Overview

Distribution

Range Description

Graptemys flavimaculata is confined to the Pascagoula River system, including the Leaf, Chickasawhay, and Escatawpa rivers, in southern Mississippi. The Leaf and Chickasawhay Rivers merge to form the Pascagoula; the Escatawpa is a tributary which joins the lower Pascagoula just before its estuary (USFWS 1993). The total range comprises less than 760 km of river [Pascagoula = 130 km, Leaf = 290 km, Chickasawhay = 340 km, but not all of this area is occupied: see the 'Population' section].

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Geographic Range

Graptemys flavimaculata are only found in the Pascagoula River drainage, occurring in the Pascagoula, Leaf,

and Chickasawhay Rivers in southern Mississippi in the United States. Based on mark and recapture studies, the U.S. Fish and Wildlife Service and Mississippi Department of Wildlife, Fisheries and Parks biologists estimated the population at 336 individuals per mile in the lower Pascagoula River, while basking studies on the upper Pascagoula, Leaf and Chickasawhay rivers revealed an average of four turtles per mile (USFWS 1992).

Biogeographic Regions: nearctic (Native )

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endemic to a single state or province

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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: (5000-20,000 square km (about 2000-8000 square miles)) Pascagoula River system, including the Leaf, Chickasawhay, and Escatawpa rivers, southern Mississippi. Apparently most abundant in Pascagoula River beteeen Wade and Vancleave, Mississippi (USFWS 1990). The largest population is in the Pascagoula River in Jackson County, mainly in the Ward Bayou Wildlife Management Area (Horne et al. 2003).

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Continent: North-America
Distribution: USA (Pascagoula River system in Mississippi, introduced to Florida)  
Type locality: Pascagoula River, 13 miles S.W. of Lucedale, George Co., Mississippi.
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Historic Range:
U.S.A. (MS)

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Physical Description

Morphology

Physical Description

Graptemys flavimaculata, an aquatic turtle species, has very pronounced sexual dimorphism in body size. The larger adult females measure between 14.9-18.0 cm, whereas the adult males measure between 6.7-11.0 cm. They are small, narrow-headed turtles with a serrated posterior carapacial margin, and laterally compressed spinelike vertebral projections. The spines are a major characteristic of adult males and juveniles but are less noticeable in females. The carapace is olive to light brown in color, with each costal scute marked by a bright yellow or orange blotch. The shape of this blotch varies from a bar to a semicircle, or a complete circle. The marginal plates have orange bars or semicircular patterns that open posteriorly. The hingeless plastron is light cream in color, with a black pattern extending along the seams. These black markings fade with age. The head of yellow-blotched map turtles is small to moderate in size with a nonprojecting snout and has neither hook nor notch on the upper jaw. The skin is olive colored with yellow stripes. Overall, yellow stripes can be found on the head, neck, legs, and tail. A yellow triangle or spot is common behind the eye. Generally, the yellow color dominates throughout the body of Graptemys flavimaculata (Ernst et al.1994; Barbour 1989).

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Size

Length: 18 cm

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Diagnostic Description

See McCoy and Vogt (1994) for a key to species in the genus Graptemys.

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology

Graptemys flavimaculata is exclusively riverine and inhabits mainly sunny river sections with moderate to strong current, abundant sand bars, and abundant deadwood basking sites.

Males and juveniles feed predominantly on insects and freshwater sponge fragments, while females consume mainly molluscs and sponges (Seigel and Brauman 1994 in Ernst and Lovich 2009).

Females may reach up to 19 cm carapace length (CL) at an average weight of 1.13 kg; males grow up to 11 cm CL at an average of 154 g weight. Females reach maturity at about 15 cm CL (Cagle 1954, Horne et al. 2003) at an estimated age of 8–10 years, while males were estimated to mature at 3–4 years (USFWS 1993). Mature females produce clutches averaging 4.7 eggs (range 3–9), and few females (16%) produce a second clutch in a year, while apparently many females skip reproduction for one or more years (Horne et al. 2003); in captivity, reproductive output is significantly higher, with females averaging 3.3 clutches of 3.4 eggs annually (Goode 1997). Generation time is unknown but at (female) age of first maturity over eight years, and exceptionally low rate of reproductive output, is probably more than 20 years.


Systems
  • Terrestrial
  • Freshwater
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Habitat

Graptemys flavimaculata usually live in sand and clay bottomed streams with moderate to rapid currents, and several hours of sun penetration daily. Piles of brush and debris provide basking locations, and tangled roots provide shelter. (Barbour 1989; USFWS 1992).

