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Evaluation of an Electric Fish Dispersal Barrier in the Chicago Sanitary and Ship Canal

机译:芝加哥卫生船舶运河中电鱼分散屏障的评价

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In 1990, the U.S. Congress authorized the Army Corps ofEngineers to study barriers to prevent the downstream movement of round gobies Apollonia (formerly Neogobius) melanostomus and other harmful, invasive fishes from southern Lake Michigan through the Chicago canal system into the Illinois River (a tributary of the Mississippi River). A demonstration electric barrier was activated too late (April 18, 2002) to block the gobies, but it was the only barrier to upstream movement of Asian carps from theIllinois River to Lake Michigan and provided useful information for design of a second, improved barrier (Barrier 2). We surgically implanted combined radio-and-acoustic transmitters in 130 common carp Cyprinus carpio that we released 20 m downstream ofthe demonstration barrier in the Chicago Sanitary and Ship Canal to assess the ability of the barrier to prevent upstream passage of fish. Movements of these fish were monitored from April 2002 through December 2006, within and beyond the 8.7-km reach bounded upstream by the electric barrier and downstream by the Lockport Dam and Lock. Fixed hydrophones and radio antennas continuously monitored the canal immediately upstream and downstream of the barrier for signals from the transmitters. In addition, 32 surveys were conducted with boat-mounted receivers to locate transmitters that were out of range of the fixed receivers. The fixed receivers detected 109 of the 130 transmitters; most detections occurred within a few days after release of the fish. Thetracking boat located 120 of the transmitters at least once and 100 at least twice. Most of the transmitters remained well downstream of the barrier and upstream of the lock, but one moved downstream beyond the lock, one passed upstream through the barrier, four moved upstream within 60-400 m of the barrier after moving downstream, and three remained at the release point for their entire battery life, indicating that the fish had died or the transmitters had been expelled. On two occasions, common carpwere visually observed within half a meter of the surface (the limit of visibility) at the barrier. These fish were not observed to move beyond the downstream margin of the electric field. The traverse of the barrier on April 3, 2003 occurred at the same time as a tow was passing. A tow consists of steel barges that are lashed together and pushed by a diesel-powered boat. The tow may have facilitated the passage of the fish, either by entraining the fish or by distorting the electric field. The tracking boat detected the transmitter upstream of the barrier on April 10,2003. The transmitter did not move more than 100 m during the remaining life of the transmitter, indicating that the fish was probably dead. After we reported the passage, Smith-Root, Inc. (operators of the electric barrier, under contract to the U.S. Army Corps of Engineers) increased the duty cycle of the electric field by fivefold. We did not detect any further passages of transmitters, suggesting that the existing electric field (Barrier l) prevented upstream movement of adult common carp and that the new, improved barrier, in combination with Barrier 1, may be effective against the more recently introduced Asian carps. The response of Asian carps to electric barriers still needs further study because the behavior of the Asian carps differs from common carp. Also, there are ways these carps could bypass Barriers 1 and 2 that need to be addressed. These potential bypasses may explain the recent detections of DNA shed from these carps in canal water upstream from the barriers.
机译:1990年,美国国会授权军团的陆军兵员研究障碍,以防止圆形鹅筒的下游运动(以前Neogobius)Melanostomus和其他有害的,受害者来自Michigan的南部密歇根州的南部密歇根州(芝加哥运河)进入伊利诺伊州河(一条支流密西西比河)。一个示范电阻被激活了太晚(2002年4月18日)来阻止胶虫,但这是来自亚洲鲤鱼到密歇根湖的亚洲鲤鱼的上游运动的唯一障碍,并为第二次改进屏障提供了有用的信息(屏障2)。我们手术植入了130个常见的鲤鱼Cyprinus carpio的组合的无线电声发射器,我们在芝加哥卫生和船舶运河中释放了20米,以评估屏障预防鱼的上游通道的能力。这些鱼的运动是从2002年4月到2006年12月监测的,其中在8.7际的电阻和下游的8.7公里范围内,由洛克波尔大坝和锁定下游。固定的Hydophers和无线电天线连续地监测管道上游和屏障下游的管道,用于来自发射机的信号。此外,用船舶接收器进行32个调查,以定位超出固定接收器范围的发射器。固定接收器检测到130变送器中的109;大多数检测发生在释放鱼后几天内发生。将船只位于120个变送器中,至少一次和100至少两次。大多数发射器保持良好的屏障下游和锁的上游,但是一个在锁边的下游移动,一个通过屏障的上游传递,在下游移动后,四个在60-400米的上游移动,三个留下整个电池寿命的释放点,表明鱼已经死亡或发射机被驱逐出来。在两次,普通的Carpwere在视觉上观察到屏障的半米(可见性极限)内观察到。未观察到这些鱼超出​​电场的下游裕度。 2003年4月3日的障碍物的横向发生在拖曳的同时发生。丝束由钢筋组成,钢驳船撞入并被柴油动力船推动。通过夹带鱼或扭曲电场,丝束可能促进了鱼的通过。跟踪船于4月10日在屏障上游检测到发射器。在发射器的剩余寿命期间,发射机在剩余寿命期间没有移动超过100米,表明鱼可能已经死了。在我们报道了这段经文之后,史密斯罗根,Inc。(电阻障碍的运营商在美国军队的工程师的合同下)通过五倍增加了电场的占空比。我们没有检测到发射机的任何进一步通道,表明现有的电场(屏障L)防止了成人普通鲤鱼的上游运动,并且新的改进的屏障与屏障1的结合可能是有效的,对最近引入的亚洲人有效鲤鱼。亚洲鲤鱼到电障障碍的反应仍然需要进一步研究,因为亚洲鲤鱼的行为与普通鲤鱼不同。此外,这些鲤鱼可以绕过需要解决的障碍1和2。这些潜在的旁路可以解释最近从屏障上游的管水中的DNA脱落的DNA脱落。

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