Dorovskikh G N, Golikova E A
Parazitologiia. 2004 Sep-Oct;38(5):413-25.
The material represented by 75 specimens of minnow of the age 2-2(+) was collected according to the standard technique in the Chovju River (tributary of the Vychegda River, a region of the settlement Nizniy Chov, district of Syktyvkar town) during the period June-September 2000. The quantitative estimation of the structure of the component parasite communities was performed by calculating errors of the equation of regression for each species group separately, with subsequent summarizing of means of errors by all parasite groups comprising the community (Dorovskikh, 2001 6; 2002 B). In order to have a possibility to get data complementing each other, the calculation of variety indexes and other indexes have been made for metazoan parasites only and for the whole community, including the protozoan parasites. In both cases, i.e. considering only metazoan parasites and the whole composition of parasite species, three states of the component parasite community have been recognised: the formed community (June), the community in destroying (July and August), the community in the process of formation (September). In the course of working on the total species composition we recorded the beginning of community destroying on 30th of June, and the beginning of community formation in August. Considering only the metazoan parasites, the community is defined (after: Pugachev, 1999) as the mature (balanced) one in June, while in July, August and September, it was unmature (off-balance) by its characteristics. Regarding the protozoan parasites, the community in June, August and September was characterized as the mature one based on indices of parasite biomass, and as unripe one based on the number of parasite individuals; however in July, both groups of indices allowed to refer it to the unripe state. However, these unripe states are essentially different. In July, it is the result of dieing out the parasites of the past generation; in August and September, it is the result of the appearances of new generations. Therefore we recognise three states of parasite community named above. Considering the whole species composition of parasites we noted the greater difference of index values based on the parasite specimen numbers and their conventional biomass, that was in the case of the metazoan parasites only. It is particularly noticeable in the middle of the June, in the period of the formed community. This fact, together with high errors of the equations of regression and the presence of the high number of Apiosoma, points to the disturbance in the structure of component parasite community in the minnow from the Chovju River. This is easily explicable, because the Chovju River is the polluted reservoir, and pollution comes from agricultural fields, Verhny-Chov settlement, pigsties and cow-sheds. The pollution is a seasonal factor here. The most powerful pollution was noted at May-June, and then it decreased along the beginning of rains in the end of August; in September it increased again. It is important to point out that the monitoring of the metazoan parasites only allows to reveal the general dynamics of the community during the period of observation, but does not allow to catch the beginning of its destroying and developing and to notice possible disturbances in the community structure caused by pollution of reservoirs, particularly, if this pollution is a seasonal factor as in the Chovju River. Three named states of the component community of the fish parasites take place in other periods of year than this observed in the intestional parasite communities of fish helminths of the temperate climate zone. The developing of parasite communities of the intestinal helminths of the Anguilla anguilla in England (Kennedy, 1997) and of Leuciscus idus from the Rybinsk reservoir (Zhohov, 2003) starts in the beginning of summer. In May, their species diversity is minimal and in August is maximal. In conditions of the middle stream of the Vychegda River, the species diversity of parasite community associated with the minnow is maximal in June and minimal in August, when it only begins developing.
2000年6月至9月期间,按照标准技术在乔夫朱河(维切格达河的支流,下乔夫定居点所在地区,位于瑟克特夫卡尔镇辖区)采集了75个2 - 2(+)龄米诺鱼样本。通过分别计算每个物种组回归方程的误差,对组成寄生虫群落结构进行定量估计,随后汇总群落中所有寄生虫组的误差均值(多罗夫斯基赫,2001年6月;2002年B)。为了有可能获得相互补充的数据,仅针对后生动物寄生虫以及包括原生动物寄生虫在内的整个群落计算了多样性指数和其他指数。在这两种情况下,即仅考虑后生动物寄生虫和寄生虫物种的整体组成时,已识别出组成寄生虫群落的三种状态:已形成的群落(6月)、正在破坏的群落(7月和8月)、正在形成过程中的群落(9月)。在研究总物种组成的过程中,我们记录到6月30日群落开始破坏,8月开始形成。仅考虑后生动物寄生虫时,该群落(依据:普加乔夫,1999年)在6月被定义为成熟(平衡)群落,而在7月、8月和9月,其特征为不成熟(失衡)群落。关于原生动物寄生虫,基于寄生虫生物量指数,6月、8月和9月的群落被表征为成熟群落,基于寄生虫个体数量则为未成熟群落;然而在7月,两组指数都表明其处于未成熟状态。然而,这些未成熟状态本质上有所不同。7月是上一代寄生虫消亡的结果;8月和9月是新一代出现的结果。因此我们识别出上述寄生虫群落的三种状态。考虑寄生虫的整个物种组成时,我们注意到基于寄生虫标本数量及其常规生物量的指数值差异更大,这种情况仅在后生动物寄生虫中出现。这在6月中旬已形成群落期间尤为明显。这一事实,连同回归方程的高误差以及大量阿皮虫属的存在,表明乔夫朱河米诺鱼组成寄生虫群落结构受到干扰。这很容易解释,因为乔夫朱河是受污染的水体,污染来自农田、上乔夫定居点、猪圈和牛棚。这里污染是一个季节性因素。5月至6月污染最为严重,然后随着8月底降雨开始减少;9月又有所增加。需要指出的是,仅监测后生动物寄生虫只能揭示观察期间群落的总体动态,但无法捕捉到其破坏和发展的开端,也无法注意到水体污染可能导致的群落结构干扰,特别是当这种污染像乔夫朱河那样是季节性因素时。鱼类寄生虫组成群落的上述三种状态出现在一年中的其他时期,不同于温带气候区鱼类蠕虫肠道寄生虫群落所观察到的时期。英国鳗鲡肠道蠕虫寄生虫群落(肯尼迪,1997年)以及雷宾斯克水库雅罗鱼的寄生虫群落(佐霍夫,2003年)的发育始于夏季初。5月其物种多样性最小,8月最大。在维切格达河中游条件下,与米诺鱼相关的寄生虫群落物种多样性在6月最大,8月最小,8月时群落才刚刚开始发育。