2007 Annual Monitoring Report (pdf 16MB) - Bolsa Chica Lowlands ...

2007 Annual Monitoring Report (pdf 16MB) - Bolsa Chica Lowlands ... 2007 Annual Monitoring Report (pdf 16MB) - Bolsa Chica Lowlands ...

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Bolsa Chica Lowlands Restoration Monitoring2007 Annual ReportBOLSA CHICA LOWLANDS RESTORATION PROJECTMonitoring ProgramAnnual Report - 2007Monitoring Year 1EXECUTIVE SUMMARYThe construction phases of the Bolsa Chica Lowlands Restoration Project were principally completeby the end of 2006, including the opening of the Full Tidal Basin (FTB) to the ocean in August 2006.The biological and physical monitoring program began in December 2006. While data collected todate represents only one year of sampling since project implementation, some general trends can beidentified and preliminary conclusions can be drawn.As anticipated, natural processes are shaping the system and the first year post-opening has been aperiod of substantial morphologic adjustment as the system seeks an equilibrium state. Shorelines andflats are smoothing while steeper slopes have experienced minor to major erosion. Major areas oferosion and accretion have been identified within the FTB, with the greatest areas of change occurringin areas of flood shoal sandbar formation within the maintenance dredging area near the ocean inletand some slope erosion requiring additional rock stabilization.The delay in opening the Muted Tidal Basins (MTBs) has precluded the beginning of tidal wetlanddevelopment in these areas. As a result, it is expected that the next monitoring year will yieldadditional early developmental conditions as these basins are opened to tidal influence.The biological, physical, and beach monitoring programs reported in this first annual report wereconducted following the Bolsa Chica Lowland Restoration Project Biological Monitoring and FollowupPlan and the Bolsa Chica Lowlands Restoration Project Beach Monitoring Plan, both prepared bythe U.S. Fish and Wildlife Service in 2001. The monitoring team included Merkel & Associates,Moffat & Nichol Engineers, Coastal Frontiers, and Chambers Group, Inc. The findings aresummarized in the following sections.WATER QUALITYWater quality monitoring was performed in October 2007 using both tended and untended continuousrecording instrumentation to coincide with biological sampling periods. The deployed units wereprogrammed to log water depth (m), temperature (C), dissolved oxygen (DO)(mg/L), turbidity (NTU),and salinity (ppt) at 20-minute intervals from October 10 to November 10, 2007 at two stations withinthe Full Tidal Basin.During the monitoring period mean water temperatures were 18.3C at Station 1 (northernmost stationfurthest from the ocean inlet) and 17.1C at Station 2 (southernnmost station nearer the ocean inlet).Salinity was similar at both stations, with a mean of 33.4 ppt at Station 1 and 33.1 ppt at Station 2. Ingeneral, turbidity at both stations was very similar, with an average reading of about 8 NTU.Dissolved oxygen at Station 1 ranged from 4.7 to 9.5 mg/L, with a mean of 7.0 mg/L. Acceptabledissolved oxygen data at Station 2 were not obtained due to probe fouling or failure.Merkel & Associates, Inc. 1

Bolsa Chica Lowlands Restoration Monitoring2007 Annual ReportThe water quality conditions observed in the FTB during this first quarter of monitoring show the tidalmarine influence that now exists in the basin, reflecting the daily and monthly tidal fluctuations seen inthe open ocean. All parameters were well within acceptable ranges to support the developing fish,invertebrate, and vegetation communities, and are indicative of a well-flushed marine environment.No changes are recommended to the water quality monitoring program at this time.VEGETATION/HABITATThe distribution, composition, and evolution of vegetation communities and unvegetated habitats arebeing monitored through the use of aerial photography and quantitative transect methods. The January2007 assessment of habitats at Bolsa Chica mapped eight vegetated and seven non-vegetated habitatswithin the 402-hectare (994-acre) study area. Vegetated habitats included: southern coastal salt marsh,disturbed coastal salt marsh, mule fat scrub, coastal sage scrub, freshwater marsh, southern arroyowillow riparian forest, decaying/transitional vegetation, and non-native vegetation. Non-vegetatedhabitats included: salt panne, disturbed salt panne, intertidal sand shoal, intertidal mudflat, open water,unvegetated nest site, and urban/developed.Cordgrass and eelgrass were transplanted throughout the FTB in August 2007. The cordgrass isanticipated to establish on the broad intertidal mudflats on the eastern shore to the FTB while eelgrassis expected to colonize much of the subtidal areas of the FTB. If patterns of expansion follow thoseobserved in other large-scale restorations, the ultimate expansion from the introduced patches isexpected to be slow at first with much more rapid expansion both vegetatively and through seedlingrecruitment around the third year following initial tidal restoration.The present vegetation monitoring has been used to establish a baseline. The first full vegetationmonitoring event, including aerial photography, habitat mapping, transect surveys, and soil analysis,will be conducted in summer 2008 (Year 2) as called for in the Monitoring Plan.Continued collection of aerial imagery each year (rather than in Years 2, 5, and 10 only) isrecommended, to track changes in water levels, site conditions, and habitat development over time.FISH COMMUNITYFish community sampling was initiated in monitoring Year 2 with the first sampling occurring inOctober 2007. Sampling was performed during daylight hours at three stations: Stations 1 (furthestfrom the ocean) and 2 (closest to the ocean) in the FTB, and one in the Muted Pocket Marsh (MPM).Sampling equipment used included an otter trawl, purse seine, and beach seine in the FTB and a beachseine only in the MPM. Captured fish were identified, counted, measured, and weighed. Physicalwater quality parameters were measured coincident with the fish sampling efforts.A total of 4,426 individual fish were captured in October 2007. The catch represented 18 species offish, from 14 families. At Station 1, a total of 2,185 fish, represented by 15 species, were captured.The mean density across gear types at Station 1 was 0.52 individuals/m 2 . Topsmelt (Atherinopsaffinis) and juvenile anchovy (Anchoa sp.) comprised 95% of the fish captured. At Station 2,considerably fewer fish were captured, with a total of 845 fish represented by 12 species. The meandensity across gear types at Station 2 was 0.19 individuals/m 2 . Topsmelt were again the most abundantfish, accounting for 92% of the total catch. Only three species were captured in the MPM: topsmelt,Merkel & Associates, Inc. 2

<strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong> Restoration <strong>Monitoring</strong><strong>2007</strong> <strong>Annual</strong> <strong>Report</strong>The water quality conditions observed in the FTB during this first quarter of monitoring show the tidalmarine influence that now exists in the basin, reflecting the daily and monthly tidal fluctuations seen inthe open ocean. All parameters were well within acceptable ranges to support the developing fish,invertebrate, and vegetation communities, and are indicative of a well-flushed marine environment.No changes are recommended to the water quality monitoring program at this time.VEGETATION/HABITATThe distribution, composition, and evolution of vegetation communities and unvegetated habitats arebeing monitored through the use of aerial photography and quantitative transect methods. The January<strong>2007</strong> assessment of habitats at <strong>Bolsa</strong> <strong>Chica</strong> mapped eight vegetated and seven non-vegetated habitatswithin the 402-hectare (994-acre) study area. Vegetated habitats included: southern coastal salt marsh,disturbed coastal salt marsh, mule fat scrub, coastal sage scrub, freshwater marsh, southern arroyowillow riparian forest, decaying/transitional vegetation, and non-native vegetation. Non-vegetatedhabitats included: salt panne, disturbed salt panne, intertidal sand shoal, intertidal mudflat, open water,unvegetated nest site, and urban/developed.Cordgrass and eelgrass were transplanted throughout the FTB in August <strong>2007</strong>. The cordgrass isanticipated to establish on the broad intertidal mudflats on the eastern shore to the FTB while eelgrassis expected to colonize much of the subtidal areas of the FTB. If patterns of expansion follow thoseobserved in other large-scale restorations, the ultimate expansion from the introduced patches isexpected to be slow at first with much more rapid expansion both vegetatively and through seedlingrecruitment around the third year following initial tidal restoration.The present vegetation monitoring has been used to establish a baseline. The first full vegetationmonitoring event, including aerial photography, habitat mapping, transect surveys, and soil analysis,will be conducted in summer 2008 (Year 2) as called for in the <strong>Monitoring</strong> Plan.Continued collection of aerial imagery each year (rather than in Years 2, 5, and 10 only) isrecommended, to track changes in water levels, site conditions, and habitat development over time.FISH COMMUNITYFish community sampling was initiated in monitoring Year 2 with the first sampling occurring inOctober <strong>2007</strong>. Sampling was performed during daylight hours at three stations: Stations 1 (furthestfrom the ocean) and 2 (closest to the ocean) in the FTB, and one in the Muted Pocket Marsh (MPM).Sampling equipment used included an otter trawl, purse seine, and beach seine in the FTB and a beachseine only in the MPM. Captured fish were identified, counted, measured, and weighed. Physicalwater quality parameters were measured coincident with the fish sampling efforts.A total of 4,426 individual fish were captured in October <strong>2007</strong>. The catch represented 18 species offish, from 14 families. At Station 1, a total of 2,185 fish, represented by 15 species, were captured.The mean density across gear types at Station 1 was 0.52 individuals/m 2 . Topsmelt (Atherinopsaffinis) and juvenile anchovy (Anchoa sp.) comprised 95% of the fish captured. At Station 2,considerably fewer fish were captured, with a total of 845 fish represented by 12 species. The meandensity across gear types at Station 2 was 0.19 individuals/m 2 . Topsmelt were again the most abundantfish, accounting for 92% of the total catch. Only three species were captured in the MPM: topsmelt,Merkel & Associates, Inc. 2

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