Hernández-Fernández Leslie, González de Zayas Roberto, Olivera Yunier M, Pina Amargós Fabián, Bustamante López Claudia, Dulce Sotolongo Lisadys B, Bretos Fernando, Figueredo Martín Tamara, Lladó Cabrera Dayli, Salmón Moret Francisco
Marine Ecology, Coastal Ecosystem Research Center, Ciego de Avila, Cuba.
Department of Tourism and Business, Máximo Gómez Báez University, Ciego de Avila, Cuba.
PeerJ. 2019 Feb 21;7:e6470. doi: 10.7717/peerj.6470. eCollection 2019.
The reef crests of the Jardines de la Reina National Park (JRNP) are largely formed by , but colonies of and the hybrid are also present. This study shows spatial distribution of colonies, thickets and live fragments of these species in the fore reefs. Snorkeling was used to perform the direct observations. The maximum diameter of 4,399 colonies of was measured and the health of 3,546 colonies was evaluated. The same was done to 168 colonies of and 104 colonies of . The influence of the location and marine currents on a number of living colonies of was analyzed. For such purpose, reef crests were divided into segments of 500 m. The marine park was divided into two sectors: East and West. The Caballones Channel was used as the reference dividing line. The park was also divided into five reserve zones. We counted 7,276 live colonies of spp. 1.4% was , 3.5% and 95.1% . There were 104 thickets of , ranging from eight to 12 colonies, and 3,495 fragments; 0.6% was and the rest (99.4%). In the East sector, 263 colonies (3.8% of the total), six thickets (5.8%) and 32 fragments (1%) of were recorded. In the same sector, there were 11 fragments (50%) of and two (2%) colonies of . Health of was evaluated as good and not so good in the study area. Health of was critical and health of was good in all five reserve zones. There was a significant increase in the number of colonies from east to west (Χ2 = 11.5, gl = 3.0, = 0.009). This corroborates the existence of an important abundance differences between the eastern and the western region of the JRNP. A negative relationship was observed between the number of colonies and the distance from the channel (Χ2 = 65.0, df = 3.0, < 0.001). The influence of the channel, for the live colonies of is greater within the first 2,000 m. It then decreases until approximately 6,000 m, and no significant increase beyond. The orientation of the reef crests significantly influenced the abundance of the colonies (Χ2 = 15.5, df = 2.9, = 0.001). The results presented here provide a baseline for future research on the status of the populations of spp., considering that there has been a certain recovery of the species during the last 10-16 years. Given the current status of the populations of spp., conservation actions focusing should be prioritized.
雷娜女王国家公园(JRNP)的礁顶主要由[具体珊瑚种类1]形成,但也有[具体珊瑚种类2]和杂交种的群体存在。本研究展示了这些物种的群体、灌木丛和活碎片在前礁中的空间分布。通过浮潜进行直接观测。测量了4399个[具体珊瑚种类1]群体的最大直径,并评估了3546个群体的健康状况。对168个[具体珊瑚种类2]群体和104个[具体珊瑚种类3]群体也进行了同样的操作。分析了位置和海流对[具体珊瑚种类1]多个活群体数量的影响。为此,将礁顶划分为500米的段。海洋公园分为两个区域:东部和西部。卡瓦约内斯海峡用作参考分界线。公园还分为五个保护区。我们统计了7276个[具体珊瑚种类1]属的活群体。其中1.4%是[具体珊瑚种类2],3.5%是[具体珊瑚种类3],95.1%是[具体珊瑚种类1]。有104个[具体珊瑚种类2]的灌木丛,由8至12个群体组成,还有3495个碎片;0.6%是[具体珊瑚种类3],其余(99.4%)是[具体珊瑚种类1]。在东部区域,记录到263个[具体珊瑚种类1]群体(占总数的3.8%)、6个灌木丛(5.8%)和32个碎片(1%)。在同一区域,有11个[具体珊瑚种类3]的碎片(50%)和2个[具体珊瑚种类2]的群体(2%)。在研究区域,[具体珊瑚种类1]的健康状况评估为良好和不太好。[具体珊瑚种类2]的健康状况危急,而在所有五个保护区中[具体珊瑚种类3]的健康状况良好。从东到西群体数量显著增加(Χ2 = 11.5,自由度 = 3.0,P = 0.009)。这证实了JRNP东部和西部区域之间存在重要的丰度差异。观察到群体数量与离海峡的距离之间存在负相关关系(Χ2 = 65.0,自由度 = 3.0,P < 0.001)。对于[具体珊瑚种类1]的活群体,海峡的影响在前2000米内更大。然后它会下降,直到大约6000米,之后没有显著增加。礁顶的方向对群体的丰度有显著影响(Χ2 = 15.5,自由度 = 2.9,P = 0.001)。考虑到在过去10 - 16年中[具体珊瑚种类1]物种有一定程度的恢复,这里呈现的结果为未来关于[具体珊瑚种类1]属种群状况的研究提供了基线。鉴于[具体珊瑚种类1]属种群的当前状况,应优先采取以[具体珊瑚种类1]为重点的保护行动。