Aquatic Biomes: rivers and streams

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Comments: River sections with moderate current, sand and clay bottom with many sand bars, or rocky bottom with limestone ledges along banks (less abundant in rocky areas). Most abundant in areas with tangled tree roots and logs in water (basking sites). Needs river wide enough to allow several hours of sunshine daily. Also uses oxbow lakes, semi-permanent ponds, and occasionally temporary flood pools (Jones 1996). Nests on sandbars or in small clearings along bank of river such as on a clay bank with a steep slope, usually 1-17 m (mean 8 m) from water (Horne et al. 2003).

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Migration

Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.

Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: No. No populations of this species make annual migrations of over 200 km.

In southeastern Mississippi, some were relatively sedentary but others moved seasonally (related to reproduction, feeding, or avoidance of increased currents in winter) (Jones 1996).

In Mississippi, mean male home range area was 1.12 ha, mean home range length was 1.8 km; these values for females were 5.75 ha and 1.5 km (difference is not significant) (Jones 1996).

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Trophic Strategy

Food Habits

Graptemys flavimaculata eat insect larvae and mollusks, and it has been speculated that there may be a sexual difference in feeding preference in this species as in other map turtles (Ernst et al. 1994; George 1991).

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Comments: Primary diet consists of snails and insects.

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Population Biology

Number of Occurrences

Note: For many non-migratory species, occurrences are roughly equivalent to populations.

Estimated Number of Occurrences: 1 - 20

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Global Abundance

2500 - 100,000 individuals

Comments: Total adult population size is unknown but likely is at least a few thousand. Forty-four individuals were sighted in a one-year study in 1979. In the 1990s, In the 1990s, Horne et al. (2003) marked more than 1,100 individuals at a site along the Pascagoula River.

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General Ecology

Incurs a high level of nest mortality as a result of river flooding and predation by fish crow and other animals (90% mortality in some years) (Horne et al. 2003).

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Life History and Behavior

Cyclicity

Comments: Active throughout the year in southeastern Mississippi (Jones 1996).

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Reproduction

Reproduction

The reproductive habits of Graptemys flavimaculata are poorly studied. During courtship, male and female attempt to stroke one another's heads with their claws while facing each other (Wahlquist 1970, cited in Ernst et al. 1994). Nesting occurs in the sand and gravel bars adjacent to the rivers in which these turtles occur (USFWS 1992). It is believed that Graptemys flavimaculata have a similar reproductive pattern to other related Graptemys species which reach reproductive maturity between the ages of 6 to 9 years. They produce 3-4 clutches of eggs with 5-7 eggs per clutch (Champie 1998) .

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Nests from mid- to late May through early to mid-August; clutch size 3-9 (mean 4.7); at least some adult females are not reproductive each year; most adult females apparently do not produce more than one clutch per reproductive year (Horne et al. 2003). Males are sexually mature in 3-4 years (or reportedly in second growing season), females later (perhaps at 6-9 years) (Behler and King 1979, USFWS 1990).

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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Graptemys flavimaculata

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 0
Species: 1
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
A2bce+4ce

Version
3.1

Year Assessed
1996

Assessor/s
van Dijk, P.P.

Reviewer/s
Horne, B.D., Mittermeier, R.A., Philippen, H.-D., Quinn, H.R., Rhodin, A.G.J. & Shaffer, H.B.

Contributor/s
Selman, W.

Justification

Graptemys flavimaculata has been of long-term concern due to declining populations, having declined historically in the Chickasawhay River and in the Leaf and upper Pascagoula rivers more recently, which together represent 80% of the range of the species; further population declines were observed following the impacts of hurricanes Ivan in 2004 and Katrina in 2005. Generation time is unknown but at age of first maturity over eight years and low rate of reproductive output, is probably more than 20 years.

Graptemys flavimaculata certainly qualifies as Vulnerable A2bce+4ce, and arguably as Endangered. It was listed as EN in 1996 Red List (criteria 2.3).


History
  • 1996
    Endangered
  • 1994
    Indeterminate
    (Groombridge 1994)
  • 1990
    Indeterminate
    (IUCN 1990)
  • 1988
    Indeterminate
    (IUCN Conservation Monitoring Centre 1988)
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Conservation Status

Graptemys flavimaculata is endangered. Although apparently not affected directly by pollution, populations may decline as pollutants adversely affect their food supply of insects and mollusks. Declining populations are attributed to channel modification for flood control and navigation purposes, which destroys basking and nesting areas, and increases siltation and turbidity of rivers, causing disruption in the food supply (USFWS 1992). Populations may also be threatened by the habit of local sportsmen of using basking turtles for target practice (McCoy and Vogt 1980, cited in Ernst et al. 1994). An estimated cost for the recovery of this species over a fifteen year period is $845,000 (Champie 1998).

