2008 Annual Monitoring Report (pdf 10.9MB) - Bolsa Chica ...
2008 Annual Monitoring Report (pdf 10.9MB) - Bolsa Chica ... 2008 Annual Monitoring Report (pdf 10.9MB) - Bolsa Chica ...
Bolsa Chica Lowlands Restoration Monitoring 2008 Annual Report Table 1-2 also summarizes the total number of native and non-native species found within one meter on either side of the transect line. The salt marsh in the MPM was by far the most diverse of all the areas surveyed, followed by Rabbit Island. One species was found in the 2-m belt that was not detected on any transect: western sea purslane (Sesuvium verrucosum) along transect MPM2. As noted above the marshes in the MTBs are low in diversity, supporting primarily S. pacifica and D. spicata. The FTB transects were primarily unvegetated in 2008, with the exception of a small amount of S. pacifica becoming established at the north end of the basin at FTB North and considerable growth of R. maritima on the intertidal mudflats on the east shore of the FTB. Although not captured in the transect monitoring, there was a narrow band of S. pacifica seedlings that had established on the large mudflats of the eastern shore of the FTB (cordgrass bench) near the base of the riprap. In some cases the pickleweed extended out as far as 30 m onto the mudflat from the riprap. Also of note, though not captured in the transect monitoring, was the persistence of the rare coastal dune plant coast woolly heads (Nemacaulis denudata var. denudata) on Rabbit Island. The restoration project aimed to protect this species at the highest elevations of Rabbit Island through removal of hottentot fig during the project and by preserving the dune areas about the highest tides in the project design. A comprehensive survey for this species was not conducted, however four patches covering approximately 50m 2 in total were mapped incidentally during the survey work on the island. Hottentot fig was encroaching on the remaining patches of woolly heads and immediate intervention through removal of the non-native will be critical to the survival of woolly heads at Bolsa Chica. The scars from the construction grading of the cordgrass bench were still evident in 2008 and created pools of standing water at low tide, which had heavy growth of R. maritima in them. An interesting observation was made by Peter Knapp of a snowy plover foraging for small fish in these pools, an unusual behavior for this bird. The bench showed signs of growing maturity with the natural development of tidal channels at the edges of the bench. Pickleweed seedlings, Ruppia maritima, and channel development on the mudflats of the eastern shore of the FTB. The photos taken at each of the nineteen transects will be presented following the next monitoring event in series to illustrate change over time. Discussion The 2008 vegetation monitoring at Bolsa Chica was the first full monitoring event to document habitat distribution and species composition following the restoration. Coastal salt marsh was the most abundant vegetated habitat and changes in its distribution will be tracked in the coming years, since its availability is critical for nesting by Belding’s Savannah sparrow. In 2008, only the west MTB was open to tidal influence and the marsh had had limited time to respond prior to the monitoring. It is Merkel & Associates, Inc. 31
Bolsa Chica Lowlands Restoration Monitoring 2008 Annual Report anticipated that this basin and the central and east MTBs will have shifts in marsh distribution in the coming years as all basins are opened to the FTB. The lowest lying areas will be converted to open water and mudflat, while marsh will be able to expand into areas previously dominated by non-native weeds once they are eliminated by the salt water influence. The MTBs were designed to support 51.1 ha (126.3 acres) of salt marsh habitat. In 2008 the three basins had a total of 49.8 ha (122.9 acres) of coastal salt marsh and disturbed coastal salt marsh. An unanticipated benefit of the restoration work in the MTBs was the placement of the sidecast excavated material from tidal channel creation (described above as disturbed coastal salt marsh). These mounds have been smoothed by weather and standing water in most areas and are gradually becoming vegetated at their base with pickleweed. The elevated mounds serve as a refuge from tidal inundation and are heavily used at high tide or during periods of heavy rainfall accumulation by loafing shorebirds. They are also used by Belding’s Savannah sparrow’s as elevated perch points, and as they become vegetated will likely provide additional nesting habitat at Hundreds of shorebirds loafing on sediment mounds in flooded marsh in the central MTB. elevations safe from tidal inundation. Their vegetation by salt marsh will also help to offset losses of pickleweed at lower elevations due to the introduction of tidal influence. Because these mounds are comprised only of the sidecast material from channel excavations, they do not have a consequential effect on the hydrology of the MTBs, but add a valuable habitat element. Salt marsh distribution is also expected to change on Rabbit Island as low-lying marsh continues to convert to mudflat. The FTB was designed to eventually support 7.7ha (19.1 acres) of pickleweed. In 2008, approximately 4.9 ha (12.4 acres) of coastal salt marsh were present in the basin, including Rabbit