMK 2-4-9-002-106 TMK 2-4-9-002-107 TMK 2-4-9-002-108 TMK 2-4-9-002-109 TMK 2-4-9-002-110 TMK 2-4-9-002-111 TMK 2-4-9-002-112 TMK 2-4-9-002-113 TMK 2-4-9-002-114 TMK 2-4-9-002-115 TMK 2-4-9-002-116 TMK 2-4-9-002117 TMK 2-4-9-002-119 TMK 2-4-9-003-010 TMK 2-4-9-003-023 TMK 2-4-9-003-027 TMK 2-4-9-004014 TMK 2-4-9-004-037 TMK 2-4-9-004-039 TMK 2-4-9-004-048 TMK 2-4-9-004-050 TMK 2-4-9-004-051 TMK 2-4-9-004-056 TMK 2-4-9-004-077 TMK 2-4-9-007-174 TMK 2-4-9-010-061 TMK 2-4-9-012-078 TMK 2-4-9-007-177 TMK 2-4-9-010-067 TMK 2-4-9-012-079 TMK 2-4-9-007-179 TMK 2-4-9-010-068 TMK 2-4-9-012-080 TMK 2-4-9-007-180 TMK 2-4-9-010-069 TMK 2-4-9-012-081 TMK 2-4-9-007-181 TMK 2-4-9-010-070 TMK 2-4-9-013-005 TMK 2-4-9-007-182 TMK 2-4-9-010-073 TMK 2-4-9-013-009 TMK 2-4-9-007-183 TMK 2-4-9-010-075 TMK 2-4-9-013-034 TMK 2-4-9-007-185 TMK 2-4-9-011-001 TMK 2-4-9-013-043 TMK 2-4-9-007-187 TMK 2-4-9-011-003 TMK 2-4-9-013-045 TMK 2-4-9-008-001 TMK 2-4-9-011-005 TMK 2-4-9-013-057 TMK 2-4-9-008-012 TMK 2-4-9-011-008 TMK 2-4-9-013-066 TMK 2-4-9-008-013 TMK 2-4-9-011-015 TMK 2-4-9-013-071 TMK 2-4-9-008-019 TMK 2-4-9-011-020 TMK 2-4-9-013-073 TMK 2-4-9-008-028 TMK 2-4-9-011-021 TMK 2-4-9-013-080 TMK 2-4-9-008-029 TMK 2-4-9-012-001 TMK 2-4-9-013-082 TMK 2-4-9-008-035 TMK 2-4-9-012-003 TMK 2-4-9-013-084 TMK 2-4-9-008-036 TMK 2-4-9-012-005 TMK 2-4-9-013-086 TMK 2-4-9-008-038 TMK 2-4-9-012-031 TMK 2-4-9-013-088 TMK 2-4-9-008-039 TMK 2-4-9-012-035 TMK 2-4-9-013-089 TMK 2-4-9-008-040 TMK 2-4-9-012-043 TMK 2-4-9-013-090 TMK 2-4-9-008-041 TMK 2-4-9-012-057 TMK 2-4-9-013-091 TMK 2-4-9-008-042 TMK 2-4-9-012-059 TMK 2-4-9-013-092 TMK 2-4-9-008-043 TMK 2-4-9-012-064 TMK 2-4-9-013-093 TMK 2-4-9-008-044 TMK 2-4-9-012-065 TMK 2-4-9-013-094 TMK 2-4-9-008-046 TMK 2-4-9-012-067 TMK 2-4-9-013-095 TMK 2-4-9-008-047 TMK 2-4-9-012-068 TMK 2-4-9-014-001 TMK 2-4-9-008-048 TMK 2-4-9-012-069 TMK 2-4-9-014-006 TMK 2-4-9-008-049 TMK 2-4-9-012-070 TMK 2-4-9-014-009 TMK 2-4-9-009-007 TMK 2-4-9-012-071 TMK 2-4-9-014-011 TMK 2-4-9-009-036 TMK 2-4-9-012-072 TMK 2-4-9-014-012 TMK 2-4-9-009-043 TMK 2-4-9-012-073 TMK 2-4-9-014-013 TMK 2-4-9-010-001 TMK 2-4-9-012-074 TMK 2-4-9-014-018 TMK 2-4-9-010-047 TMK 2-4-9-012-077 TMK 2-4-9-014-022 TMK 2-4-9-014-023 TMK 2-4-9-016-149 TMK 2-4-9-019-037 TMK 2-4-9-015-001 TMK 2-4-9-017-001 TMK 2-4-9-019-041 TMK 2-4-9-015-022 TMK 2-4-9-017-002 TMK 2-4-9-019-042 TMK 2-4-9-015-041 TMK 2-4-9-017-003 TMK 2-4-9-019-046 TMK 2-4-9-015-051 TMK 2-4-9-017-004 TMK 2-4-9-019-054 TMK 2-4-9-015-052 TMK 2-4-9-017-005 TMK 2-4-9-019-055 TMK 2-4-9-015-071 TMK 2-4-9-017-006-600 6002 TMK 2-4-9-019-066 TMK 2-4-9-015-072 TMK 2-4-9-017-008 TMK 2-4-9-019-068 TMK 2-4-9-015-073 TMK 2-4-9-017-009 TMK 2-4-9-019-071 TMK 2-4-9-015-077 TMK 2-4-9-017-010 TMK 2-4-9-019-073 TMK 2-4-9-015-079 TMK 2-4-9-017-011 TMK 2-4-9-019-087 TMK 2-4-9-016-001 TMK 2-4-9-017-022 TMK 2-4-9-019-095 TMK 2-4-9-016-002 TMK 2-4-9-017-023 TMK 2-4-9-019-102 TMK 2-4-9-016-008 TMK 2-4-9-017-024 TMK 2-4-9-019-104 TMK 2-4-9-016-009 TMK 2-4-9-017-025 TMK 2-4-9-017020-026 020 TMK 2-4-9-016-010 TMK 2-4-9-017-028 TMK 2-4-9-017-029 TMK 2-4-9-017-030 TMK 2-4-9-017-031 TMK 2-4-9-017-032 TMK 2-4-9-017-034 TMK 2-4-9-018-001 TMK 2-4-9-018-002 TMK 2-4-9-018-003 TMK 2-4-9-018-004 TMK 2-4-9-018-005 TMK 2-4-9-019-005 TMK 2-4-9-019-010 TMK 2-4-9-019-028 TMK 2-4-9-019-031 TMK 2-4-9-019-035 TMK 2-4-9-019-036 TMK 2-4-9-019-041 TMK 2-4-9-019-042 TMK 2-4-9-019-046 TMK 2-4-9-019-054 TMK 