The First Annual IEP Monitoring
Survey of the Chinese Mitten Crab in the Delta and Suisun Marsh
Tanya Veldhuizen,
CDFG
The
Chinese mitten crab, Eriocheir sinensis, native to coastal rivers
and estuaries of China and Korea along the Yellow Sea (Panning
1938), was first discovered in South San Francisco Bay in 1992 and
quickly spread throughout the estuary during the next several years. Mitten
crabs were first collected in San Pablo Bay in the fall of 1994, in Suisun
Marsh in February 1996, and in the Sacramento-San Joaquin Delta in August
1996 (Hieb 1997). The current known distribution of
the Chinese mitten crab in the Delta extends north up the Sacramento River
to the Port of Sacramento, east to Stockton (Fourteenmile
Slough), and south to Fabian and Bell Canal. The crab is also distributed
throughout Suisun Marsh. We expect the known distribution to expand this
fall as emigrating adult crabs continue to be incidently caught by fishermen.
This
summer was a pilot year for implementing an annual monitoring program for
juvenile mitten crabs in Suisun Marsh and the Delta. The 45 adult crabs
collected last fall and winter in the Delta, Suisun Marsh and Suisun Bay
indicated the population in the northern estuary was large enough to be
detected by monitoring. Because the juvenile crab’s diet is comprised mainly
of vegetation, capturing them with baited traps was not feasible. Instead,
juvenile crabs were excavated from the burrows they dig for protection
from predators and desiccation during low tide (Panning 1938).
After
surveying the Delta and Suisun Marsh for potential sites in late June and
early July, 15 monitoring stations were selected based on several criteria:
sites had to be tidally influenced, contain adequate expanses of unrocked
bank exposed during low tide, and be accessible by vehicle. We attempted
to select stations to achieve an even distribution throughout the Delta
and Marsh, but due to large expanses of riprapped bank or inaccessibility,
portions of the Delta may be under represented.
Currently,
there are 4 stations in Suisun Marsh and 11 in the Delta, of which 8 are
core stations and 3 are peripheral stations. Core stations are sampled
twice a year separated by 4 weeks. Peripheral stations are sampled once
a year, and represent the upstream limit of where juvenile mitten crabs
can be expected to burrow.
Each
station was surveyed during low tide when the bank was exposed. We searched
for mitten crabs along a 5 meter transect paralleling the bank and extending
from the water line to the high tide line or to the top of the bank. The
transect height was measured at 1 meter intervals and the average height
was used to determine the total area of the transect. For core stations,
the second transect was placed within 0.25 miles from the first transect,
preferably adjacent to the original. Transect searches involved excavating
all cavities, such as burrows and rotted root tunnels, and examining all
debris, driftwood, rootwads, and ponded water for mitten crabs.
Carapace
length and width at the widest point were measured for all crabs. Crabs
larger than 9 mm were sexed and all were returned to the same location
where captured. Additional information recorded included vegetation and
soil types, bank profile, water salinity and temperature, and tidal phase.
Sampling
began in late July and continued through early September. Average densities
were highest at the Suisun Marsh stations (Figure
1). Of the 4 stations surveyed in the Marsh, Denverton Slough
had the highest average density of 3.07 crabs/m2 and Montezuma Slough had
the lowest average density of 0.55 crabs/m2. During the second survey,
densities increased at the Montezuma and Denverton Slough stations and
decreased at the Suisun and Hill Slough stations. The mean carapace width
(cw) was 15.3 mm for both surveys (n=25,
survey 1, n=36, survey 2). The salinity ranged from 4.4 to 7.2 ‰,
with the highest salinity at the Denverton Slough station on both surveys.
Crabs
were found at only 4 of the 8 core stations in the Delta (Figure
1). Average densities were relatively low, ranging from 0.31
crabs/m2 in Middle River near the railroad tracks on Jones Tract to 0.13
crabs/m2 in Fabian and Bell Canal at Tracy Oasis Marina. The mean size
was also 15.3 mm cw (n=11); all crabs were collected
from freshwater. Densities at all 4 of these Delta stations declined to
zero on the second survey. No crabs were found at the peripheral stations.
Juvenile
crab densities in the Delta and Suisun Marsh are significantly less than
those reported in South San Francisco Bay sloughs. Average densities for
1997 in South Bay sloughs ranged from 3.38 crabs/m2 to 6.31 crabs/m2 in
July and from 5.02 crabs/m2 to 15.87 crabs/m2 in August (Diana
Theriault, UC Berkeley, personal communication). Previously, a maximum
density of 30 crabs/m2 was reported (Halat 1997).
Both
the State and Federal water project pumping plants collected the first
juvenile mitten crabs this summer. The Skinner Fish Facility (DWR)
caught one crab of 29 mm cw in August. The Tracy Fish Collection Facility
(USBR) captured juvenile crabs in the holding tanks
beginning in late June. Mean size of age-0 juveniles was 15.0 mm cw in
June (n=1), 17.6 mm in July (n=21),
23.2 mm in August (n=13), and 31.0 mm in September
(n=7). Additional crabs, which were determined to
be age-1 or age-2, were collected in July, August and September. These
totals represent only a small fraction of crabs located at the pumps. Only
the crabs caught during the periodic 10 minute counts were saved; others
were salvaged with the fish without being counted. Also, the fish facility
crews reported finding crabs in the floating debris caught against the
screens and among the louver structures.
The
IEP will continue to monitor juvenile mitten crabs in the Delta and Suisun
Marsh annually. Sampling will occur in July and August, the peak migration
period of juvenile crabs to brackish and freshwater rearing areas. We plan
to add several more stations in the Delta, including additional core stations
in Central and West Delta and a peripheral station in the southeast Delta.

Acknowledgments:
I thank Anna Holmes and Jennifer Osmondson
of CDFG for their assistance in field collections and developing sampling
procedures; Kathy Hieb for the opportunity to collaborate on the design
and implementation of a biological study; USBR personnel at the Tracy Fish
Collection Facility and CDFG personnel at the Skinner Fish Facility for
crab collections; Kathleen Halat of Wetlands Research Associates and Diana
Theriault of UC Berkeley for guidance on sampling protocol and sharing
data; Dave Feliz of Grizzly Island Wildlife Area and Bay-Delta Division
personnel who provided valuable advice on locations of potential monitoring
sites; and Paul Raquel, Tracy Oasis Marina, and Windmill Cove for access
to their property. This work is part of the Green and Mitten Crab Studies,
which is funded and supported by the Interagency Ecological Program.

Literature Cited:
Halat, K. M. 1997. The distribution and
abundance of the Chinese mitten crab (Eriocheir sinensis)
in southern San Francisco Bay, 1995-1996. M.S. Thesis, University of California,
Berkeley, 80 pp.
Hieb, K. 1997. Chinese mitten crabs in the
Delta. IEP Newsletter, Vol. 10, No. 1-Winter 1997.
Panning, A. 1938. The Chinese mitten crab.
Annual Report Smithsonian Institution, pp 361-375.
Figure 1. Average densities of juvenile
Chinese mitten crabs in the Delta and Suisun Marsh, summer 1997.