Island. Salt marsh will be gained at the higher elevations as non-native vegetation continues to convert to mid and high marsh. Pickleweed on the cordgrass bench in the FTB may continue to fill in along the base of the riprap in the coming years as well. The transplant of cordgrass in the FTB was intended to accelerate the development of low salt marsh habitat, with the goal of providing suitable habitat for light-footed clapper rails (Rallus longirostris levipes). In 2008, one year post-transplant, the majority of the transplant sites had persisted. By December 2007, four months post-transplant, most of the planted shoots had senesced and fallen over, so all shoots mapped and measured in 2008 were new growth. Although only 196 m 2 of cordgrass were mapped in 2008 (in comparison to the 3,000 m 2 area that was planted), the cordgrass had expanded within each transplant to become denser, and was healthy, flowering, and dispersing seed. The slow establishment is typical of cordgrass transplants, but may have been exacerbated by the prolonged inundation periods that resulted from tidal muting as the flood shoal in the FTB inlet increased in size, restricting low tide drainage (see Appendix 2-A). Dredging scheduled for January 2009 will improve tidal range and reduce inundation periods at the elevations where the cordgrass was planted. It is likely that cordgrass at slightly higher elevations on the cordgrass bench will be more successful. Based on the establishment and expansion rates seen in a similar transplant conducted at Batiquitos Lagoon, it is expected that the cordgrass will begin to form continuous patches suitable as habitat within four to five years of transplant (M&A 2009). Merkel & Associates, Inc. 32
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<strong>Bolsa</strong> <strong>Chica</strong> Lowlands Restoration <strong>Monitoring</strong><br />
<strong>2008</strong> <strong>Annual</strong> <strong>Report</strong><br />
Table 1-2 also summarizes the total number of native and non-native species found within one meter<br />
on either side of the transect line. The salt marsh in the MPM was by far the most diverse of all the<br />
areas surveyed, followed by Rabbit Island. One species was found in the 2-m belt that was not<br />
detected on any transect: western sea purslane (Sesuvium verrucosum) along transect MPM2. As noted<br />
above the marshes in the MTBs are low in diversity, supporting primarily S. pacifica and D. spicata.<br />
The FTB transects were primarily unvegetated in <strong>2008</strong>, with the exception of a small amount of S.<br />
pacifica becoming established at the north end of the basin at FTB North and considerable growth of<br />
R. maritima on the intertidal mudflats on the east shore of the FTB.<br />
Although not captured in the transect monitoring, there was a narrow band of S. pacifica seedlings that<br />
had established on the large mudflats of the eastern shore of the FTB (cordgrass bench) near the base<br />
of the riprap. In some cases the pickleweed extended out as far as 30 m onto the mudflat from the<br />
riprap. Also of note, though not captured in the transect monitoring, was the persistence of the rare<br />
coastal dune plant coast woolly heads (Nemacaulis denudata var. denudata) on Rabbit Island. The<br />
restoration project aimed to protect this species at the highest elevations of Rabbit Island through<br />
removal of hottentot fig during the project and by preserving the dune areas about the highest tides in<br />
the project design. A comprehensive survey for this species was not conducted, however four patches<br />
covering approximately 50m 2 in total were mapped incidentally during the survey work on the island.<br />
Hottentot fig was encroaching on the remaining patches of woolly heads and immediate intervention<br />
through removal of the non-native will be critical to the survival of woolly heads at <strong>Bolsa</strong> <strong>Chica</strong>.<br />
The scars from the construction grading of the cordgrass bench were still evident in <strong>2008</strong> and created<br />
pools of standing water at low tide, which had heavy growth of R. maritima in them. An interesting<br />
observation was made by Peter Knapp of a snowy plover foraging for small fish in these pools, an<br />
unusual behavior for this bird. The bench showed signs of growing maturity with the natural<br />
development of tidal channels at the edges of the bench.<br />
Pickleweed seedlings, Ruppia maritima, and channel development on the mudflats of the eastern shore of the FTB.<br />
The photos taken at each of the nineteen transects will be presented following the next monitoring<br />
event in series to illustrate change over time.<br />
Discussion<br />
The <strong>2008</strong> vegetation monitoring at <strong>Bolsa</strong> <strong>Chica</strong> was the first full monitoring event to document habitat<br />
distribution and species composition following the restoration. Coastal salt marsh was the most<br />
abundant vegetated habitat and changes in its distribution will be tracked in the coming years, since its<br />
availability is critical for nesting by Belding’s Savannah sparrow. In <strong>2008</strong>, only the west MTB was<br />
open to tidal influence and the marsh had had limited time to respond prior to the monitoring. It is<br />
Merkel & Associates, Inc. 31