2-4-9-019-055 TMK 2-4-9-019-066 TMK 2-4-9-019-068 TMK 2-4-9-019-071 TMK 2-4-9-019-073 TMK 2-4-9-019-087 TMK 2-4-9-019-095 TMK 2-4-9-019-102 TMK 2-4-9-019-104 TMK 2-4-9-020-020 026 TMK 2-4-9-021-002-0001 TMK 2-4-9-016-011 TMK 2-4-9-017-028 TMK 2-4-9-021-002-0007 TMK 2-4-9-016-012 TMK 2-4-9-017-029 TMK 2-4-9-021-003 TMK 2-4-9-016-013 TMK 2-4-9-017-030 TMK 2-4-9-021-004-0003 TMK 2-4-9-016-019 TMK 2-4-9-017-031 TMK 2-4-9-021-004-0005 TMK 2-4-9-016-033 TMK 2-4-9-017-032 TMK 2-4-9-021-004-0011 TMK 2-4-9-016-035 TMK 2-4-9-017-034 TMK 2-4-9-021-004-0013 TMK 2-4-9-016-036 TMK 2-4-9-018-001 TMK 2-4-9-021-004-0016 TMK 2-4-9-016-042 TMK 2-4-9-018-002 TMK 2-4-9-021-004-0018 TMK 2-4-9-016-044 TMK 2-4-9-018-003 TMK 2-4-9-021-004-0019 TMK 2-4-9-016-046 TMK 2-4-9-018-004 TMK 2-4-9-021-004-0020 TMK 2-4-9-016-101 TMK 2-4-9-018-005 TMK 2-4-9-021-005 TMK 2-4-9-016-103 TMK 2-4-9-019-005 TMK 2-4-9-021-006 TMK 2-4-9-016-126 TMK 2-4-9-019-010 TMK 2-4-9-021-008 TMK 2-4-9-016-127 TMK 2-4-9-019-028 TMK 2-4-9-021-009 TMK 2-4-9-016-146 TMK 2-4-9-019-031 TMK 2-4-9-021-011 TMK 2-4-9-016-147 TMK 2-4-9-019-035 TMK 2-4-9-022-001 TMK 2-4-9-016-148 TMK 2-4-9-019-036 TMK 2-4-9-022-002-0004 TMK 2-4-9-022-005 TMK 2-4-9-023-006 TMK 2-4-9-023-021 TMK 2-4-9-022-023 TMK 2-4-9-023-007 TMK 2-4-9-023-022 TMK 2-4-9-023-001 TMK 2-4-9-023-008 TMK 2-4-9-023-023 TMK 2-4-9-023-002 TMK 2-4-9-023-009 TMK 2-4-9-023-025 TMK 2-4-9-023-003 TMK 2-4-9-023-010 TMK 2-4-9-023-005 TMK 2-4-9-023-011 The U.S. Fish and Wildlife Service (USFWS) recommends the following measures to be incorporated into project planning to avoid or minimize impacts to fish and wildlife resources. Best Management Practices (BMPs) include the incorporation of procedures or materials that may be used to reduce either direct or indirect negative impacts to aquatic habitats that result from project construction-related activities. These BMPs are recommended in addition to, and do not over-ride any terms, conditions, or other recommendations prepared by the USFWS, other federal, state or local agencies. If you have questions concerning these BMPs, please contact the USFWS Aquatic Ecosystems Conservation Program at ▇▇▇-▇▇▇-▇▇▇▇. 1. Authorized dredging and filling-related activities that may result in the temporary or permanent loss of aquatic habitats should be designed to avoid indirect, negative impacts to aquatic habitats beyond the planned project area. 2. Dredging/filling in the marine environment should be scheduled to avoid coral spawning and recruitment periods, and sea turtle nesting and hatching periods. Because these periods are variable throughout the Pacific islands, we recommend contacting the relevant local, state, or federal fish and wildlife resource agency for site specific guidance. 3. Turbidity and siltation from project-related work should be minimized and contained within the project area by silt containment devices and curtailing work during flooding or adverse tidal and weather conditions. BMPs should be maintained for the life of the construction period until turbidity and siltation within the project area is stabilized. All project construction-related debris and sediment containment devices should be removed and disposed of at an approved site. 4. All project construction-related materials and equipment (dredges, vessels, backhoes, silt curtains, etc.) to be placed in an aquatic environment should be inspected for pollutants including, but not limited to; marine fouling organisms, grease, oil, etc., and cleaned to remove pollutants prior to use. Project related activities should not result in any debris disposal, non-native species introductions, or attraction of non-native pests to the affected or adjacent aquatic or terrestrial habitats. Implementing both a litter-control plan and a Hazard Analysis and Critical Control Point plan (HACCP – see ▇▇▇▇▇://▇▇▇.