| Literature DB >> 20186292 |
Gen Hua Yue1, Jia Le Li, Chun Ming Wang, Jun Hong Xia, Gen Lin Wang, Jian Bing Feng.
Abstract
Reproductive strategy is a central feature of the ecology of invasive species as it determines the potential for population increase and range expansion. The red swamp crayfish, Procambarus clarkii, has invaded many countries and caused serious problems in freshwater ecosystems. However, little is known about the effects of environmental conditions on crayfish paternity and offspring traits in the wild. We studied these reproductive characteristics of P. clarkii in wild populations from two different habitats (ponds and ditches) in three locations with different environmental conditions in China. Genotyping of 1,436 offspring and 30 mothers of 30 broods was conducted by using four microsatellites. An analysis of genotyping results revealed that gravid females were the exclusive mother of the progeny they tended. Twenty-nine of 30 mothers had mated with multiple (2-4) males, each of which contributed differently to the number of offspring in a brood. The average number of fathers per brood and the number of offspring per brood were similar (P>0.05) among six sampling sites, indicating that in P. clarkii multiple paternity and offspring number per brood are independent of environmental conditions studied. Indirect benefits from increasing the genetic diversity of broods, male and sperm competition, and cryptic female choice are a possible explanation for the high level multiple paternity and different contribution of fathers to offspring in this species.Entities:
Keywords: Decapod; allochthonous species; mating system; microsatellite; multiple paternity
Mesh:
Substances:
Year: 2010 PMID: 20186292 PMCID: PMC2828620 DOI: 10.7150/ijbs.6.107
Source DB: PubMed Journal: Int J Biol Sci ISSN: 1449-2288 Impact factor: 6.580
Parameters of water quality in ponds and ditches from three sampling locations
| Location | Jiangning | Huzhou | Tongxiang | |||
|---|---|---|---|---|---|---|
| Site | Pond | Ditch | Pond | Ditch | Pond | Ditch |
| pH | 6.96 ± 0.03 a | 7.07 ± 0.03 a | 6.76 ± 0.04 a | 7.14 ± 0.14 a | 6.88 ± 0.08 a | 7.07 ± 0.07 a |
| COD (mg/ml) | 14.76 ± 0.32 b | 5.29 ± 0.18 cd | 5.73 ± 0.09 c | 3.51 ± 0.13 e | 27.41 ± 0.63 a | 4.63 ± 0.21 d |
| DO (mg/ml) | 4.80 ± 0.10 e | 11.59 ± 0.21 b | 7.63 ± 0.17 d | 12.20 ± 0.20 a | 3.73 ± 0.03 f | 10.69 ± 0.11 c |
| TN (mg/ml) | 1.31 ± 0.05 b | 0.51 ± 0.02 a | 0.68 ± 0.01 c | 0.42 ± 0.10 de | 1.51 ± 0.04 a | 0.35 ± 0.03 e |
| TP (mg/ml) | 0.75 ± 0.01 b | 0.11 ± 0.01 d | 0.20 ± 0.01 c | 0.09 ± 0.00 e | 0.86 ± 0.10 a | 0.07 ± 0.01 e |
COD: Chemical oxygen demand; DO: Dissolved oxygen; TN: Total nitrogen; TP: Total phosphorus; M: Male and F: Female; Significant differences (P < 0.05) are shown using different letters in rows.
Sampling location, environment, sample sizes, total body length (BL) of dams and inferred genetic paternity in 30 Procambarus clarkii broods
| Location | Site | Dam's ID | BL (cm) | Number of offspring | Number of sires | |
|---|---|---|---|---|---|---|
| genotyped | total | |||||
| TX | ditch | M01 | 10.5 | 48 | 351 | 4 |
| M02 | 9.8 | 48 | 220 | 2 | ||
| M03 | 9.7 | 48 | 356 | 2 | ||
| M04 | 9.0 | 48 | 219 | 3 | ||
| pond | M05 | 10.5 | 46* | 318 | 4 | |
| M06 | 10.9 | 48 | 310 | 2 | ||
| M07 | 9.4 | 47* | 236 | 2 | ||
| M08 | 11.6 | 48 | 331 | 4 | ||
| M09 | 10.1 | 48 | 220 | 3 | ||
| M10 | 10.2 | 48 | 316 | 3 | ||
| JN | ditch | M11 | 8.7 | 48 | 209 | 2 |
| M12 | 11 | 48 | 308 | 2 | ||
| M13 | 11.2 | 48 | 325 | 4 | ||
| M14 | 7.4 | 48 | 136 | 3 | ||
| pond | M15 | 10.7 | 48 | 321 | 3 | |
| M16 | 10.0 | 48 | 270 | 2 | ||
| M17 | 10.8 | 48 | 356 | 2 | ||
| M18 | 10.1 | 48 | 219 | 3 | ||
| M19 | 11.6 | 48 | 318 | 2 | ||
| HZ | ditch | M20 | 11.5 | 48 | 330 | 2 |
| M21 | 7.4 | 48 | 136 | 3 | ||
| M22 | 10.7 | 47* | 321 | 2 | ||
| M23 | 11.8 | 48 | 362 | 3 | ||
| M24 | 10.4 | 48 | 256 | 2 | ||
| pond | M25 | 10.0 | 48 | 219 | 4 | |
| M26 | 11.9 | 48 | 318 | 1 | ||
| M27 | 11.8 | 48 | 361 | 2 | ||
| M28 | 8.6 | 48 | 188 | 2 | ||
| M29 | 7.5 | 48 | 136 | 4 | ||
| M30 | 11.0 | 48 | 321 | 2 | ||
TX : Tongxiang, Zhejiang province; JN: Jiangning, Jiangsu province and HZ: Huzhou, Zhejiang province. * In these broods, 48 offspring were genotyped, whereas genotypes of 1-2 offspring were not clear due to low quality of DNA.
Multiple comparisons of the body length of mothers, number of offspring and number of fathers in 30 Procambarus clarkii broods among habitats within location *
| Location | Habitat | N | Body length of mothers (cm) | No. of offspring | No. of sirs | |||
|---|---|---|---|---|---|---|---|---|
| Mean | SD | Mean | SD | Mean | SD | |||
| HZ | ditch | 5 | 10.36 | 1.75 | 281.0 | 89.7 | 2.4 | 0.5 |
| pond | 6 | 10.13 | 1.79 | 257.2 | 88.9 | 2.5 | 1.2 | |
| NJ | ditch | 4 | 9.57 | 1.84 | 244.5 | 88.6 | 2.8 | 1.0 |
| pond | 5 | 10.64 | 0.64 | 296.8 | 53.2 | 2.4 | 0.5 | |
| TX | ditch | 4 | 9.75 | 0.61 | 286.5 | 77.4 | 2.8 | 1.0 |
| pond | 6 | 10.45 | 0.75 | 288.5 | 47.6 | 3.0 | 0.9 | |
* Differences among environments within location were not significant.
Fig 1Relative contribution of fathers to broods sired by multiple paternity in 30 broods of red swamp crayfish (Procambarus clarkii). F1: the first father; F2: the second father; F3: the third father and F4: the fourth father.
Fig 2The number of offspring per brood plotted against female body size in 30 broods of red swamp crayfish (Procambarus clarkii)
Fig 3The number of offspring in 30 broods plotted against the number of fathers in 30 broods of red swamp crayfish (Procambarus clarkii)
Fig 4The number of fathers detected in 30 broods plotted against female body length in 30 broods of red swamp crayfish (Procambarus clarkii)