US Federal List: threatened

CITES: no special status

IUCN Red List of Threatened Species: endangered

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National NatureServe Conservation Status

United States

Rounded National Status Rank: N2 - Imperiled

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NatureServe Conservation Status

Rounded Global Status Rank: G2 - Imperiled

Reasons: Small range in the Pascagoula River system, Mississippi; habitat alteration is a major threat; small population size; may warrant G1.

Intrinsic Vulnerability: Highly to moderately vulnerable.

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Current Listing Status Summary

Status: Threatened
Date Listed: 01/14/1991
Lead Region:   Southeast Region (Region 4) 
Where Listed:


Population detail:

Population location: entire
Listing status: T

For most current information and documents related to the conservation status and management of Graptemys flavimaculata , see its USFWS Species Profile

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Population

Population

Available information indicates that the Yellow Blotched Sawback declined substantially in the late 20th century, and while the decline appears to have been halted, the species has not recovered to historical levels yet.

At the time of its description, Cagle (1954) reported G. flavimaculata to be the dominant turtle in the Pascagoula and Chickasawhay rivers. Early surveys (McCoy and Vogt 1980, in USFWS 1993) reported good populations throughout most of the Leaf and Pascagoula rivers, while populations in the Chickasawhay were in decline.

Lovich (in Ernst and Lovich 2009) found the species common in the Leaf River upstream from a pulp processing plant but absent for an undetermined distance downstream. No G. flavimaculata were observed in the upper Leaf River by Lindeman (1998) during repeated surveys during 1994–95, though he reported low to good numbers near Hattiesburg and further downstream (Lindeman pers. comm.). Some observations were made on the far upper Leaf by Selman, and the population in the middle Leaf river appeared relatively common during studies and casual observations during 2006–2010 (Selman unpubl. 2010, P.P. van Dijk pers. obs. 2010).

USFWS surveys in 1989 (Stewart 1989, Murrah 1991 in USFWS 1993) documented near-absence of the species from the Leaf and upper Pascagoula river sections where the species was abundant a decade earlier, but an apparent increase in population density in the lower Pascagoula. This subpopulation however declined substantially following the impact and aftermath of hurricane Katrina in late 2005 (Selman and Qualls 2007).

Graptemys flavimaculata was considered the third-rarest Graptemys by Lindeman (pers. comm. 2009) based on extensive basking surveys.

Population Trend
Decreasing
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Global Short Term Trend: Relatively stable to decline of 30%

Comments: Population densities seem to have declined in recent years (USFWS 1993).

Global Long Term Trend: Increase of 10-25% to decline of 50%

Comments: Now absent from some areas of the Pascagoula River system where formerly abundant (Horne et al. 2003).

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Threats

Threats

Major Threats

Graptemys flavimaculata has been documented and hypothesized as impacted by a variety of processes, of which habitat degradation and pollution stand out.

Navigation and flood control improvement measures lead to the removal of snags, logs and other obstacles, which represent prime basking sites as well as invertebrate prey habitat. Localized riverine gravel mining increases river water turbidity downstream and affects invertebrate prey populations. Reservoir construction and operation within the Pascagoula basin changes river characteristics to impoundments and affects flow patterns and water quality parameters downstream.

Pollution from municipal run-off and sewage discharges, industrial effluents (particularly from paper pulp processing, and brine discharges from oilfields) and elevated dioxin levels are extensive throughout the basin and have apparently impacted the turtles directly and indirectly through compromised reproduction.

Past commercial and current personal collection for pets, wanton shooting of basking turtles, exceptionally high (increased) nest predation, at the order of 90%, by (subsidized) fish crows, raccoons and fire ants, and reduced reproductive success as a result of human disturbance of preferred nesting sites, have all been indicated as significant additional impacts on populations.

For detailed reviews of threats, see USFWS (1993), Horne et al. (2003), and Ernst and Lovich (2009).