▇▇▇.▇▇▇/policy/A1750fw1.html) can help to prevent attraction and introduction of non-native species. 5. Project construction-related materials (fill, revetment rock, pipe, etc.) should not be stockpiled in, or in close proximity to aquatic habitats and should be protected from erosion (e.g., with filter fabric, etc.), to prevent materials from being carried into waters by wind, rain, or high surf. 6. Fueling of project-related vehicles and equipment should take place away from the aquatic environment and a contingency plan to control petroleum products accidentally spilled during the project should be developed. The plan should be retained on site with the person responsible for compliance with the plan. Absorbent pads and containment booms should be stored on-site to facilitate the clean-up of accidental petroleum releases. 7. All deliberately exposed soil or under-layer materials used in the project near water should be protected from erosion and stabilized as soon as possible with geotextile, filter fabric or native or non-invasive vegetation matting, hydro-seeding, etc. ▇▇▇▇▇▇▇▇▇▇, K. 2020. Electronic mail message regarding Megalagrion xanthomelas on Maui. (August 5, 2020). 2 pp. ▇▇▇▇▇▇▇, ▇.▇. 1981. The reproductive biology of the Hawaiian subspecies of the black-necked stilt, Himantopus mexicanus knudseni. Ph.D. dissertation, Pennsylvania State University, PA. 106 pp. ▇▇▇▇, ▇.▇., and ▇.▇. ▇▇▇▇▇▇▇▇. 2003. Insects of Hawaii, Vol. 17: Hawaiian Hylaeus (Nesoprosopis) Bees (Hymenoptera: Apoidea). University of Hawaii Press, Honolulu. 234 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources, Division of Forestry and Wildlife. 2003. Title 13 Chapter 123 Rules Regulating Game Mammal Hunting. 56 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2015. Hawaiʻi State Wildlfie Action Plan. Prepared by ▇.▇. ▇▇▇▇▇▇ and Associates, Honolulu, HI 893 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2018. Commission on Water Resources Management. 06/20/18 – Decision on East Maui interim instream flow standards released. ▇▇▇▇▇://▇▇▇▇.▇▇▇▇▇▇.▇▇▇/blog/2018/06/20/nr18-116/. Last accessed September 27, 2022. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2020. Aquatic invasive species. ▇▇▇▇▇://▇▇▇▇.▇▇▇▇▇▇.▇▇▇/ais/. Last accessed July 10, 2020.

Minimization and Avoidance Measures for Predator Control. Pūlama Lānaʻi will implement the following minimization and avoidance measures for its predator control activities: (1) Cat trap lines may be situated on the inside or outside of the perimeter fence, located to minimize interactions with waterbirds, while maintaining trapping efficacy. (2) Rat traps may be situated on the inside or outside of the perimeter fence. Traps which pose a potential source of Take (e.g. snap traps) will be enclosed in a box or other suitable structure that excludes water birds entirely, or in the case of A24 automatic rat traps, with an excluder that prevents them from accessing the inside of the trap. (3) Rodenticide may be used inside or outside the perimeter fence. All rodenticide use will follow United States Environmental Protection Agency (“EPA”) labeling for that rodenticide. Any rodenticide used will be deployed in containers that exclude waterbirds per EPA labeling instructions. Loose and/or hand broadcast rodenticides will not be used. (4) Fine mesh screen barrier will be installed on the perimeter fence at ground level to prevent entry of bullfrogs and cane toads. TMK 2-4-9-002-102 TMK 2-4-9-002-103 TMK 2-4-9-002-104 TMK 2-4-9-002-105 TMK 2-4-9-002-106 TMK 2-4-9-002-107 TMK 2-4-9-002-108 TMK 2-4-9-002-109 TMK 2-4-9-002-110 TMK 2-4-9-002-111 TMK 2-4-9-002-112 TMK 2-4-9-002-113 TMK 2-4-9-002-114 TMK 2-4-9-002-115 TMK 2-4-9-002-116 TMK 2-4-9-002117 TMK 2-4-9-002-119 TMK 2-4-9-003-010 TMK 2-4-9-003-023 TMK 2-4-9-003-027 TMK 2-4-9-004014 TMK 2-4-9-004-037 TMK 2-4-9-004-039 TMK 2-4-9-004-048 TMK 2-4-9-004-050 TMK 2-4-9-004-051 TMK 2-4-9-004-056 TMK 2-4-9-004-077 TMK 2-4-9-017-001 TMK 2-4-9-017-002 TMK 2-4-9-017-003 TMK 2-4-9-017-004 TMK 2-4-9-017-005 TMK 2-4-9-017-006-600 6002 TMK 2-4-9-017-008 TMK 2-4-9-017-009 TMK 2-4-9-017-010 TMK 2-4-9-017-011 TMK 2-4-9-017-022 TMK 2-4-9-017-023 TMK 2-4-9-017-024 TMK 2-4-9-017-025 TMK 2-4-9-017-026 TMK 2-4-9-017-028 TMK 2-4-9-017-029 TMK 2-4-9-017-030 TMK 2-4-9-017-031 TMK 2-4-9-017-032 TMK 2-4-9-017-034 TMK 2-4-9-018-001 TMK 2-4-9-018-002 TMK 2-4-9-018-003 TMK 2-4-9-018-004 TMK 2-4-9-018-005 TMK 2-4-9-019-005 TMK 2-4-9-019-010 TMK 2-4-9-019-028 TMK 2-4-9-019-031 TMK 2-4-9-019-035 TMK 2-4-9-019-036 TMK 2-4-9-019-041 TMK 2-4-9-019-042 TMK 2-4-9-019-046 TMK 2-4-9-019-054 TMK 2-4-9-019-055 TMK 2-4-9-019-066 TMK 2-4-9-019-068 TMK 2-4-9-019-071 TMK 2-4-9-019-073 TMK 2-4-9-019-087 TMK 2-4-9-019-095 TMK 2-4-9-019-102 TMK 2-4-9-019-104 TMK 2-4-9-020-020 TMK 2-4-9-021-002-0001 TMK 2-4-9-021-002-0007 TMK 2-4-9-021-003 TMK 2-4-9-021-004-0003 TMK 2-4-9-021-004-0005 TMK 2-4-9-021-004-0011 TMK 2-4-9-021-004-0013 TMK 2-4-9-021-004-0016 TMK 2-4-9-021-004-0018 TMK 2-4-9-021-004-0019 TMK 2-4-9-021-004-0020 TMK 2-4-9-021-005 TMK 2-4-9-021-006 TMK 2-4-9-021-008 TMK 2-4-9-021-009 TMK 2-4-9-021-011 TMK 2-4-9-022-001 TMK 2-4-9-022-002-0004 The U.S. Fish and Wildlife Service (USFWS) recommends the following measures to be incorporated into project planning to avoid or minimize impacts to fish and wildlife resources. Best Management Practices (BMPs) include the incorporation of procedures or materials that may be used to reduce either direct or indirect negative impacts to aquatic habitats that result from project construction-related activities. These BMPs are recommended in addition to, and do not over-ride any terms, conditions, or other recommendations prepared by the USFWS, other federal, state or local agencies. If you have questions concerning these BMPs, please contact the USFWS Aquatic Ecosystems Conservation Program at ▇▇▇-▇▇▇-▇▇▇▇. 1. Authorized dredging and filling-related activities that may result in the temporary or permanent loss of aquatic habitats should be designed to avoid indirect, negative impacts to aquatic habitats beyond the planned project area. 2. Dredging/filling in the marine environment should be scheduled to avoid coral spawning and recruitment periods, and sea turtle nesting and hatching periods. Because these periods are variable throughout the Pacific islands, we recommend contacting the relevant local, state, or federal fish and wildlife resource agency for site specific guidance. 