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Degree of Threat: B : Moderately threatened throughout its range, communities provide natural resources that when exploited alter the composition and structure of the community over the long-term, but are apparently recoverable

Comments: Threatened by habitat modification such as by navigation and flood control projects; changing water levels during the nesting season and more flooding than normal of sand bar nest sites (Bob Jones, pers. comm., 1995); gravel dredging; sedimentation from gravel mining, timber harvesting, and agricultural activities; loss of basking sites and nesting areas, and by wanton shooting, collecting for pet trade, water quality degradation due to various industries, and nest predation (see USFWS 1990 for details and for results of 1989 survey).

In the Pascagoula River, this turtle exhibits low reproductive frequency, high nest mortality, and an unexpectedly high level of nesting in shaded areas along the riverbank, perhaps in response to human disturbance on and near sandbars (Horne et al. 2003). In the absence of extraordinarily high adult survival, this population probably will decline because of low recruitment (Horne et al. 2003).

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Management

Conservation Actions

Conservation Actions

Graptemys flavimaculata was listed as federally threatened under the Endangered Species Act (ESA) in 1991; as Endangered by the State of Mississippi; and was included in CITES Appendix III (United States) on 14 June 2006. The 1993 Recovery Plan listed six actions needed:

  1. Conduct population assessments throughout the range
  2. Conduct life history research on the species
  3. Investigate water quality and determine habitat suitability
  4. Formulate actions to protect the habitat
  5. Develop educational materials about the turtle, its habitat, and threats
  6. Develop population monitoring plan.

Horne et al. (2003) called for improved law enforcement protecting adult turtles, public education, and possibly nesting beach protection.

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Management Requirements: This species would benefit from better law enforcement to protect adult turtles, public education, and possibly protection of nests on the nesting beaches (Horne et al. 2003).

Biological Research Needs: Research life history, alternate habitats.

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Global Protection: Unknown whether any occurrences are appropriately protected and managed

Needs: Protect all occurrences.

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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

N/A

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Economic Importance for Humans: Positive

These turtles have been collected commericially, and have been listed for retail sale at $65 each. However, enforcement of laws protecting these animals has likely curtailed this activity (USFWS 1992).

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Wikipedia

Yellow-blotched map turtle

The yellow-blotched map turtle (Graptemys flavimaculata), or yellow blotched sawback is a species of turtle in the Emydidae family. They are a part of the narrow headed group of map turtles. This species is listed as Threatened under the U.S. Endangered Species Act due to a recent decline. This can be attributed to a low reproductive frequency as compared with most other map turtles, with a maximum of 1.16 clutches per female. A high level of nest mortality due to fish crow predation and river flooding are also attributed to endangerment. Unexpectedly high occurrences of nesting in shaded areas could possibly be attributed to human disturbances on and near sandbars, which raises mortality rates.

Contents

Range

Habitat

It is endemic to the United States. Its habitat is limited to the Pascagoula River of Mississippi and most of its tributaries (a range it shared with the Pascagoula map turtle), and suffers from pollution and agricultural changes to the water levels, affecting nesting beaches. "Turtle plinking" kills significant portions of this endangered turtle's population each year. Males have a mean home range area of 1.12 ha and a mean home range length of 1.8 km. Females have a mean home range area of 5.75 ha, due to nesting activities, and a mean home range length of 1.5 km.

Description

Yellow blotched map turtles are medium to small sized turtles, with males ranging from 3.5 to 4.5 inches in size as adults. Adult females are larger, about 5 to 7.5 inches long. The yellow blotched has the highest central keel of all map turtles.

Diet

Yellow blotched map turtles feed mostly on insects, but are opportunistic feeders so also consume crustaceans and fish.

Notes

References

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Names and Taxonomy

Taxonomy

Comments: Lamb et al. (1994) conducted a mtDNA-based phylogenetic analysis of turtles in the genus Graptemys and discovered three monophyletic lineages: G. pulchra group (including G. pulchra, G. gibbonsi, G. ernsti, and G. barbouri); G. pseudogeographica group (including G. pseudogeographica, G. nigrinoda, G. flavimaculata, G. oculifera, G. versa, G. caglei, and G. ouachitensis); and G. geographica. Overall genetic divergence was relatively low, and G. pseudogeographica, G. nigrinoda, G. flavimaculata, G. oculifera, and G. versa all shared the same mtDNA genotype. There was no evidence of infraspecific variation in any species. Walker and Avise (1998) reviewed these data and suggested that the Graptemys complex has been taxonomically oversplit at the species level.

McDowell (1964) concluded that the genus Graptemys should be included in the genus Malaclemys, but this arrangement generally has been rejected (e.g., see Dobie 1981 for information on osteological differences between the two genera).

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