3. Turbidity and siltation from project-related work should be minimized and contained within the project area by silt containment devices and curtailing work during flooding or adverse tidal and weather conditions. BMPs should be maintained for the life of the construction period until turbidity and siltation within the project area is stabilized. All project construction-related debris and sediment containment devices should be removed and disposed of at an approved site. 4. All project construction-related materials and equipment (dredges, vessels, backhoes, silt curtains, etc.) to be placed in an aquatic environment should be inspected for pollutants including, but not limited to; marine fouling organisms, grease, oil, etc., and cleaned to remove pollutants prior to use. Project related activities should not result in any debris disposal, non-native species introductions, or attraction of non-native pests to the affected or adjacent aquatic or terrestrial habitats. Implementing both a litter-control plan and a Hazard Analysis and Critical Control Point plan (HACCP – see ▇▇▇▇▇://▇▇▇.▇▇▇.▇▇▇/policy/A1750fw1.html) can help to prevent attraction and introduction of non-native species. 5. Project construction-related materials (fill, revetment rock, pipe, etc.) should not be stockpiled in, or in close proximity to aquatic habitats and should be protected from erosion (e.g., with filter fabric, etc.), to prevent materials from being carried into waters by wind, rain, or high surf. 6. Fueling of project-related vehicles and equipment should take place away from the aquatic environment and a contingency plan to control petroleum products accidentally spilled during the project should be developed. The plan should be retained on site with the person responsible for compliance with the plan. Absorbent pads and containment booms should be stored on-site to facilitate the clean-up of accidental petroleum releases. 7. All deliberately exposed soil or under-layer materials used in the project near water should be protected from erosion and stabilized as soon as possible with geotextile, filter fabric or native or non-invasive vegetation matting, hydro-seeding, etc. ▇▇▇▇▇▇▇▇▇▇, K. 2020. Electronic mail message regarding Megalagrion xanthomelas on Maui. (August 5, 2020). 2 pp. ▇▇▇▇▇▇▇, ▇.▇. 1981. The reproductive biology of the Hawaiian subspecies of the black-necked stilt, Himantopus mexicanus knudseni. Ph.D. dissertation, Pennsylvania State University, PA. 106 pp. ▇▇▇▇, ▇.▇., and ▇.▇. ▇▇▇▇▇▇▇▇. 2003. Insects of Hawaii, Vol. 17: Hawaiian Hylaeus (Nesoprosopis) Bees (Hymenoptera: Apoidea). University of Hawaii Press, Honolulu. 234 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources, Division of Forestry and Wildlife. 2003. Title 13 Chapter 123 Rules Regulating Game Mammal Hunting. 56 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2015. Hawaiʻi State Wildlfie Action Plan. Prepared by ▇.▇. ▇▇▇▇▇▇ and Associates, Honolulu, HI 893 pp. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2018. Commission on Water Resources Management. 06/20/18 – Decision on East Maui interim instream flow standards released. ▇▇▇▇▇://▇▇▇▇.▇▇▇▇▇▇.▇▇▇/blog/2018/06/20/nr18-116/. Last accessed September 27, 2022. [DLNR] State of Hawaiʻi Department of Land and Natural Resources. 2020. Aquatic invasive species. ▇▇▇▇▇://▇▇▇▇.▇▇▇▇▇▇.▇▇▇/ais/. Last accessed July 10, 2020.